DSHW-1992-004804 - 0901a068806c10c7

74,ea& coRpo,AroN
STRATEGIC OPERATIONS Mtr. HIVED
Iroy I 6 l99Z
ll November 1992
v400-FY93-r-N7 ,u?ndf, fi ,,di ; [,ffii,Hl[f6i$, u
William J. Sinclair, Hazardous Waste Branch Manager
Division of Solid and Hazardous Waste
Department of Environmental Quality
P. O. Box 16690
Salt Lake City, Urah 84112-4880
Dear Mr. Sinclair:
SUBJECT: M-136 Burn Grounds Partial Closurc 'Plan
Enclosed is the Partial Closure Plan for the M-136 Burn Grounds, This
outline of the closure activities for five burn loeations: in the M,1i35 Burn
written in compliance with the closure requiremens' of R450.7-,1*i: d,f the
Rules for the Utah Solid and Hazardous Waste Cdmmittee
!f you !r1ve any questions or require additional clarificatic*U please contact Kevin fgf .+863-8903.
Sincerel!,
'[iirn presents.-..,ait^
Groutds.' It Is '
Adrnffiisuative
t,fU--'
J . Slaughter, Supenrisor
Environmental Engineering
enc.
PO. Box 689, Brigham Cny UT 84302-0689 i80t) 863-35t t
PARTIAL CLOSI.'RE PLA}.I
M.I36 BURN GROI.'NDS
November 1992
K. R. Fox
Environmental Engineering
lk-
J Slaughter, Supervisor
Environmental Engineering
PARTIAL CLOSI.'RE PLA}.I, M.136 BI,JRN GROI''NDS
1.0 INTRODUCTION
2.0 CLOSIJRE PI-A}.I
1.1 Operation of the M-136 Bum Grounds
1.2 Physical Setting
1.2.t Facility l.ocation
1.2.2 Hydrogeologicd Characteristics
1,2.3 Soil and Soil ProPenies
1.3 Chemical and Physical Properties of Waste
1.4 Conclusions
2.1 Closure Phases
2.2 Closure Time Schedulc
2.3 Administrative and Communication Procedures
2.3.1 Contact Person
2.3.2 Facility Access
2.3.3 Splitting SamPles
2.4 Preliminary Site Decontamination
2.4.1 Area Decontamination
2.4.2 Personnel Protection and Decontamination
2.5 Phase I, Investigative Phase
2.5.1 Surface SamPling Program
2.5.2 Background Soil Samples
2.5.3 Analyticat Methods
2.5.4 Interpreting and Reporting Data
2.6 Phase II, Closure Operations
2.6.1 Closure by Excavation of Wastes
2.6.1.1 Decontamination
2.6.1.2 Restoration of Site
2.7 Certification
3.0 cLosLrRE cosrs
3.1 Rcmoval and Disposal of Contaminated Soil
3.2 Soil Sanpling and tuialysis
3.3 Closure Certification
3.4 Contingency and Administration
I
FIGI.JRES
Vicinity (Location) Map
Site locations and Topography Map M-136 Bum Ground Area
Soil Tlpe Map of M-136 Bum Ground Arca
Closure Schedule
Sample Grid Area for Bum Locations
2.
3.
4.
5.
I
TABLES
Physical and Chemical Propenies of Abela Soils
Possible Hazardous Constinrents in the 5 Bum Locations
Random Numbers Table
Closure Cost Estimate
2.
3.
4.
A.
B.
C.
D.
APPENDICES
T-2 md D-3 Monitoring Well Geologic Logs
GM-3.r
Sampling Procedures
Statistical Comparison Techniques
1.0
l.l
1.2
INTRODUCTION
The M-136 Bum Grounds are located between Air Force Plant 78 and
Thiokol's Space manufacturing facilities in Box Elder County Utatr (See Figure
1). The site was chosen because of it's rcmote location and to provide a
central disposal point for waste generatcd at each manufacturing area. This
paxtial closure plan addresses five closed bum locations in the M-136 area that
wore previously used to qpen bum reactive sludges produced during
manufacture. Specifically, locations 21,22,23,24, and 25 (See Figure 2).
The capacity of these five locations is no longer needed due to altemative
processing methods (M-705, Thiokol's Hazardous'Wastewater Treatrnent
Facility) for disposal of their characteristic wastes. This plan is written to
comply with the closure requirements of R450-7-14 of the Administrative
Rules for the Utah Solid and Hazardous 'Waste Committee.
Operations of the M-136 Bum Grounds
Operations at the M-136 Bum Grounds consists of open buming of propellant
and propellant contaminated solids produced during manufacture. These wastes
are prepared and placed in steel burn trays for opcn buming. After the bum,
the ash and residue is collected and placcd in Thiokol's Industrial Wa*e
Trench. Testing of the resultant astr and residue indicates that all reactive
prolrrties have been eliminated and the waste can be disposed of as non-
hazardous.
All applicable regulations are followed for the proper bum and disposal of
these wastes, including inqpections, operating records, security precautions,
emcrgency preparedness procedures, and contingency plans.
Access to the Thiokol facility is restricted to the public by a perimeter barbed
wire fence, natural barriers, and a fuily equipped security force. Thiokol
employee access to the M-136 Bum Grounds Area is controlled by a barbed
wire fence and M-136 personnel.
Phvsical Setting
1.2.1 Facility l.ocation
Thiokol Corporation's plant is located in northem Utah in Box Elder County,
as illustrated in Figure 1. The facility comprises over 19,000 total acres and
includes several manufacnring, test, and research aroas. The M-136 Bum
Grounds is located benreen tr*ro manufacturing areas, Air Force Plant 78 to the
north, and Thiokol's Manufacnuing Area to the south. Frgurc 3 details Ore
location and topography of the M-136 area
1.3
1.2.2 Hydrogeologic Characteristics
M-136 Buming Area is situated at the stnrctural boundary benreen Blue Creek
valley and the southwestem flank of the Blue springs Hills. This is a horst
and graben block fault system with aro major fault trends: north 20 degrees
east, and east-west. The Blue Springs Hills at this location consists of
Paleozoic carbonate units covered with a thin veneer of Quatemary alluvium.
The valley is filled with Tertiary and Quaternary sediments which include older
fluvial and lacustrine sediments, alluvial fan deposits, Lakc Bormeville
sediments, and recent alluvium. M-136 is locued at the mouth of a srnall,
fault contrrolled, cast-west oriented canyon.
Extensive geohydrologic data has been compiled for this area during pas
studies of the M-136 Burning Grounds. This information can be found in the
M-136 Buminc Area Ground Water Monitorinq Prosram First Interim Report
submitted to the Utah Bureau of Solid and Hazardous Waste in February 1988,
an Addendum to the First Interim Report submitted May 1989, ttre Second
Interim Report zubmimed May 1990, The 1991 Interim Repon submitted in
April l99l, and lhe 1992 Interim Repon submitted in February, 1992.
1.2.3 Soils and Soil Properties
The five bum locations at M-136 are located in alluvial soils identified by the
Soil Conservation Service as Abela gravelly loam. Figurc 3 shows the extent
of the Abela soils around the bum ground area. Table I identifies some of the
physical and chemical propenies of Abela soils. Data obtained from the
geologic log for monitoring well T-2 strows the ground water level at 307 ft
and the bedrock at a depth of 27 ft. Likewise, data for monitoring well D-3
shows the ground water level at 270 ft and the bedrock at a depth of 230 ft.
Figure 2 shows the location of both wells. The geologic log for each well is
included for review in Appendix A.
Chemical and Phvsical Prooerties of Wasrc
The waste disposed of at these five locations consisted of reactive sludges and
waste propellant. This sludge was ttre result of an evaporation of Hazardous
wastewafers from the manufacturing area in permiaed storage vessels and water
treatnent at M-705. This sludge is no longer generated on plant. The
hazardous classification is a result of the reactive/explosive constituents used in
the production of solid rocket motors.
t.4
2.0
2.1
Conclusions
Thiokol Corporation intends to clean close the five buming locations M-136
Bum Grounar Uy demonstrating ttrat no hazardous wastes have been rcleased
during pa* buming activities. This option for closure is the logical approach
because the activities conducted at the five locations in question, ale similar to
crurent buming practices. Testing indicates that curent bums of similar
reactive wastes, rczult in non hazardous waste that can be disposed of in
Thiokol's Industrial Waste Trench.
This closgre plan will provide a demonstration based on the assumption that
hazardous waste could have entercd the soil during the opcn buming Process'
To make this demonstration, a plan involving soil sampling and testing will be
implemented.
CLOSURE PLAN
In order to demonstrate ttrat the operation of the five locations in the M-136
Bum Grounds has only minimally impacted the surrounding arca, a rwo-phase
closure plan will be used. The first phase will determine if a release has
o..r11"d from any bum area and the extent of any contamination, the second
phase will be the actual implcmentation of the closure plan.
The closure of these areas will be conducted on an individud, s required basis
and in accordance with the Closure Performance Standard of Section 7-14'2 of
the Administrative Rules for the Utah Solid and Hazardous Wastes Committee.
Closure Phases
phase I is an investigation phase. This phase will determine ttre extent of
contamination, if any, at each of the frve sites.
Phase tr of the closure plan defines actual closure oPerations necessary to close
any of the bum locations and dispose of any identified hazardous waste, waste
muerials containing hazardous waste, or materials containing hazardous waste
constituents.
Closure Time Schedule
A timc schedule for closure is illustrated in Figure 4. All dates rcference the
first day of the respective month. The time schedule reflects the timely
implementation and approval of the closure plan and lists only milestone for
2.2
2.3
implementing each phase and rcport. Field work at the site will be performed
only during the dry weather season: typically April through October.
Administrative and, Communication Procedures
2.3.1 Contact Person
On approval of this closure and post-closure plan, a contact Person will be
designated for coordination of activities and communications. The State will
be notified of any construction, sampling, and/or drilling activities to be
conducted under this closure and post-closule at least tcn days in advance.
2.3.2 Facility Access
Upon request, Thiokol will provide reasonable access to its facility to
authorized representatives of the State for thc purpose of monitoring, sampling,
and observing activities carried out undcr this plan. State representatives shall
comply wittr established safety practices. In the event rcpresentatives wish to
have photographs of any of the five burn ground locations or the work carried
out under this plan, the camera, fitn, and all other equipment to be used in
taking photographs will be provided by Thiokol; an authorized State
rq)resentative may specify ttre type of film to be used. The photographs will
be taken by Thiokol personnel. The authorized rcpresentative of the State will
designate the area to be photographed and may be present if he or she so
desires. If a photogfaph is taken of an object or an alea which would indicate
or show proprietary information or processes, it will be providcd to State only
under the procedures specified by applicable law for the protection of
proprietary material.
2.3.3 Splitting Samples
Upon request by authorized rcpresentatives of the State, Thiokol Corporation
will provide split samples of any samples collected pursuant to this plan.
Preliminarv Site Decontamination
2.4.1 Area Decontamination
During the buming of propellant and propellant contaminated materials, a small
portion of the buming material is ejected around the bum tray. This result a
small ring of the ash and residue around the bum tray itself. Although no
decontamination activities or procedures are expected, we have allowed for the
2.4
following possible solution for this top soil sttould it be required. The top 6"
of soil shall be scooped into the adjacent burn tray. This will be completed
such that there is a 15' radius circle around the edge of the bum tray. This
should allow for collection all ejecta around each tray. This 15' figure is based
on visual observation of the sites combined with previous obsenation of ejecta
from M-136 Bum Ground activities. The soil will then be diqposed of in a
hazardous landfill with the initial rcsidue in the bum trays.
2.4.2 Personnel Protection and Decontamination
During the clozure of each site, all personnel will wear (at a minimum) the
following safety equipment:
Tyvek suit
Rubber Boots
Monogoggles
Rubber Gloves
2.5 Phase I. Investieative Phase
Phase I of the closure plan will be the collection of data to determine if any
hazardous waste contamination has occurrcd. To obtain the necessary data,
cxtcnt of the waste must be determined using a sampling program. This
progmm will utilized zurface sampling and will incorporate a simple random
sample design.
Because of q'picdly homogeneous bum materials and pas bum sampling
testing, Thiokol has chosen to perform a simple random sanpling procedure for
taking samples. This technique will involve placing a $id over the site area.
The grid will be divided into squares each 5 ft by 5 ft. The intersections of the
grids will be numbercd as outlined in Figure 5. Each intersection will be a
possible sample location for a surface sample. The location of these sample
sites will be chosen by a Random Numbers Table (fable 3). The actual
location of thc sample sitcs will not bc choson until the day of sampling. Only
then will the random number chart be used to select exact sample locations.
2.5.1 Surface Sampling Program
Four sampling points will be chosen for each of the 5 bum locations. A
sample will be taken at 0-1 foot below ground surface at each chosen sampling
point. The Selection of sampling points at each bum location will include (at a
minimum) 1 sample from within the original bum tray location. The samples
will be analyzcd for the hazardous constituents as shown in Table 2. Sampling
procedures and techniques are discussed in Appendix C.
2.5.2 Background Soil Samples
Four background locations will be chosen with samples taken at 0-l foot below
ground surface. The depth of this sample is based on the depth of samples to
be taken in each bum location area. Soil samples will be analyzed for the
constituents in Table 2.
2.5.3 Andytical Metlrcds
All samples will be analyzed for constituents listed in Table 2. Thiokol will
contract with an independent, Utah State certified laboratory to analyz.e the soil
samples. The selected company will follow State Approved quality control and
quality assurance plans for testing environmental samples.
2.5.4 Interpreting and Reporting Data
The analytical results of Phase I and other rclevant data (aboratory QA/QC,
actual analytical methods, etc.) will be organized and included as part of a
closure re?ort and submitted to the State.
In order to determine if any contamination has occurred in the soils around
each of the five bum locations, a comparison will be made benveen the
analytical results from each zurface sample and the background samples. The
data will be analyzed using analysis of variance technique for simple random
sampling. This technique is described in ttre publication Preparation of Soil
Sampling Protocol. Techniques and Strueqies.
Comparisons will be made between the zurface samples and the background
samples using analysis of variance. Also, a test will be conducted to test the
bum location sample mean against the background mean using the least
significant difference test. This test is also discussed in the previously
mentioned publication.
The detailed steps for making these calculations is presented in Appendix D.
All tests will be conducted at a significance level of 0.90. Any analysis below
detection limits will be treated as if at the detection level. For example, rf a
background sample was analyzed and it contained less than the detection limit
for the constihrent, Ore calculations for thc AI.IOVA test and Orc least
significance difference test will use the detection limit for numerical value.
If the concentrations of the samples in the AI.IOVA test and the least
significance difference test indicate that the samples and background do belong
to different populations, then that particular sampling grid area at it's respective
bum location will be considercd contaminated and require remedid action in
2.6
the second phase of the closure plan. The identified area of contamination will
be excavated and disposed of properly as hazardous waste. These activities are
outlined in Phase tr of the closure plan.
Phase tr. Closure Operations
If hazardous waste or hazardous waste constituents are detected in the shallow
soils, an excavation option will be implemented to remove the wastes.
2.6.1 Closure by Excavation of 'Wastes
All waste and wase residues identified in the sample program as hazardous
waste, will be excavated from the site. These materials will be properly
disposed as a hazardous waste. After completing the excavation of the
contaminated soils, soil samples will be taken to demonstrate that the area has
been cleaned. All soil samples procedures are discussed in Appendix C. The
soil samples will be analyzcd for the constituents identified in Table 2. Sample
locations will be defincd by gridding the area of excavation into 5 ft by 5 ft
squares. Four sample locations will be selected using the Random Numbers
Table. The samples will be 0-l foot deep soil cores. Each sample will be
analyzed individually. The analysis of the soils beneath the excavated area will
be compared to analysis of background soil samples taken in Phase I.
The analyticd results from the excavated area will be compared with the soil
background data using the techniques previously discussed in Section 2.3.5. lf
the concentrations in the soil bcneath the cxcavated area belong to the samc
population as the background soil, then all waste and waste residues will be
considered removed.
If a comparison of the analytical results indicates the soils are not from the
sample population, all reasonable efforts will be made to continue excavation
until it has been conlirmed that dl contamination has been removed.
Confirmation will be made by resampling the area using the same procedures,
including gridding the area, as previously discusscd.
2.6.1.1 Decontamination
Cleanup and excavation of wastes will be performed by contractor(s)
retained by Thiokol Corporation. All equipment which comes in contact
with hazardous wastes or contaminated soils will be thorougtrly
decontaminated. Gross solid accumulations wiII be removed on site and
combined with contaminated soil for proper disposal as a hazardous waste.
All equipment will be thoroughly washed with water and seam and these
waters will be collected and analyzed. If these waters contain hazardous
wasf,es, they will be tranryorted to the M-705 wastewater facility and treated
as hazardous waste liquids.
Decontamination will be handled next to the site. A decontamination station
consisting of lined surface sloped to a lined depression in the soil to collect
wasrh waters will be established. The deconamination area will be lined
with an plasic liner of not lcss than 30 mills thick polyethylene. All liner
and residues on the liner will be disposed with the contaminated soils.
2.6.1.2 Restoration of Site
After the excavation is complete, the excavated site will be backfilled with
natural occurring soils and graded appropriately for the surrounding area.
AII results from Phase tr will be submitted the Utah Bureau of Solid and
Hazardous Waste in a closure report. Data to make appropriate
demonstrations will be organized and prescnted for agency review and
approval.
2.7 Certification
3.0
All data shall be certified by an independent professional engineer for closure
requirements. The engineer certrSing closure shall be prescnt at all mileposts
listed in the schedule for closure and shall review dl reports and data.
CLOSURE COSTS
Detailed closure costs are presented axe presented in Table 4. The closure cost
estimate will be reviewed whenever a change in the closurc plan affects the
cost estimate. It will be adjusted annually to reflect inflation. The Departnent
of Commcrcc's Annual Implicit Price Deflator for Gross National Product will
be used to make this adjustment. All closure cost estimates arc made by
assuming a third party is contacted to perform the closure and a worst-case
sinration exists. The following assumptions are made when cdculating the
closure costs.
Removal and Disoosal of Contaminated Soil
No soil contamination is expectd to bc found at closure; however, the
potential of contamination exists and so it is accounted for in the cost estimate.
3.1
3.4
3.5
3.6
An estimate of five percent of the surface area could be contaminated.
Contamination should not be found at depths greater than six inches. Total
contaminated soil is calculated below:
(0.05) (5) (0.5 x80x trc ln ffttvd) =20.4yd,
During the removal of the waste, approximately 450 gallons of contaminated
rinse water will be generated and need to be managed and disposed of a
hazardous waste.
Soil Sanrplins and Analvsis
All soil analysis will performed by outside contractor(s). Soil sampling will be
conducted by Thiokol personnel. It is anticipated that a minimum of 20
samples and 4 field blanks will need to be analyzed. An additional ten samples
are included in the estimate if contamination if found.
Closure Certification
The cost of closure certification is based on a potential three-day need of an
professional engineer.
Continsencv and A&ninistration
Total costs will assume 15 percent contingency costs and a 15 percent
administrative cost. Administrative costs include tracking manifests,
supervision of work, and other general follow up and closure preparation
activities.
TAb-o I
PROPURTIES OP ABEI,A SOII,S
TOTAL
SIZE CI,ASS AND DIA}IETIR OF PARTICI,ES
SAND TRACTION
SOIL
Abela Gravelly
l,oaur
(ABE, AEE)
ltoRIzoN
All
Ar2
B2
Clca
C2ca
C3
CI,AY2
( .a. 0 .002
urnr. )
l8
20
2t
l6
l5
t2
VERY
COARSE
SANt)
(2 .0-l .0
urm. )
COARSE
SAND(r.0-0.s
urn. )
MEDIUI'I
SANI)(0.5-0.25
mru. )
SANI)(0.25-0. I
nro. )
VERY
}'INE
SAND(0. l -0.05
um. )
DEPTH
0.5
5-l 4
L4-28
28-39
39-49
49-50
SANI)
( 2.0-0.05
mn. )
28
25
27
A9
53
50
S].I,7
( 0 .05-
0 .002
mnr. )
I.IEFI
INCHES PERCENT PDITCT:NT PERCUI.IT PERCENT PERCI'NT PERCENT PERCENT PURCENT
s4
55
52
35
32
38
7
6
6
l6
t9
l9
3
3
3
9
0
0
I
I
4
4
5
8
9
7
I
I
2
4
4
4
t2ll
l1
t2
ll
l0
TABLE I (uUNTINUED)
PROPERTIES OP ABELA SOILS
COARSE
FRAGI'IENTS(2 nm, to
3 lnches)
ORGANIC
CARBON
SOLt]I}I,E
SALT
(BI'REAII
(:llP)
ELUCTRICAI,
CONDUCTIVITY
RDACTIONCALCIUM WATI]R
CARBONATE CONTENT CATIONEQUTVAI.ENT AT 15 EXCI|ANGE.ATMoSPIIURUS
--
CAI,A(]II'Y
SATURATIiI)
PASTE
l:5
EXCIIANGEABLE BAStsS
(MILLIEQUIVALENTS
PER IOO GRAMS
oF sotL)
SODII]M POTASSIIIM
EXCIIANGDABLE
SODIU}I
I
PERCENTAGE
BY WEIGIIT PERCENT
44
69
90
73
PERCENT PERCENT Pll pH
}IEG I'ER
100 cl'r
OE SOlI,PERCEI'lT PERCENT
0.05
.05
.04
.04
.03
.04
MMIIOS PER
CI.T AT 25"C
4A
44
2
I
I
5
3
o
7
6
3
9ll
l5
25
36
27
2l.l
19.7
r8.0
lo.6
8.6
8.8
8.6
8.7
8.8
9.0
9.2
9.3
7.5
7.5
7.6
7.8
7.9
8.0
10.4
9.9
10.0
6.9
6.4
5.7
1.9
1.7
.8
.5
.5
,..,, 8
0.2
.3
.4
.5
.5
.5
I
2
2
5
6
5
2.2
1.0
.7
1.2,
1.4
1.4
i FROM: So11 Survey of Box Elder County, Utah, Eastern part
TABT-B 2
POSSIBLE IIAZARDOUS CONSTITI.'ENTS
IN TTIE 5 BI'RN LOCATIONS
ANALYTICAL PARAMEIERS
The following list represents the parameterc to be measurpd in each of the samples taken at the
5 burn locations. This list is the current matrix used in tesring normal burn ground residues.
Hh/D(
Niroglycerin
Total Metals
Arsenic
Barium
Cadmium
Chromium
Lead
Mercury
Selenium
Silver
Total Organics
Benzene
Carbon Terachloride
Chlorobenzene
Chloroform
o-Cresol
m-Cresol
p-Cresol
Cresol
1,4-Dichlorobenzene
1,2-Dichloroethaae
I,1-Dichloroethylene
2,4-Dinitrotoluene
Methyl ethyl ketone
Nirobenzene
Pentachlorophenol
Pyridine
Terachloroethylene
Trichloroethylene
24,Slicblorophenol
24,6-Tichlorophenol
Vinyl Chloride
Method
HPLC
HPLC
Method Numbers
6010,7060,706t
6010,7080,70gl
6010, 7130, 7131
6010, 7t90,7191
fi10,7420,7421
7470,7471
6010,77N,7741
fit0,77fi,776t
8020,8Az-
8010,8240
E020,8240
8010, 8240
8040, 8250
8040,8250
8040,8250
8M0,8250
8010, 8120,
8010, 8240
8010,8240
8090,8250
8015,8240
8090,8250
8040,8250
8090, E250
E010, E240
E010, Ezo
8040,8250
8040,8250
8010, E240
8250
TABLE 3
RANDO!,T NWBERS TABLE*
03
97
16
L2
55
43
24
62
85
56
61
20
07
31
22
16
84
63
33
57
18
26
23
52
37
70
56
99
16
31
22
42
01
2L
60
18
62
42
36
85
29
62
49
08
16
77
L7
63
L2
86
73
67
27
99
35
L2
37
22
04
32
39
31
59
29
44
46
75
74
95
L2
36
42
56
96
38
44
84
82
50
83
40
96
88
33
50
96
81
50
96
54
L7
r6
97
92
39
47
l4
26
68
82
55
55
56
27
20
50
95
L4
89
36
57
7L
27
46
54
06
67
07
96
58
44
77
1l
08
38
87
45
34
87
82
88
19
82
54
46
42
32
05
3r
L7
77
98
5Z
49
79
83
07
00
42
l_1
97
l6
4)
?o
37
04
10
42
L7
89
L2
64
59
15
63
32
79
72
43
93
74
50
07
46
5r
25
36
34
37
7l
37
78
93
09
23
47
7t
44
09
19
32
T4
31
96
03
93
16
68
00
62
32
53
15
90
74
47
00
49
49
98
53
90
03
62
86
62
66
26
64
47
74
76
56
59
49
57
l6
78
09
94
53
78
34
32
5tt
24
95
64
47
78
67
75
38
62
62
24
08
38
88
43
16
07
77
26
50
07
38
40
28
94
92
97
64
19
35
09
99
81
97
30
83
11
45
56
34
86
46
12
76
07
l7
t8
57
15
93
13
35
77
72
43
33
83
42
27
27
26
75
72
09
19
I
* Hor to use the Random Numbers Table:
If saupllng conta{nerized lraates (1.e., dlilas, sacks, etc.)
segregate the contalners accordlag to traste type based on available
Lnformarlon e.g. contalner uarklngs, labels. Nuuber eontalnerswlth the saoe waste type consecutlvely, starttng fron 01. If
sanpllng surface lraters, dlvlde the area lnto a t!ro- or
three-dluenslonal grld and number the grld locatloas.
2.
3.
Detemlne the nunber of saurples you need to take. For routlne
sunrelllance aaupllng one or Ero ls ueally adequate aud Judguentsaqllng le sultable. but for regulatory or research purposes, I
larger sanple elze (such as one saople for every group of flve
contalners) taken at randou w111 generate Eore statlstlcally valld
data.
Uslng the random nunbers table, choose any nuuber aa a lrtartlngpolat.
Fron thls number go ln any dlrectlon untll you have selected the
predeterol.ned number of sanples wlth no repetltlons. Nunbers
larger than che populatlon Elze are lnellgtble.
4
I
TABLE 4
CLOSI'RE COST ESTI}{ATE
Disposal of Contaminated Soils
a. Disposal (20.a yt @ $1,500 yC31
b. Removal 20.4 yd' (40 hrs @ $75lhr)
Soil Sampling and Analysis
a. Labor (20 hrs @ $40/hr)
b. Analysis (34 samples @ $ZOO sample)
Certilication
a.Labor (8 hrs @ $604n and
$100/day expenses)
SUBToTAL ($)
Contingency (15 percent subtotal)
Administrative (15 percent subtotal)
rorAl, ($)
2.
30,600
3,000
23,W
3.
800
580
4.
5
58,780
8,817
8,817
76,414
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APPENDIX A
T-2 and D-3 Monitoring Well
Geologic t ogs
GECLOGIC LOG CCMPLETION DETAILS
ooJI
G
Go
DESCRIPTION
ELEVANON AT TOP OF PVC CASINE 459TC2
'LNOFTHINq .€.re53 n EASr|I.IQ 1715363.9 6
WELL CAP
10'STEEL PAOTECTIVE
cAstNo
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Mild r.ldion to HCL 10 yR O/3, &olr
gttveI
8.o.latr Grlvclly ctlt ADgrox, BOt llt 3Ot orlvcl tot ,t^. Crlln.d s.,rd
&!yd la lljb-uroir!, to sub{oJndad llnartofi, rn l qJrrtzltc
Low to no Dlasdcity. 10 yR otz udrt browrisn gray,
l8.O-27.q Slrdy lllt Aogror. 50!. !ilt, 2Ot s!l||4 2Ot cobblan
Wlth mho, ctay. G.lvC b SA - A f \R 612 UCht BrowForly.
27ogg Mlcrilc Urreslo.l. with lrown crtc,it. v.io., Hhhty
r..,ritvc to HCL 5 y t{t/ 7/Z UCH c'.y.
aa.o-68.(, Lhr.3ton.{rlcrtilc silrr tacc o, *trlta to leht tao
doloi$l.' H.rd wtttr ocar.rto.r.t hr.rb.d o, loht ef., to yhtt.
.attttona ModaJra. ,..ction to HcL o ya 12 L],dx urv.
640-t0t-q Dobmfic tD.uoo. Mlcrt0e Mod..at.,{ctloo lo }lcL
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llodrlt r..(ilor to HCL
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2S Y N7/O.
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PROTECTION
PAO
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9 7/r DRII
2r
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CONCFETE
SURFACE
IETT CEM€NT
BEXTOMIE
GAOUT
20
40
60
80
100
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0
EarthFax
Engineering. lnc.Thiokcl Corporation MoNlroRlNG WELL Paso
T-2 01
2
GEOLOGIC LCG COMPLETION DETAILS
9io<otto DESCRIPTION
0.lr dril.c t-28-et to 2-tg-9r
Onlld: ZlrilnfiD.n WaI S6dc.
orlllhC nrthoc Crbta toot/Alf rotrry
dlarn td: tof
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1,2.O-$Cg Dolorrilla, Mlcrocryttrllnc r,ttt Inc. o, y.tor to sttlt.
crrcltr 25 Y N7/O Uet{ tty.
IEAO-22q, Crysi.lllno ttD.3ton wlth drro. y.Xowlrh c.bfta,
Hhtrtr rc.c0v. to HCL 2.5 y NC/o, [fd{ Ony.
22Ob22A.g oolootaa So.rry. Mo(brrt. 'ucdsr lo HCL
sonr. Lolt orlda .trStno uglt gry to lctt t.^ Har(L
22AD-24e(, Oob,rtdc LD.atcra ttod.rtta,..cIct to lGL Ueha
g.Y 6Y M/O to [ctt t ,t
216.O-2C?.9 ooacD.[a thr..tm. .nd clr..t bor o:ddo ltrilro!
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2t3or3og(f S.ad, ln .tct Sory. Coltr5. arro.|o n ! Ci-t
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i..!oy.$lll hcrca.ho d-t Frrclrac
3O1Og|aO ljtraarlr Maatrvr lro.ra.tra ,racldor to HCL Scr... tqt od. .arblro F,lct rd, lto CrrL 25 y tl6/O G[y.
OCo,tS ln .rqia LtoDt,a..iloo to HCL ft.atrr.(L31A.+3ng
t n to Ucl l'ry. zty t{/rl0.
a scH 80
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CET{IR^IIZER
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Engineering; lnc.Thiol<ol Corporation MONITORTNG WELL
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PROJECT No.l C- t+l -o t o(OL)rBY:
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RECORDED
WELL FM.CONSTRUCTION TIME LOG
START FINSHTASX
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JO8 NUMBEB s6t 26 CLIENT Y^?rm fh.,^1.^l
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s-5
57,0
57.4
77
77
0
4
!!-9
i
D
v
E-v
PERMEABILITY
r - sllght
m - ,ttodctatc r'
v - vcry
EE
-=rw
SPLIT SPOON SAMPLE
GBAB SAMPLE
UNOISTURBEO SAMPLE
WATER TABLE 24 HR
WATEF TA8LE TIME OF BORING
ENGINEERING-SCIENCE
JO8 NUMEER 56426 CLIENT
BORTNG NUMBEF-=- BOBING DIAMETER
GEOLOGIC BORING LOG
ftrl aleal
7-7 /8"
CONTBACTON
earlable tF WEATHEF ver{ahle
OFILLTNG MEOIUM USED Al'r
Shect 3 of 7
oATE 10/2r /85 - lrl3l85
Etc vATloN t553.42
DATUM lec-rl-gffasrcs.
ENGTNEER GAIJ
UACHINE TYPE
TEMPEBATURE
llo
DEPTH
(FT.)GEOLOGIC DESCBIPTION
SAMPLES lrlC
F
d=oH BEMABKS
NO.DEPTHlF?-)
o.oo^cdo60o
9S gOoclo
6 o66ogoo100
o...::ei;
,.o
r05
6
o
-uq-
o o
9rr5o o
.s
J:0-
,
t5
gray GR-IVEL (1/8 - l") rrlc,h E! fl-qo
sand a:rd s: sllc- subrnC. il€d dense
s.A.A.
cao to !r!ay v fI,-fl SAIID rlsh soac
gravel (ll8 - 3/4"). looge-oed deasa----
s.-{.A.
s..l.r.
s-a-.{.
ts8 v fl cb ef SltO trlth Er crancl
(Lli-314\- subrod----
a
s.A.A-
s-6
97
91
0
0
$
t-G
ro1!t
PEFMEABILITY. - tllght
m - nocarrla
v - vcry
EEI
E
--=F
SPLTT SPOOII SAMPLE
GRAE SAMPLE
UNOISTUREED SAMPLE
WATER TABLE 24 HR
WATER TAELE TIME OF BORING
ENGIHEEFTNG-SCIENCt
Sheet t1 of
OATE tol2t/8s - rrl3l15
ENGINEER GA!'
GEOLOGIC BCBING LOG
JO8 NUMEER 56426 CLIENT {ortm
BOFTHO NUMBER D'3 gORING OIAMETER 7-7 18"
TIACHTNE TYPE cP 7000
TEMPERATUHE a-uar{ahl. F WEATHEF varlable
ORILLIHC UEOIUM USED
ELEVATION 6ssl a,
CONTRACTOB OATUM loLci-:lg-Cesle-
DEPTH
(FT.)GEOLOGIC DESCBIPTION
SAMPLES tgJlgqA
=><t-
at
iE<H BEMABKS
xo.OEPTHlF?-l
s.a..{.
140
s.A.A.
-ta:- -
150
Eaa e fl eo El SAIID, ouaarzose.
osd denge
155
.. j .-{.-q..
160
,.
.A.A.
-r(L
s.A.a.
170
s.A.A.
t75
S.A.A.
tE0
t37
137
0
L
S-a
It
!118ht1y Eolsr
PEFMEABILITY
! - ttlghtn - ,ttodatttc
v - vc?y
EE
It
-=-
SPLI? SPOON SAMPLE
GRAE SAMPLE
UNOISTUHBED SAMPLE
WATEB TABLE 21 HA
WATEB TABLE T'ME OF BORING
ENGINEEBING-SCIEilCE
Sheet s of i
GEOLOGIC BOHING LOG
JOE NUMBEB 56426
BORIHG HUMBEF n-'l
MACHINE TYPE e? 70no
TEMPERATURE varlable 'F WEATHEB vatl,abl,e
ORILLING MEOIUM USED A1!
CLIENT Vo"tort 1r{111.^1 DATE t0l2rl85 - tu7tgi
EORtNG OIAHETER 7-7 /8"ELEVATION 6S53 42
CONTRACTOR Dave'r Drl1l1nq DATUMfoo of P(T Czcirs
ENGINEER CAIJ
SAMPLESDEPTH(F".)NO
uta
F
.:adA(EoE REMARKSGEOLOGIC DESCHIPTION DEPTH(FT.I
190
_lgs_
-2ra-
205
lt0-
2ts
220
225
t95
ca8 e fl SA..ID .rlEh B! s1lc,
, Euiiaceous. dase
s.A.A.
s.A.A.
s.a.a.
s.A..1.
s.A.A.
s.A.A.
s.A.A-
s..{.A.
i
)It
3<
PERMEASILITYr - ltlght
m - modarutc
v - Yory
E=
E
--=f
SPLIT SPOON SAMPLE
GRAE SAMPLE
UNOTSTUHEEO SAMPLE
WATER TAELE 21 HR
WATEH TAELE TIME OF BOR'NG
ENGINEEBNG-SCIE}TCE
JO8 NUMBEF 56426 CLIENT
BORING NUMEER D.]EOFING OIAMETER
CONTHACTORMACHINE TYPE CP 7000
TEMPE FATUFE varr,able tF WEATHER varlable
ORILLINC MEDIUM USED
GEOLOGIC BOR!!{G LOG
Yorton ltrlokol '
7-7 /8"
llarra, q t'\l.l l1{ao
l{r
Sheet 6 of 7
OATE lo/21183 - ttrllns
ELEyAT|ON 4553.12
OATUMtop of PC;v Caslag
ENGINEER CA!'
DEPTH
(FT.)GEOLOGIC DESCRIPTION SAMPLES utA
F
dEoH BEMARKS
NO.DEPTHlF?-l
230
235
I
I
I
240
245
- -2:0--
235
260
- J65--
270
s.A.A.
conqloocrate O. - 2n\
r.iEh soac fi-co saod. CaC03 ceaeaaed
subrad
-EiS S -$J4SD_,.1!!, lr-'IIL
qualtzosa, guffaceous, aed deose
:... .
s.a..t.
i?g J i1:r! !${P3{g!qo3 il,lq- - -
s.A.A.
taa EO gs SA.\DSIOUE irlch (ntaFz ad
f crah3-s+r-Earar+,9 f.t -
geq E:a_lgd- -{egSg _
s.A.A.
g-a
,
h
tt-O
249.8)
tclt
3
270'
PEFMEA8ILTTY
! - tllght
,D - moc,cratc
v - vary
EI
E:.
+:!t
SPLIT SPOON SAMPLE
GAAS SAMPLE
UNDTSTURSED SAMPLE
WATER TABLE 24 HR
WATEH TABLE TTME OF BOFTIIG
ENGIHEEBING-SCtENCE
Jo8 NUHBER 56426 .
BORTNo NUMBEn-$-
GEOLOGIC BOBING LOG
Sheet ; ol 7
CLIENT !{o?t6n ?!rloltol oATe tol2l/85 - ru3raJ
BOBING OIAMETER 7-7 lAi.ELEVATIO N 6553-42
CONTRACTOR OATUM jc!-eL.:g!l45Lee_
ua!1ab1e tF WEATHER varlable ENGINEER
OBILLINO MEOIUM UgEO Alr
MACHINE TYPE
TEMPERATURE
c9
DEPTH
(FT.)GEOLOGIC DESCBIPTION
SAMPLES tr,A
F
d=AE<H BEMABKSxo.DEPTHlF"-!
s.A.A.
_us_
s
280
i8 -!o- gaa LrgSfq$LP4tsles- - -
-- 2j)-q1Bb spgg .fi:ccatge- sara
285
dk gray Bo ba LB€StlllE rrlih chert
strLagels ald Ea calclge velns
290
S.A.A.
?95
t
U
6-v
aodetacely fraccured
lo:lac_r 1q93r sa_O_t!!'_ _
PERMEAEILITY
3 - cllght
m - nodcrata
v - Yary
t:
r
=r
--
SPLIT SPOON 9AMPLE
GFAE SAMPLE
UNOTSTUREEO SAMFLE
WATER TAELE 2/t HR
WATER TAELE TTME OF BORIIIO
ENGINEEBTNG-SCIEHCE
APPENDD( B
GM-3.1
DISPOSAL INSTRUCTIONS FOR
WASTE MATERIALS
December 1991
General Process Instmction
GM-3.1
Issue No. l-11
Progmd by:
WASTE MANAGEMENT AND ENVIRONMENTAL SERVTCES
CORPORATION
Rtblicotiotts No. 92@5O
13 DECEMBER ,99'
DISPOSAL INSTRUCTIONS FOR
WASTE MATERIALS
BOOK NUMBEB 33?,
MGDOCI.'MENT
GENERAL PROCESS INSTRUCTION
DOCUMENT NO GM.3.1
ISSUE NUMBER 12
EFFECTwE DATE: 13 DECEMBER 1991
J--
(zdl,.-
RF.ASr)N (--I.IANGF.
To incorporate changes in waste disposal requirements as summarized in the preface.
,Er.r
olo.r
lrotr 1lo. 122l &pi.rib.r l0a2
6MN.I ACTIVE PAGE IJST
Prcfecc
l.iA-iC ....2lScptcmbcr1992
V-tl
It
[l
lv
vlr
vru
xr
xll
,dii
I
. . 2l Sopamber 1992
2l SGptcEbGr 1992
2l Scptcmbcr 1992
2l Scptcmbcr 1992
2l Scptcobcr 1992
2l ScptcmbGr 1992
2l Scptcmbct 1992
2l Septcmbct 1992
21Scptcmba 1992
2l Scptcmbct 1992
2l Septoobct 192
2l Scptcmbcr L992
2l Soptcmbcr 1992
2l Scptcmbcr 1992
2l Scptembcr 1992
21 Scptembet 1992
2l Scpambct 1992
2l Scpambct 1992
2l Septembct 1992
2l Scptcmbcr 1992
2l Scpombcr 1992
2l Scptcmbct 1992
2l Scptcmbcr 1992
2l Scptambc 1992
2l Scptcobcr 1992
2l Scptcobcr 19912
2l Scptcmbcr 1992
21 Scptcmbcr 1992
tI-I.
Section I - Incrt Prqcllentaod Livc Marsrial Prcparetion
1A
-4
7
2
3
5
6
8
9
9A-l0ll - llA
13-14
t2
t7
3t
3tA
15. 16
?t -20A
It-19
2t -22
Scction II - Ilazardou lVartc hcparetioa
t2
2'
26n
2t
x,
30
3t
34
39
24 -E 2l Scpambcr 1992
2l Scptcmbct 1992
2l Scpambcr 1992
2l Scptembct 1992
2l Scpoobcr 1992
21 SGptcnbcr 1992
21 Scpambct 1992
2l Scptcmbct 1992
2l Scptaobct 1992
2l Scptcmbct 1992
2l Scpambct 1992
2l Scptambct 1992
2l Scptcobct 1992
2l Scptcmbct 1992
2l Scpambct l99/l
34A-37
4/,-47A
4t.49
50
--
Scction Itr - Empty Dnrm Prcparatioasod DispoEal
. 2l Scptcmbcr 1992
. 2l lhptcmbcr 192
21 SGptcnbcr 1992
2l Scptcmbor 1992
2l ScptcnbGr 1992
2l Scptcmbcr 1992
2l SGptcmbcs lD2
21 Scptcmbcr 1992
2l Scptambc 192
2l Scpambd 1992
2l Scptcmbor 1992
2l Scptambc 1992
2l Scptcmbcr 1992
21 Scptcobcr 1992
2l Scptcmbcr 1992
2l Scptcmbc 1992
2l Scptcmbcr 1992
2l Scpambcr 192
2l Scptcmbcr 192
2l Scpambo 1992
2l Scptcmbc 1992
2l Scptcmbc 1992
2l Scpamba 192
2l Scptcmbcr 1992
2l Scptcmbcr 1992
13 Dcccmbcr 1991
2l Scptcmbc 1992
2l Scpambor 1992
6U€.t
lrrtr llc. 12
2t Spioosor l9a2
22lluirc 1992
5l
52
5t
54
55
57
6l
62
6'
-56
-60
. . 2l Scptambor 1992
63A- il
Scction IV - Suop;
ScctionV - Empty DruE!
656
et
6t
7t
69 -70
72 -73
Tablc and Figurcr75-76 .,,.2lScptcmb*1992
9t
95
tt-
92-
71
n
7t
79
80u
t2
t6n
96
- 8:iA
97 -9t
99 - 100 l3lhccmbcr l99l
t02-rcg
l0l
lr0
2l Scptcnbcr 1992
13 Doccmbcr l99l
2l Scpambcr 1992lll . . 13 Dcccmbcr 191
1B
o*t.rbrtr fo. t22t arplot$or faC2
Ap,pcDdixcr
tt2lt3 ..13 Deccnbcr 191
2l Scptcmbcr 1992
2l Scptcmbcr 1992
2l Scptcmbc 1992
114 ..u5-u9
r39
t45
tm
t2t
tz2IB
t24
IE
t26tn
13lt2
t36
t37
13t
lrO
150
2l Scpambcr 1992
13 Dcccmbcr 191
1l Itferch 1992
ll Mrsch 1992
2l Scptcmbc 1992
13 Dccaobc 1991
2jlllurrp 1992-130 .
-135 .
13 Dcccmbcr l9l
13 Dcccobcr l9t
2l Scptambc 1992
13 Dcccobcr l9l
2l Scptcmbo 1992
2l Scpanbcr 1992
2l Sopambcr 1992
2l Scptcmbcr 1992
2l Scpambcr 1992
Indcx ts - t49
lil - 152 ll lr,Iarch 1992
1C
GIU-3.1
Issue No. Ul
2f Sqtclnba 1992
MEFACE
llig docttucot, GM-3.l,Issuc 12, supcrscdca B$rc ll c,hich b to bc discgrdcd. This docuncat
sup,plics inshrtioEs Dcccasary fos dispmal of wastc netcdds throrigh rhc E-fl)I, M;136, M-186,
M-336A, d M-rc5 dispos.l facilitics rad nrycrscdcs buildiag plaoniag docuocnr u,hich dalc ro
6c disposd prcc6$ Pcer rcvicw is cascotial b cosurc that insuuetions arc sccuratc and rerflc11snl linc conditionr. If iucqtrrcics ato found iu Setionc I, IIL IV or V, plcasc scod reqncstcd
cteoges on e Spccd la* (Foo TC lsfr) b Supcrvisor, Eavironnconl Vlastc Disp$al, lrgs
30fB. If insurcicr are found in Scctioa tr; plcerc rcod reqrcstcd chaagcs oa e Spocd Lacr
(Foru TC IjIT) to Supcrvisor, Eavimnocolrl Eezrrdons Wasto, tvf/S 3Ol. lAc usc of ra a*crisk() b idi@ chengn har mJ bcco u'ritd is thir docoocat duo to tho cxtmsivc cbeagcs fton Is$c
11. Nsw rdditioot wiU bo ttodcrliacd 5 trigfili$t chr8ps to thc docuDcot. Dclctioas ia the text
will bc showu bv lining out. F ch tiuo t Dcrv sa of chrogo pcger b isnrcd, thc 'old' uodcdiacs l$llinc outs frou 6o pevious changc will bo dclced. Bsuo 12 should bo rced c{Gfutly frou covcr o
covcr rod usd i! itt cotiray. Aay vrdedoa iou ttc proccercs outlincd Eust bo covcred wi6 shop
plroaing aod hevo prior appmvrl frou tho Eavircnncoal Wass Disposel (EWD) Scction or 6c
Euvimnncol Eezrrdous W.stc (EUD Scctioa of thc Wsstc ldrargencnt aod Eavimnrncaol
Scrviccs Dcprrrucot, Stmtcgic Operationr.
EWD Tcl@oer"agcr R.gistry
l. Wrstc PmpcllaotlEnpty Drunr Ext 520, Pagcr 4t0
Ext 4lZ), Pe&E036
Ef,t 82:i4, PeSer 04O
2. M-136 Arta Forcoro (Dey Shn Oof)
3. Gcoerel gropclt ot Weste Dispoc.l
4. OttcE ftsre Dispos.l . . . Ext 41205. Gcocral Qucstionr About Snopc Ext 6299
7.6 Trerh Tilck OpcElos (Dey Shifi Oaly)Fllt2S2nJ,, h8er 039t l Sunp Tntck Opcralor (Dey Shn Ody) . . En 2520, Pagpr qrt
9.! Stnegic Trouble C.ll Dcsk . . . . E$ 24j5
EEW Tdahm/Pagc R4istry
t. Esrdouc Slasto Arce Group l-crdrl
(Dey Shift Only)Fst 5m, Pagcr 960
Cdlutsphooc ..... (&J.DTD6ZS}a Erzrdouc WrooPichp CrEwr (Dry Shifr Only) . .H,f,fi2SiEEw3. GGocrrl Qucrtiou.d ort6 wrnc Dirpool . . . . . cdluLr (&l) 720otj
o o . . . . . . Ert58fi)or424t4. Spil RccponscsFcidin . . . . . . . . . . . . Ext 3923, Ccllulr TD4tn
Spro Opadoor t! dcrrdoPGd itr wr ScsT LIcid Teg (SP 0frD. Iactnrdolr on rho uso of6L nt rrc ftood il Amadr I. St&gh Opalioar, % rod Corpoao usc 6c
scrlp lr,fehl Ter (rc (tr7t) frood il eppcodr L colarL urorrcocc Folisy or ulon3pldry dmo6 for rcqufulocc. GMd.f ril r loojer etr o eddrccr rll 6c qGcifc
rcqutcoco
l,[slJ
GM€.I
Bsue No. ljl
2l Septcmber l99l
Tho llazardoug Waste Ptopcllaat I$cl (IC 8159) shdl bc placed oa all propcllaot, cxplosivc or
pymtochaic (PEP) wast€s (including conraminatcd $astcs). It is m additional requirtmcnt to thc
Screp l\,Idcrid Tag CfC 0t?8 or SP O87t), Scrap kbcl CfC t064L IMO, DD 1t49, ac.
Tho \[/astc I$Gl CfC 8Df) shall bc placcd ea gll a6nhrzrndous itcms atrd wiU bc sn edditioD8l
rcquirem-cm !o thc Asbcstos Ilbd CfC 4445). Thc Ilazardous Stasre I$d (IC 7l&t) shall continuc
to bo plaad oa all hazardous qrastcs cxccpt propcllaot wasEs.
ltc Wastc DisPosel Noticc CIC 8lZ) will bc left by Wastc Meoa&Ecot aad Envimnncaal Serviccs
pcrsonnd' with itcms placed on an agroved wsstc dock sirnp, or trash bia, urtich hevc a
discleercy stop,ping the disposat crcun fron picking up.or rc,ooving tho itcm(s). Thc Noticc will
pmvidc irtntc{iols to allow a spccdy rcsolution of thc discrqorcy and piclcup of thc itcm(s).
A SaloUitc Ilazardous wastc I$ef GC 8190) nus bc placcd on any contrincr 8t e satcllito
acc.umulstiotr erEa inncdiaaly uficn any enount of hazardors wastc is placcd in thc coaaincr.
Thc appropdar DOT Ilazed class l$cl must bc afrachcd in an updght position adjaccnt to rho
applicablc Hazardous Wastc or Sarcllito llazadous Wastc l:bcl on thc uppcr onc-third of aoy
hrzadous nrasto containcr.
Thc Ilazrrdou U/sstc Profilc Dats (IIWPD) shea is r dosuncst gcnaarcd by Eavimnmeaal
Ilezardoug wastc (EXIW) to give tho buildings all tho &te thcy nccd on all their wesls strca6s to
conply with thc EPA srd DCII r4uletions for disposal. Tho &tr wiU bc cveilablo cirhcr in hard
copics or on thc VAX conputcr systcn.
To ordcr reqrrired labcls (c.9., Salcllitc Ilazadous Westc ltbcl, Forn TC tlg0), from Stotcs, thc
Stock Nunber will bc 26 - followed by tum zeros, aad then tho form numbcr or 26-@8190.
Buildirg/Arca narcscntanve(s) shall be dcsigDatcd to rcprcscnt all buildings/arcas rrhich have an
approved dock or sump for pickup of wastc matcrials. This represcoativc is assigacd by supcrvisionb bc thc ooEtrct person(s) for mattcrs coaccrning qnstc dispossl aod/or lvostc Olsposd Xoticcs.Itis rcprescotadvc is responsiblc for thc tincly rcsolutioa of proccdural Ossrceooclcs. It is tho
rcsponsibility of cach building/arca sqrcrvisor o iabtn Wsstc Manegcmcot aad Eavironnenal
Scrviocs of thc name(s) of their cutteot rcprescnudveG).
Building pcrsooncl Eust iD$inilc a mahod of marcrial inspoction of wasrc contaiDcrs prior to
placcmcot on a8 8P[rlovod rrasc doc& or ia a bin (in spccificd cascs) to cnsurE corest prcparation
procoaurcs hevc bccn follourod.
Hrzadous rnstcs .od PEP unstca (includinghazardons eDd PEP conamioatcd $,tstcrvotc4 offcred
for trrnsportation on prblic highrmys frou Tcst, Plant ltr, x-20, A-16, H-Z or z-12 must bcmupenicd by e signod Uniforn Hazrrdons lVtstc Msoiftst. Asbcstos $rastc from thc ssnc trtos
bdng 3cot for disposd.lthc M-336A Ssoitery lrodfill Eust bc acconpenicd by ra Asbcstos \Vastc
Shipmcot REod (Forn Tc tl7r. Thc Unifuru Hazrrdous wesrc tvtroitst ria esUsos Wssrc
shipnoot Rmtd erc 'chlil of orstody'dosuncr8 u,tich rccoutrt fur ell tnnsftrs of rcguldcd
nrlcrids fron thc 'gcacnuor' of tho $,ls!o to thc finrl disposition of ltc urastc et 6c Treatmeat,
Sloregc, and Dispod frility.
,[}LN
GM-3.1
IssuG No. 12
2f Septetnbcr DqZ
Instnrc-tioos erc given for thc disposal of matcrials for which thc common n8nc, MSDS, II\ilPD, orMII$.rc uDtDowr 08 erE not arnilablc in Scction tr, Paragraph 9.4.
i
Instnrc{iou arp dso givco on spccific rcquiremcnts for btrildings with we*c*alcr sunps. Rcfercncc
is EdG !o tho llrzerd CommunicationPmgram ufiich is a legd requiremeat for pasonncl who wortwi6 or arc e.:rposod to hazardous nalcrials.
Insrustiou oo wsstc acctmulatioa areas hgvc.bcon givca in Scction tr, Paragnph lt. Explaoations
oo rcquircEcots for sarallitc and gGday stontic areas and dock critcria requircmoots for all nrasto
rps{Eutado[ arcr8 arc dso grvco. :
I! thb doc{tncot ttc umrds '$dl,' 'willr' a[d 'nust' arc uscd to dcmtc thiu thc roquircmeat is
'nsodatorlr. lto word 'should' is uscd for a nonnrodrrory dcairc or pncfcr:od soursc of action.
rLc *otd 'Dly' is uscd for an accaaCto or suggcstcd coursc of actioa.
This docuncnt hs bcco issucd in a threc-ringed bindcr so thu documcat upgradc pages can bc
ioscrted. Coptcc of GM-3.1, Issuc 12, will bc is$ld and controllod through Speco Opctations' Print
Crib u A-2. Whco a chaogc is nadc, tho dare thu chaogc unas publishcd will appear'on tho thirdlirc is thc qryct right hsrd corDcr of cac,h pagc. A list of the activc poges ia thc marusl will
accoEpcoy my chrages nrdc o thc docomcot. frc uscE Eust tfirD the initidcd vcrificatioa pagc
to thc A-2 kint Crib, arcntion Gloria, It[ail Stop 515A3, assnring reccip of aoy page chaoges.
IY9DDLT,
. GM-3.r
Bsuc No. ljl
2f Septcmbc Dql
4.
5.
TABIJ OF CONTENTS
sECTION I - INEXTT PROPF',TI 'r.IT nND LIW Ulrtnnr pnrpmlrroN
1. INIRODUEITON
t. REFERENCES
MATERHIS AND EOIMMENT
SPECIAL SAFFTT AI{D HEALTII REOT'IREMEIYTS5.I PERSONALPROIECTTVEEQI'IPMENT5.2 IIAZARDCOMMI,'MCATIONPROGRAM
6. MATERIAL INSPECNON6.I ESTABLI$IPROCEDT'RES6.2 SEOREGATE MATERIAIS
7. DISPOSAL PREPARATION7.1 GENERALINSTRUCTIONS7.2 CI.ASS I.3 PROPELI.AI{TS A}.ID ILLI'MINAI$TS7.3 PREPARATION OF CI.ASS I.3 PROPELI.AIVT IN SLING BAGS7.4 HIGII.ENERGY WASTE MATERIAIS7.5 St BMDGS AIID PREMD(ES (OIIIER THAN BII{DER pREMDg7.6 PYROIECHMCMAIERIAIS7.7 I.ABORATORYSAIVTPIEHARD$,ARE7.I LOADED s-IN. CP CASES AI{D POI'I{D CIIARGES7.9 DIITSECTED CASE PROPELI.AT.IT
GAS GENERAI{T
PROPEII.A}.IT.COI{TAT.IINAIED SOLVENTS
PROPELLAI{I CONTAIVIINAIED ALt MINI M pOwDER
PROPELI.AI{T O)qDIZERS
INERT PROPELI.AIVT
?.)5 PEP€oIITAMINAIED. ASBESTOS-CONTAINING MATERIAL
TRANSFORIATION OF PROPELI.AI{T AND ILLI'MINANT
TO WASTE D@IOSHEDt.I }VASIE DOCK CRITERIA
9. PICKTJP CRTERIA
t
I
I
4
4
5
5
5
6
6
6
7
7
7
7
7
l0tl
t2
l3
t4
6
6
9ll
l3
r5
l6
l6
t7
t7
t7
t7Itn
2ln
E.
t2
x2
x2,
v9[Dt.r
GM-3.1
Issue No. lil
2l Septonbc 1992
2.
3.
4.
5.
CONTENTII (cong
SECTION TI . IIAZARDOUS $'ASTES PREPARATION
1.INIRODUCITON
DEFINIIIONS
REFERENCES
MAIERIAIS AI{D EOI.'IPMETfr
SPECIAL SAFETY ANN }IFAITII REOI'IREMENTS5.1 PERITONAL PROIECTION EQT IPMENT5.2 IIAZARDCOMMT'MCATIONPROGRAM
6.DISPOSAL INSTRUETIONS FOR LIOI'ID IIAZARbUS WASTE6.I ESTAELISHPROCEDT'RES6.2 INSPECT CONTAINER INIEGRITY6.I MARK THE CONTAINER6.4 PTACE lEE WA.SIE IN TIIE CONTAINER6.5 SEAL CONTAINER6.6 PREPARE FOR SHIPMENT
6.7 wAsIE TRANSFER/OVERPACX (OPTIONAL)
24
24
u
29
30
30
30
3l
32
32
32
92
33
3t
34
34
34
35
35
35
35
36
t6
36
t7
37
37
t7
t7
37
3t
t.l
t.2
t.3
t.4
t.
6.t PICXCT'P CRITERH
7.DISPOSAL INSTRUCTIONS FOR SOLID IIAZARDOT'SI WASTE7.1 EIITABLISHPROCEDT'RES7.2 EITTABLISHCONTAINERINIEGRITY7.I MARK THE CONTAINER7.4 PIACE TIIE WASIE IN THE CONTAINER7.5 SEAL CONTAINER7.6 PREPARE FOR SHIPMENT7.7 WASIE OVERPACK (OPIIONAL)7.I PICKT'P CRITERIA
DISPOSAL INSTRUCTIONS FOR. SMALL OUAI{TITIES OF
IIAZARDOT'TI WASTE
EI'TADLISH PROCEDT'RES
PACKAGE WASIE
IDET{TIFT WASIE
PTCKI,'P CRITERIA
vltD$r.d
GM-3.1
Issue No. lrZ
2l Septanbq 1992
CONTENTS (cong
9. HAZARDOUS WASTE PROFIIT DATA SYSTEM
INFORMATION REISIEVAL INSTRUCTIONS
BUILDING SPECIFIC IIAZARDOUS WASIE PROFILE DATA
MAIERIAI,S WnxI MItrSI, IIAZARDOUS WASTE PROFILE DATA . . .
MATERHIJ WITII NO MIISI, IIAZARDOUS WASTE PROFILE DATA
IO. DISFOSAL OF SPECIFIC WASTES AND/OR SPECIFIC WASTE STREAMS . . .IO.T EMPIY CONTAINERSlo.2 soLvENr wAsIEIO.3 GNEASE AIrID OIL10.4 coRRosrvEwAsrEIO.5 WASIE PAINT
10.6 SPRAY OR AEROSOL CAI{SIO.7 LIGIIT BT'LBSlo.t BATTERIES10.9 PROPELI.AI{T PREMD( AT.ID PREMD( WASIE
TO.IO ALT'MINT'MPOV'DER
IO.TI DRAEGIER TT'BES
IO.I2 OXIDIZERS AT.ID ORGAITIIC PERO'SDES
IO.I3 C/IIIER OXIDIZERS
10.14 MT'LTIPART STOCK NT'MBER MATERIAISIO.I5 LEAD SOLDER
10.16 PIIOTOGRAPHIC CHEMICAIS
IO.I7 WASIE ISOCTA}IATE PREPARATIONIO.It RESPTRATOR CARTRIDGES
IO.I9 SOLVENT COMAIVfiNAIED INERT PROPELI.AI{T WASTE
11. WASTF ACCLTMULA*TION AREASII.I NINETY.DAY IIAZARDOUS WASTE STORAGE AREASll.2 SATELUIE IIAZARDOUS WASIE ACC[ MULA-TION AREASU3 WASIE DOCK CRITERIA
SECIION M. OTHER WASTE PREPARATION
I. INTRODUCTIONI.I I.AEELINGREQI'IREMENTS1.2 ENIRY RESTRICTIONS
9.1
9.2
9.3
9.4
3t
38
3t
3t
39
,9
39
?9
40
4la
4l
4lu
45
,llt
4566
45
46
47
47
47
4t
47A
OA
49
49
5l
5l
5l
51
2.
t.
4.
REFERENCES
DEFINNONS s2
54
54
E$r.It
MATERIAIS AI{D EOT'IPMENT
vii
GM-3.1
Issue No. ljl
21 Septcmb€r f992
CONTED{IIi (conO
5. SPECIAL SAFETY AI{D IIEALTII REOT]IREMEI{TS5.1 PERSONAL PROIECTI. EQUTPMENT5.2 TRANSFERREQT'IREMENN
6. SAMTARY LAI{DFILL
54
54
55
55
55
56
56
56
57
57
57
57
5t
5t
5t
5t
58
58
59
60
60
60
6l
61a
62
63
63
63
63
g
6.1
6.2
6.3
6.4
6.5
6.6
BASIC POUCY
CAFEIERIAWASTE ...
DRAINED OIL FILTERS
TAG EIIIDS, PHENOLIC PIECES, AI{D PI.ASTER
NTIISANCE DUSTS
ASBESTOS WASTES
7. DISPOSAL PREPARATION7.1 CONTAINERS7.2 I-ABELING REQT IREMENTS7.3 G:ENERALINSIRUCTIONS
t. II{DUSTRHL WASTE TRENCIIESt.l NONHAZARDOUSWASTESt.2 AP DESICCANT WASTESt.3 EA 934 AT{D SIMILAR TWGPART ADHESTVESt.4 NONHAZARDOUS INERT PROPELLANT
9. MATERHL GOING TO OTHER ONSITE COLLECTION/DISPOSAL AREAS9.1 NONHAZARDOUS LrQt rD WASTES9.2 WASTE OIL .9.3 DISPOSAL OF WASTE AMMONIUM IIYDROXIDE SOLUTION9.4 DISFOSAL OF WASTE PMASSIUM CTILORIDE9.5 WASTE AMTIFREEZE9.6 SALVAGEABLE MATERIAIS
10. sA.IFr r rTF PLANTS
IO.T GARBAGE DISPOSALIO.2 SATELLIIE PLANT I.ABEIJNG REQT'IREMENTSIO.3 ASBESTOS WASTE SHIPMENTS
1I. PICKT'P ERITERIA
fiDr.rt vlll
GM€.I
Issue No. 12
2l SepaembGr f992
COIYTENTS (on0
t
2.
3.
4.
3.
4.
SECTION TV . EMPTY DRUM PREPARATION AI{D DISPOSAL
1. INIRODUETION
DEFIMTIONS
REFERENCES
EMPTY DRUM PREPARATION4.1 I.ABELING INSTRUCIIONS4.2 EMPTY DRUM SEGREGATION
5. MATERIAL INSPECTION5.1 ESTABUSHPROCEDT'RES5.2 DRUM INSPECTION5.3 DRUM TRANSFER
6. PICKUP ERITFRIA
7.SATELLITE PLANTS
7.t SHIPMENTS FROM H-7 (CLEARFTELD)7.2 SEIPMENTS FROM X-20 (BRrGrrAM Crr)
8. DISPOSMON OF EMPTY DRUMS
SECTION V. SUMPS
l.INTRODUETION
2. DEFIMTIONS
REFFRENCES
OPERATING REOTTIREMENTS4.r IIAZARDOUS WASIE SUMP REQT IREI\TENTS4.2 NONIIAZARDOUS WASTE SUMP REQT TREMENTS
5. WASTEWATER TREATMENT FACILITY5.I GENERALINSTRUCTIONS5.2 SPIIJS OR ACCIDENTAL DISCIIARGES
65
65
65
66
666
66
6I
6l
67
6t
6t
6t
6t
@
69
@
70
70
70
70
7t
7t
7l
t&rn ix
GM-3.1
Is$e No. lil
2l Septcmbcr Dql
CONTENTS (con0.
6. DAILY SUMP INSPECTION 7l
7t
72
72
T2
72
73
73
73
74
74
74
75
n
7t
82
83
t6
t6
t6
t7
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t9
90
92
93
6.I GENERALINSTRUCTIONS6.2 SECOI{DARY CONTAINMENT
7. INSPEETION SHEET
8. DISCREPANCIESt.I GENERALINSIRUCTIONSt.2 SUMP II{DICATOR PANEL
9. SUMP PUMPING9.I DETERMINING WHEN TO PUMP9.2 ST'MP TRUO( OPERATOR ASSISTANCE9.3 SOLIDS
IO. PICKUP CRITERIA
LIST OF TABLES ANN FTGURES
TABLE I WASTE ACCUMT'I.ATION AREAS
TABLE tr M.136 WASTE REACTIVE II.IATERHL DISPOSAL CATEGORIES
AND CI.ASSIFICATION GROT'PS
TABI.E M M.136 TRENCH LOCATION BY GROT'P TYPE
TABLE IV COMAINER IT{ARKING, PREPARATION, AI{D I.ABEIS
APPROVED HAZARDOUS WASTE DISPOSAL CONTAINERS . .
APPROVED DRUM LOCK RING
APPRO1TED BUNG PLUGS
TABLE V WASTE DESENSTTUTNG REQT TREMENTS
TABLE VI HAZARDOUS WASTE TR,OM NONSPECIFIC SOURCES
EAZARDOUS WASTE FROM SPESFIC SOURCES
TABLE VII CIIARACTERISTIC HAZARDOUS WASTE
TABLE VItr NG WASTEf,'ATER
TABLE D( HMX WASTEWATER
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auday
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cilorolluorocrrtoor
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c&coler poc
oooollcd procco iorrucioor
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Fd.trl OGllW.tlrActood qlorivc fornulcioa
hridoaoirilc
Trldot-t oirilc
dimlylfororoido
dircbrgs Dooitorilt rcporr
dlo.tyl.dip.to
dlocryl odcrto
Dcarnnaof Trraryorutba
diroqrrcyrcpoa
TrUoc.tr oirdlo
caoxy ori4qcotcooay hrzrrdour obcroco
hvirooocotrl llrzrrdour Wro
crviloucotd oooioda3
Erlrcoocotel Opcrdooe
cquiocot opcntiog procoduor
ocruion prooduro (toricsy
daoiortba)
Erboooml Protocdoo Agcocy
foclcogy Ptrnriat 1a!
Cooouofy R[ht-to-IwAcaiylcpropylcdlcmaos
Gutod
eoc6acy RraoorGrido
EriruoolWrrc Dirpodqlodvoouirl
Fdal hcicftlq Fuodcidc, roO
RodoicidcActual qutrdooilodcnl rGdc
FfIn .....s..
GC/MS
GOCO .
@t..
GSHM
IIARM
HPA
HML
HMX
HTDB
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IT'PAC
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MNB
MSDS
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NBR
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N.O.S.
LISI OF ACRONYMS
GM€.1
Issue No. 12
2l Septembcr DqZ
Fouicr trrarforu idmrGd(loorcopy)
jrr chrooerogrrpUnar
rPcooctry
twcilocat o*tdl @ltrrGloF
Acr&d
SCoGsd procc.. ioEucsioa
Gcoonl S.fdy .d HGaIn M.oud
hl3bpocdeatirdrnirdlc
hi$.cmcbosy prrtiadrto dr
(f,trr)
brzudourortaid lic
IIc lilriry'r Erplorivo
(cyclocnoabylcoc tctnaiaeoioc)
tydroxyl-tcruiaetod polybutrdicoc
@{5 polyuct)
hcrtiag, vcotiletioo, ud rir
coditbaiag
hrzrrdourmlc
lLzrrdour Srrlo hofilo Dlre
Itcarrtod lajhhr SuppocbE!.| oovo ordct
Ltpholooo diirccyautc
iodurhl prctacarocot ptogt r[iollltba rctoruba plogrro
Iioorartbod Uoioa of hrc rd
Appli.d Chcoilr
iodu*rid wecc tlooch
pooriun chloridolorrt rchicv.blc coirioo ntc
liquid cpory rtrio
lrCoruorytehaicd prcccr
liquid tbcnd tncrtocot rrc.
mhyl eziridilyl pborphiao oridoriyl aiyl lcctooc
D.laid [c.|ti rod r.fcty
ioforurtioo
oetcthl rwir:wboudogid lfcty dlt .hGa
ac rp,plftrbloor oot ryrilrblo
llrilc butrdicoo rubbcr
m crrtoo rcquircd
N.doo.l Eoigbor Studlrdr for
llsrdourAir no[ut stt
Ndood Firohotabo
ArEciab!
ltqlycoril
Ndoo.l lorhlo for Occqrtloort
S.f.ay.d HG.lttd ottcrvir ?seirlodl{dod nogoorc Ccotcrlorrararblocooir
HW
Its
IMO
IDDI
IPP
NP
rer.d xll
IIIRC
ITIPDES
OB/OD
LIST OF ACROIYYITfiS (conO
Nrti(ml Polhnrr Diralr.r3e TRACS . . .* . .
Elirminrtio Syrcilr
opco buroing/qco dctoo.tin TSCA .
octdcyl itost/.tr1t TSD .orptizOU opcildng TSDP .
irnttgbmoFdoo.lrEdinirryccdon U.N.O. ......
oahctrirc rlgulrt d nuiel UACC .
Ooerertonl Srfcty Comnioo IrBAQ .
Oocnp.doml Srfcty.trd Hc.Ih ITBSIIW
Adoinialin
potrrui,
polyhtdian rcrylmitila (HB
polyrr)
polpttothoe biplilsryl
procc.. ch.oSo odcr
gamrriUoqpooru lsrcl
propolbr, crpbdvo, p3tlot*hi,
prc&ryfu jrottp
trrrtrc of roiafoy/dtr&nty
plocG.a iniuctiool
fcrofryor
pnbliclyolnd trcrlncil rprttpqurl pdoctim GquiFtG.t
prcr pcr millioo
Dctrcriotr of rignifictc
d*altntioo
T"ifY/dLt ncc
RmrcoCooravrtion ad
noqtcry ec
cr/cloofoo(@
EPA RGti,o.l Officq Danu
qudfty
dlicoc rutrbcr corryouod
Srycrnna Amodrrulr radRafiortdn Ac
rtfirty lrodfill
rolf-corrind bc.tlrioS .gprilrrerll tratochc*rl bdlidc
tnirib
Ti[plururioo cqtol .!dqncstHuo (ph)
rdid rocb nrorrhlbEb cdirE
rolid rro mttrgGod uoilttuylpqto1o
bdcfty clrurctcirio lorclu
DIE itrr
taldld didrtrr
thrrhold tini v.bo
t*rtrytotatrr aiduloEl oqrdo coqouod
ffiotofiqr
uc
WMES
GM-3.1
Issuc No. Ul
2l Septanbor 1991
Tnioiag Rmrdr !d Coiltol
Strtcm
Toric $baarpo Cortrol Ac
E!.Ertcot ttongo sd dirpoad
ttt r!trGrrt, ion8o, srd dirFod
f.dtity
Uoibd Nrtioor Orguam
Utrh & Conrqvuiolr Corunicoo
Ut h Burc.u of Air Qdity
Utrh Burcu of Solit erd
Ilzrrdour \[rlc
uodcrgtoud iqiGcdon coorol
Utdr Ocorprdood Srfay sd
Hc.Xh
Utrh Pollutur Dirchlrgo
Eliminlirn Sytan
udcqpuf rorr3s t ofr
ullrvioh
vohib oryub conryomal
'tf,ero Menrgcrncil sd
Eavisugrd Scrviccr
mtcc +.litY critorie
W.rtch dcty boud
lxlrlaultcf,
*rra.ertE trcrtrrcrt frcility
crudin&od doublc br*
Grcedlr)
OSIIA
oDt
@t
ORI
onM
osc
P/fPl
PCB
PCO
PBAN
PEL
PEP
PO
pHH.
m(
uo$t .
T'PDES
USTtv
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wsB
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WWTF
XIJB .
FOTW
PPE
PI,ln
PSD
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SANA
SI.F
SCBA
slcBlu
sFcc
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sTc
swldu
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TCI'
TD
TLV
TOC
TNT
TMEII.I
rlDt.tfl dii
SECTION I.INENT PROPELLAI\IT AT{D LTYE
MAIERIAL PREPARATION
1. INIRODUCTION
Ilis scctioa prcvidcs insnrstions for
pcparing aod rclocatiag wastc pmpellaat
aod othe,t livc natcrids from thc opcrating
rrcas to e Wastc lvlaoagcment aod
Eovironmcaal Scrviccs-approvcd nnstc
dock or shcd. (Scc Tablc I for thc list of
ap,provod docks.)
Tho hazardous nalcrial disposal ercas at M-
136,I-10K, afrIo/.X2i arc tho only
locations eutorizcd for disposal of wastc
rad other hazardous wastc
ndcsisls. Advancd Talnobgy
L&orotqia Ttlnbal hocdtrc (L7?)
L7?-24DOI&,'Disposal of Wastc
Marcrids in lhc Pleat Itr Burning Trcach,'
will supcrsodc GM-3.1 for Earcdal disposd
at thc Plaa Itr Buming Gmuads. Advarcd
Tcdttolog Lafuromria (RiL:D lfrs)
Tarlaical Prccdurc (LTP ) L7?-243H3 3 E,
'Ileodling rd Disposal of Explosives aod
PS6otcchaics.t thc High Ihzsrd Disposd
Plt, I-10K, South of Building I-10,'will
supctscdc GM-3.1 for matcdal disposal u
thc l-l0KBuming Ptt. All propcltaat aad
livc nrrcrial hadling proccdures Dust moet
thc requirtocnB of thc cunent issue of
GM-3.1 aod eny othc ap,pliceblo
dosuncnE.
NOlts
hopctlon dbpsal crctt's ,t 6y bc contrctd
as dacribd in tlu EWD rcgistryfottnd on
pagc iL
,[o2.t
GM-3.1
Issue No. ljl
2l Septanber 1992
2. DEFIMIIONS
BuilqlS/Ar,ea Repmscntative - All
buildings/arlos uftich havc an approvcd
dock for picknp of wastc matcrials must
hevc e desigreicd rqntscnativo. ltig
rcp,rcsootativc is assigucd by supewision to
bc thc c{rtrtact pcrson(s) for mattcrs
conccraing weste disposd aod/or Wastc
Disposel Notices (Forn TC tl24). This
fqprrscotrtivc is rcsponsiblc for the tincly
rccolution of proccdural discrepaocics. It is
tho rcsponsibility of each buildiag/area
opcrvisor to iaforn Environnental Westc
Dsposel of thc namc(s) of thcir currcnt
rcP'rcscntativc(s).
Ceution - Dcsignatcs activitics in which
&nagc to cquipmcnt Eay occur.
Compoeite Propellant - A non-nitratcd,
phsticizcd pmpellant containing aa oxidizcr
(anmonium pcrchloraa), aluminun, aod e
biDdcr Eetdr. Exaoplcs iu this proccdurc
uc nornally U.N.O. Classification 1.3
nrtcrids such as SRM propcllaat.
Crocstinked llouble Basc Propellant
(XLDB) - A high-cncrgy propellaat
conAining nitratc plasticizcrs such as
nitroglyccrin or TMEIN and dso
conuining nitrocellulosc as an encrgaic
erors6-linking agegt. Exanplc: U.N.O.
Classification l.l explosivcs such as D-5
propcllaot.
Dcontominrtion - To matc safc by
dinineting thc prcscncc of PEP wastcs.
Dcconaandnation Critcria -
lX Bulkofcontrninaatremovcd. Sonc
residuc nay rcnain.
3X All surfaccs previorsly cxposcd to
contaniorot arc aow visibly frec of
coataniDdion.
I
GM-3.1
Bsue No. 12
2l Sbprcmber 1992
5X Chc,mically frec of contrminsnt.
Rcquircs disasscmbly aod clcaoing by
onc of thc rPP,rcrred ncthods. This
,rr.t la
idcntificetion is uscd in all cascs
rrhcrp e flamc is uscd, ufrcn spart-
eroArciag rro* (dtiling, sawing, ctc.)
ir pcrforncd, or if thc itcn is t Lc[
out of e live arpa for work or scrap.
EPA - U. S. Eovironncntal hotection
A3eocy.
Enplodves, UN.O. Cfas 1.1 (DOT Class
netcrial thlt is a blast hgard. Il,less
daonation Eay occur whcn aoy lnrtion of
tho nefcrial b itritietod by any EceDs.
Erplocivos, UJ{.O. C'lass 13 (DOI Class
B) - Clr$ 1.3 metcrials arc dofincd in
gencrel as thosc cxplosivcs tha fuocion by
rapid combustion rathcr thao dctonation.
Ilenmeblc Liquid - Dcfitrcd by DOf as
aay liErid heving a flash point -5i l4()'F.
FuGb - Mrfiedals addcd to a propcllaot mix
rhrt cso bc oxidized to producc enelgy aad
hig[ tcmpcrstlrca during combtrstion.
Ilo,ror.6 Oas - DOT h.,rd class as
dcfiDGd by 49 CFR 172. Exemples of
hrard clssscs aru flamnablc (3),
ootmsivc (t), oxidizct (t, 8od poison (O.
Esrdous llflrteriel - Aay matorid having
chrractcristics u,hich E8y bc hrrmful to
humea hc.l6 or thc cnvirronmcot.
rr.aadous Wesac - Aay discsrdcd, off-
speificetion, or spillcd natcrial in ono or
norc of tho following catcgorics: ignitablc,
r!&'tiyo, cormcivo, toxic, or lislcd al
hurdour unrE h 4() CFR 2*265 ot
Scction II of thc Utrh Hezrdous Wtstc
UrnrgcocoRnlcs. Thcso rrrcriels rrc
idcodfid on thc buildins Ilezrrdou Wlslo
Profilo h ( II\ilPD) shca3.
GM-3.1
Issue No. lil
2l Septembcr 1992
Ilozrdous Wasilc Propdlant l"abet (Fotm
TC 8159) - A3ll4by 5 ll2 in. grecn label
witi Hrck lcmcdng. Thc llazardous Wastc
noecttat kbot shdl be ptaccd oa dl
pmpellaat, cxplosivc, and pyrotcchnic
(PP) ooateniDatcd D.tsrids 8!d dl PEP
coffioiaarcd unstc bogs. Hazrrdous Wastc
noecttaot kbcls Dry b ordcrcd fron
Stotcc (Stock No. 02640t159).
Ilsrdors l[este Storage - Areas
dcsiSDdcd for thc stomgc of hazardous
wagto narcrids.
Hlgh+norgy Itiltteriab - A tcrn uscd to
iaclu& both high-cnergy propellaorc aad
high cxplosivcs.
mgUcncrgy Propcllants - Propellaats
oontrining solid or liquid high-cxplosivc
Erlcrids, such as III\d(, RDX, or NG.
Thoy are calld Class l.l cxplosives.
XLDB propcllant is aa cxamplc of a high-
cocrSy propcllent.
H[b Explofves - Mstaial thu ceo bo
cspetd !o dAonslc aod coasume thc entirp
nesg iostaoteaorsly ufren a smdl ponion
ir mbjcctod to firc, !o scyerc concussion or
iupect, to tho impulsc of ao initiating
r8pnt, or to thc cffcc,t of a considcrable
dfuchsrge of caergy from without.
Matcriels of this catcgory arc considqed
mrss daoosting (INf, RDX, CIO{-3,
HI\,D(,ITUEIN, NG).
Inert Ililsterisl - hopcllant and propcllaot
ingrcdicnt nixarrcs that do not provido
coough orygca to suslai! combustion and
hrvc bcco tcatd to daaniDc that thcy do
rctcoffiin rny hrzsrdous nastc
chrnstcristics (se Scctioa III).
Ilvc ttilrterial - Propcll8lt end ptopelleot
Brc nngto coauining oxidizcrs.
M-l36livo rnrncr rre cetcaorizcd bclow:
2,rcL2
A - Clasr 1.3 conlrositc propcllaot without
HMX eod/orRDX
B - CL$ 1.3 compositc propollmt with
HID( aod/orRDX
C - Chrr l.l litralc cstcr containing
nercdds
D - Higl-cxplosive maicrials
E - ryrotcchtrics/iUuminents/masleondcc :
F - Oxidizcrs (does mt iaclu& IiltDQ
G - Iaborelory unstca (must bo
3cpgetcd as dircctcd by GM-3.1)
H - A.F. neot 78 nixcr nnstqt
Sco Trblc tr for daails.
NOTE
All livc naqial slull bc grourddlrross-
bndd througlou tlu dbposal poccss.
Itilclc.BdopBrcak Rule - Atach (nalce)
a DGw ground cablo conncc-tion bcfore you
disconncct Orcsk) thc old grouad cable
corocctiotr. Ap,plics to groundiag aod
cross-bondiag.
VANNING
Atach o liyc ntotc?ialfilrit ad avayfum
Itvu noqiallast.
Itilrlcrial llcalth and Sofety Infotmation
fltlESI) - Thc MIISI are prcposGd by Wastc
Meoagcncot and Environneatal Scrviccs
and revicutrd by Iadusrid Hygicoc. Thc
MII$ docuncnt conteins chcmical
inforuetion fron veodor-srpplicd Matctial
Srfcty Dalr Shccts (MSDS), safcty hazads
d.oL eod hc.lth inf,otuation.
NOTE
MHSI's no bnco contalg, dirytosal
instrucrlorls. &ntet Waetc Manaearsa
ond Env*orutstul Srryices for insttttctiortsh asa nd avqd by rtis rrulnuol mI@
GM-3.1
Bsrte No. lil
21 Septernbcr 1992
otrt of-place Propcllatrt - Aay PEP trot itr
itc p,ropcrly assigncd location pcr plaoning.
Thir ipcludcs snall pioccs on thc floor, on
buc&efs, on cquipncat, on the outsidc of
sling lincrs, ouai& of Velostar beg(s), ia
pmpcllaot contaiacrs, etc.
ddzlr - Plopcltant oxidizers rcferrcd oi[ thb proccdurc arc those matctials ufiich
yicld oxygea !o support combustion (ia thc
propcltant fornulatioos).
Exanplcs are enmonium pcrchloratc,
potrssium perchlotatc, sodium Ditmtc, aod
potrsciuo oitntc.
PEP - Abbrcvistion for propollants,
cxplosivcs, and pyrotcchnics.
P;notechnic - Metsrial which produccs e
bright or colorcd light, evolvcs heat,
p,todttccs smokc, or givcs acoustical cffccts
utco iguitcd. Me&rial rcfcrrcd to h thig
pmceduro as p)tlptcchoic marcrids iaclu&
boma potassiun nitmlc, flares, magucsium
lnudcr, stroatium pcrchloratc, boron
ne$dg. aod gEs gcncrail.
$tng Bog - A conduetivc lincr for haodling
ftitrcs uscd to disposo of large quaatitics(t0 !o 3,0q) lb sizos) of wasrc propcllaot.
Todc Itfiilerid - Any subeancc having the
rbility !o causc damagc o living tissuc,
inpairmcnt of the ceotral Eewous systcE,
ssverr iltncss, or (in cxtremc cases) dcath
uficn iogcstod, inhalcd, or absoftcd
through the skia.
Werning - Dcsignatca activitics in whic.h
bodily injury E8y occur.
lf,rsac DlsDoeel Notica (Form TC tl24) -
A mticc u,tich prcvidca iafotuationo
building pcrroucl oa how to contct .
dircGecrcy so thst prchrp aod disposel of
6o itcm(s) pleccd on e Wrsto Meoegpocot
rod Eovimnmcntel Scrviccs-apprcvcd dock
E y b eccomplishcd il e tincty ErlrcE.
,[$2S 3
fhc $lrgto Dbpos.l Noticc wi[ bc left with
building pcrroancl or on the uastc disposel
dock on m itco(s) that caoaot bc pickcd up
by M-136 dispos.t crrun bccausc of a
proccdural dbsrcpercy.
3. REIIERENCTII
de of Fdlru,lRcgubtbtts,
'Traosporttionr'TiOc 49, perts l@
througb 199
D OT Tlans portoilm R c gttbtiotts
DOD @ntuors' S6a! Mauulfor
,bmnittun &, @bsiva, DOD 4145.2GM
Erybsiva S6ay Stanfurds,AFR 127-100
fuwal S$ay and Hcalrr, Montol, Ctaptcr
5, Color Coding, 'Wastc Matcriel
Coilrincrs'
ful Salal and Hcalrt Manal, Chaptcf
5, 'tlsing Wastc Conaiocrs in Ilazadous
Locrtions'
fuurul Sday ard Hcalt, Mouul, Ctaptcr
5, 'Collcctioa aod Dispossl of Erplosivcs,
Propcllaots, aod Ohcr Ilezirdous
I\,ldcri8b'
fuwal Way and Hcalrh Moiual, Ctatrcr
9, trodling and Traospottation'
fuaal Safay atd Halrt Maiual, Chapcrll, 'Uso of Firc Synbols'
Eardour W.stc hofilc Date Shca
(rrwDD)
I*PlaatHadlttrg Mat ual, 'Geoctal
fudling'
tloaiolHalrtt and Salay l$ontrltbn
(MEfl)
GM.3.I
Issue No. 12
2l Septanlir l99l
Naiond Fire hotection Association
(NFPA)
NFPA-7-19t3,'Rocommendod Pmtcction
on Stetic Eloaricity'
NFPA-7t-19t3,'Ughtning Pmtcction
Codc'
Rcsourcc Conscrrruion aod Rccovcry Act
ECRA), ss rmcndcd in Novcmbcr 1989
Tcchtricsl Disclosures (ID)
Toxis Substaoccs Contml Act GSCA)
Utrh Hezardous \[astc Maoagcment
Rcaulatioos
4. MAITRIAIS AI{D EOI,IPIVGNIT
Bunny's Minclc Fea or oquivalcnt
(Stock No. 5l-5870O4)
WrtcE
Minaal oil, No. l0 motor oil, or othcr
s.ftty appoved oils
Tri.caitr
$wfust or wipcs
F\tcl oil (No. I or 2 diescl fucl)
DOT l7E strd lTlI stccl and
polycthylcnc drums
Eolyahylcnc drum lincrs
Coaduaivc Velostat bag
Hrzadous lllastc hopcllaat kbel
GC U59)
Hrzsdous Westc Ilbd GC 718,
Scnp Ltucrid Tag (fC 0t7t or SP 0878)
Screp l$cl GC 10eD
SlinS bsg (conductivc)
Ilrodling firtrc foi 3ling bai
lGgrl Clrss l.l wrltc p,ropcllsil
coffiirctr
ZlFl Clsss 1.3 *asto propcllenr
cominGfs
Gruudiry stnpc
Supcr seck type disposrblc
ooilriocr!
gEa.
llubl S$ay Dara g,ca (MSD.S)
4
5.
5.1
SPECIAL SAI'TIY AND MALTII
NEOI'IREMENTS
PERSONAL TROIECITVE
EQT'IPD{U{T
NOtts
Plottning or MHSI slull dlctotc panorul
prura*c cqtipnatt rqubaruts.
5.1.1 FcrsoDtrcl hendling live natcdds nust wesr
flrnc rarrdrnt covaalls or snocks, safcty
shoor, glovcs, ard chcoicel-t1pc gogglcs or
sefay glrsscs with si& shields. All
clothing Du!,t bc closcd. Na$ral nrbbor or
NBR glovcs Eust bc worn. Coton glovcs
Ery b worn ovct nrbbcr glovcs ufren
crrnt ct with propcllant is possiblc.
5.t.2 FcrsooDcl uorting with staris scositivo
prcpelhot! or natcrids must waor non-
strtic producing ootton clo6ing, flamc
rtristeat coveralls, and adcquea cyc
ptotetion. Conduaivc shocs or lcgstats
nust bc wor[ as rcqrired in arcos with
condrctivc floors.
WANN/,i|,G
Uapatc gmuldiai or aoss-bondhgrust
bc ruintaindfor all livc nutqial
thmuflowrtc atirc wastc dispsal
Pnacess.
s.2 IIAZARD COMMT'MCATION
PROGRAI}I
Ooc of Thiokol's foremost obirtivcs is to
sco that tho setay md hcalth of cach
cmploye is considcrcd ia cverT job. All
cmployccs cra hclp achicvc this gpd by
boning 6orougtly fenilier with thoIlrzrd Connunicrrion Pr.ognm aod usiag
it u e guidc ia disposing of ell hezeidorus
nrrcrirlr.
5.2.1 Ney hire tniniog hrr ba cstrblbhcd ro
inforu cnployea of:
GM€.1
Issue No. Ul
2l Septonber 1992
l.Procodures cst blishd to cover dl
coployces who ney bc cxposcd to
tpzrr0ons Daleriab.
b. ncqufucmcnts of thc llazad
Connunication Staodad.
c.Opcretioos in which hazardous
nrncriets arc prcscat (gencral
ovcwicw).
d. I-ocetion aad evailability of thc writcn
hrad communication progf,eo
includiag tho hazadous marcriel list
Gil,II-) and natcrial safcty date shca
(MSDS), or matcrial hcslth aud safay
informatioa (MHS[).
e.ltc sigaificaocc to thc coploycc of
crch setion of infornuion in the
MSDS, how to r€ad it, aad what it
nclDs.
5.2.2 Pmccdutes for training cmployccs ia thoir
nort area inclu&:
t.Infotuation about physical aad hcalth
hrzsr& of chcmicals ia thc work arca.
b. Dctcctiag the prcseace of hazardous
Erlcdrk - monitoring procedurcs,
odors, visibility, ac.
c.kopcr scletion and usc of pcrsonel
protcctivo cquipmcnt (PPE).
d. Emcqgcncy proccdurcs in tho cvcnt of
accidcotrl cqrosurc to hazardons
Edcrials, including energercy phoae
mnbcrr and thc location of cyo
wrsh6 and sefay showers.
e.Itrow o dctcflniac hazsds by rccding e
lrbd.
t&2.t 5
Ttc loclion of thc MSDS/MESI aad
thc proccdure for rpviewing thcm
rod/or ohliniag e oopy.
S. Itrow o obtaia thc corrcct
MSDS/MII$ for thc hazardou
$bstrre uscd by thc cmployec, such
.. ulo of thc tm& oamc, spccifrcatioa
nunbcr, psrUstock numbcr, etc.
h. Iilow tho MSDS/MIISI is updatcd aod
tho ptoccdurc for obteining updatcd
oopicr fron thc chcmical
mraufrctlrr, inportcr, or distribuor.
frc ncasurc3 cmployccs cao takc to
prctcst thcmsclvcs from chcmical
cxposurcs including thc usc of eyc
wrshcs, facc shiclds, lGipiralots, etc.
j. Ttdning which is donc ptior to tho
headliag of hazadous chcmicels,
ircluding cmployccs who rey only
tcuporuily do rhis wort.
k. Updstcd tnining which is reqnired
rrytco tho coploycc hes traosfciled
jobc or @rEcots.
Updstcd tnining which is required
uficn c,heoges in chcmicals or
opqatiotrs havc occured.
5.2.3 Supervision will cstablish m Arra Specific
Iftzards Tnining hognn.
Supcrvision is responsiblc to: (l) crtetc eDd
nrimain e list of hszudou matcrials found
in thc work aree, @) cstrblish sod Erirtcir
e I?ACS rEquirEocot (or o6cr tnining),
(3) trin coployccs in rrce speific
hrzrrds, rd (4) psriodically audit coploye
conplirre dudng thc qmrt pcriod.
q[$16
GM-3.1
Is$rc No. 12
2l Sqtcmbc DqZ
6. MAIERIAL INSPECIION
I wAnNlNG
Wostc PEP rnotqbls prcpodfor dbposal
a M-136nast bc corutty prcpard o
ansrtrlc rtc s$ay of dtc Disposal Ara rr:avs
bt hc pithtp of, tosponfunto, atdufunig u M-136; and to awilt ntiilups
fuing bu-nhg opaatbrc.
NOTR
Allwastc PEP nutcrblsftottthc Tcst aad
Plot m vet rrutst bc uwryanidby a
signd U$orm Hutrfuus Elastc Manifat.
(scc Appctdbl). Matatub $A not bc
nansprtd on public higbwys wiless a
signdnw$fat is on rtc rrlastc bck$rt
the nwaiols at titu of pichtp.
6.1 ESITABII$I PROCEDT'RES
Dock coordinalots or othcr building
personocl prcpodDg unstc for disposal nust
ingtitutc m ap,propdatc merhod of matcrid
iupcction of rryasc PEP containers prior to
pleccmcm otr ao alrlnoved wastc dock o
cosurc corrcct unsa disposel stcps havc
bcco followcd (scc Appcndix t).
62 SEGREGAIE MAIERIAIS
Wesb PEP metcrials ars scgrcgatcd
according o Tablc tr aod placcd into
tEochB/pitt accordiog to Tablo ltr. Uscts
Enst scgpprc $lastc PEP natcdals using
thcsc tablcg so rhat rhc M-136 ctclrc Dry
seftly haodlc and placc the matcrials in
thoir propa location at M-136.
f.
l.
l.
7.
7.1
7.t.t
DISFOSAL PREPARATION
GDNENAL I}.ISIRUCTIONS
OhiD coatrircrr from thc dock stongc
rrce. sclca thoso contrircrs that conply
with tbo idcotificetioa nertings ncodcd for
tho operetioot !o bo pcrformod (sco TablcID. Comc EWD if ncw contrincs arp
Dcdcd.
6
7.t.2
7.r.3
Visnlly choc,k thc conraincrs o cosurc they
rrp slcra prior o filling. If not clcea, do
not uso tho oooincr. Rcfcr to Scction
7.l.kbclow.
Prce.ru thc oonteiocrs as follows:
a. Stastc nrtcriel eoilaircts must bcD.fid aod prrperca ia accordanoe
with Teblc IV.
NO|ts
Oty ycllat plartb 10 ard 2G gal
cofialnql prestcrnild:
1.1 or 1.3
EXP
TilAT
h td laar
0c b bc ttsd to pdagc snallq arrrrutrs
of ltw na*iol
NOTts
othcr a@wastc onminax (a. spct-
sacb, bora, e), do ttot na;asarrity
rqtbc statcillbtg. @ruaa frlDlor
statcillbtg rquitanants on rfr,ac itans.
NOTE
lhe usc ol a Scrap Tag (DC O87E or SP
N7E) dqdds on MRB rulcs,. Thc
soqping orgalzdbn trust raiat
oppltcdb ttwugarcnt pW atdlor
bttiJdbtg plambg o dacnnhc scmp rctg
rqubarcns. Arry qratbns slpuUbc&rasd to Wpqty ,mtugarun orqplb&b q,aliry orgar&:otiorr^
b. All idcotification latcring aod color
codcr nust seoci& thc netaiel typc
br u,tich tho contrincr ury bc usod.
g.Idcotificetion lcfrering nust bc d lcastI h. i! hdght ufrcocver possiblc.
d. IdcdrS Eus bc stcocilod twicc on
oppositc ridcc of tho conuim.
GM-3.1
Bsuc No. ljl
2l Septombcr 1991
7.r.4
c. Clcaa any rasablc ooatrincr if
coDt niutGd with propcllent or othcr
edcrhl.
Lirc dl 'tiyc" wstc matcrid containcc
with conduaivc black Vclostat lincr.
Conteiocn for 'livc' wastc3 whish contain
liqui& nust bc litrd with tulo coaductivc
lircn. Roll thc op of thc beg dowa a
niDiilrn of 6 in. ovcr thc oueidc of aoy
conrais uscd.
NOTE
BEFOREvnstc goa into hc contaho,
agocrt a Hagfuus Wastc hopcllottldcl
(rc U59), to tlv contahowith all of hc
ir{onatlonfitU h accpt corylabn of
tlu ryotitta, whichwdllbc addd oia thc
opaubn is complad.
7.1.5 Excrcisc carc to kccp thc conaiacrs from
booning cootaDilitcd by unstc mataids.
7.r.6 Ag it acc'umulatcs, put tbc 'tive' rvastc
nrtcrid in thc conaiacrs dcsigDatod for thc
rpplicablc t1ryo of natctial. frc coilsircs
mtst bc Sroundcd as thc matctid is
mmul*cd.
WANNINC
Livc nutqial wastc slull na contaia ary
forcisn nutqiob sdt as pop cats, cotdy
wrappas, disctdd tols, paint cans, ntgt,
bohs, *.
WANMNG
lf wastc PEP is contonbutd wirt pyridhc,
trritc tlv rrrd Wdtnc in ot last l-ittlaqt on a piac of yclbw tqc atd osoch
tlu tapc o rtc uppa oncrthird oltlv
Vclasta bag. Tapc nust bc pbdso & iscluly nrilc o M-136 p*tomel as thcy
qprorchthc vastc de*. EPAWastc dc
FNS ms bc on hc Hqobus Wastc
Prupcllaat Labelfor PEP Wastcs contoin'irzig
FyriaUa Wrltc 'FNS itt the ratw*s
brr;h
7,D&L1
7.t.7
7.r.t
WAN,{,NG
ry?idtne ts ttoltgartiD,lc wirt nilrugtycah,
raw urctd ptopcllant, ad ury sttunt
oxillhlrt sch as omoniunpadioratc
(AP). Do ro, prasant hquds to M-136
Dlsgrr,al Ocrw by pluitrg ittonpittc
nbwa lrnvastc contaircn.
Do oot nir propdlant/illuminaat tlpca. :
Bct conuim nust hsvc a lid wtilc imidc
r hilding. A lid is not reqdrod rfier thc
p,rotcctivo lig is closod aod thc coatrincr
h.r bcas rtoorrcd fron thc building. A
looco fiting covcr is rcquircd for illuniomt
wrrtql slorGd ouEido.
NO|ts
A contahabAbg PEPvustc natqiat
nalst al*urys bc cbsd &rhg stonagc.
accpt v*at it ts naasar-y to & wasta A
Vclutobag w/icrtlns bccn rwistd and
a.dd is orsibd cbsd. A slhg bag
lito it considcrd a cbsd contabav,hcn
,ltc dW draw $rfng it dtun cbsd.
ltc disposel mcthod, arca (cithcr burniag u
M-136 or bumiag/dctonatiag at M-225A)
rnd thc nacriel cless (l.l or 1.3) Eust bc
strlcd on thc Scrap Matcdal Tag for dlh[[ e.xplorives rnd crpcdmcnal
1nopclleoo fton tho Dcvclopmcot Ilb. All
pro,pcttmt contamiodcd natcriel must hevc
r I?-H or tlpc aunbcrffiitco oo thc Scrap
Trg. Ieboruory trrstc shdl bc
eocomil.icd for disposal in tho sanc
D.Dtrcr rs dcscribed in tho preccding
euryrapU.
WANilINGb NOTnn Class 1.1 wastc propdlottfr, Class 1.3 wa*c propclla*
NOIR
A ffi lb 6 il t Mbb conratad iadr onnba, ircMilg PEPa nwdnad
wge, fiul$ h btMd oa a Hogfutts
Walre Prqtunt LaM (rc Ell9)filld ou
ttsbq a &oury's Mlnrclc Pan o qdwlai&
GM.3.I
Is$e No. 12
2l Septembcr 1992
Tlu Hqofuus Wac Prcpcllant lfrcl ttust
bc rcM b drc Vclastat bag nco rtc
bp. Ilp Hoseus Wac hopcllant
Iabclb an &itilrulrcquirarcnt o ohqrqtbd ugs such as u IMO or Scrapl[oqbl Tag (lC 0E7E or 8P U7E). lhc
Hogfutts Wastc hopcllant Ldcl rrutst bc
usd on dtay containa of PEP rrrastc or
contoninotd v,aqrc.
7.t.9 Befop westc first gocs into the container,
ooach thc complaod Ilezrrdous lVestc
Pr,opdlsril hbd, twist tho top of tho drun
lincr closcd, aod tuck it ino the insi& of
thc contrincr. Irstalltbc lid oa thc
ootrteiDcr, ifrequired by shop travclcr
plaoning or Tablc tV. Transport tho westc
conteincs to thc applicablc uastc docUshcd
(sco Tablc I).
NOTE
Thc onuinq ca-rying rtc pocttt Scrap
MoaiolTag (TC OA78 or SP 087E) tttust
bc on tlp da* u hc sotu tinu asoontainllra o dnt mg wirt Scmp
Ifrcb (rc INI). M-li6 DLsposal cr:aw
will na pil* up rtc nutqbl if rtc ng and
tlu uconprying ldcb rcfaatcd o it arc
na ogaha on rtc wastc bh
7.1.10 All 'livo" wrstcs must bo collcctcd and
rpmovod from the opcrating areas aod
relocatcd to $lastc slomgc arcas 8t lcast
o[cc cvc(y wortiag shifi. Irboratorics
Ery b excmptod fp6 rhis requirencnt if
rnouots acctnulatcd.tr so small thu it is
nore practical to rctnove then oncc r d.y.
7.l.ll Pmperly void aoy Accctr Ta$ aod ensurc
thrt Ilezrrdous $lastc PlopclLot hbels, (if
.pplic.blo) Scap Tegt, .ad Scnp kbcb
erc propcrly fillod out ad.o.chcd to thc
ooaAincrr. Forurrd thc whita Scnp
Itfetcdd Tag (Appcodix D o tho ]vletcriel
Rsvicw Boed or Intcgrrtod logisics
Suppon (epecoOr I) for Spocc Opcotionr.
t,&1t
7.1.12 ExccasGd neterial Dust bc accompeoicd by
emmpfttc shop plaoning aod aa Exccss
Try (Form TC IYliJ) for compeny-owuod
nrcrisl or c DD 1149 for Goveramcnt-
oumcd propcrty.
NOTB
For daaild hsrzlrltions covthtg 'F.rccss
hopaty,' corsult Appadlr II.
7.l.ll For dispocel of wrsts melcriels not
speificelly covcrcd in this scction, oootect
EWD. Spccific iol&uctiou mugt bc
prcvidcd by thc dispoccr, on aa itcm by
it€m bssil, usiag shop travcler planniag or
cquivalcot, with siprnucs roqnired from
E,|VD, Safcty, aod rppropriatc
lvlanufacnring Enginsiag for my
matcdab not listcd i! this document.
GM-3.1
Bcuc No. Il
2l Septonbcr l99l
A propcdy fillod out Ilazadous Wastc
PropdLil lrbcl CIC tl59) must bc
rtrchd to thc Velostat bsg, itr additioo to
-y oiho required t"gr or l*.tr. Thc typo
of rmsto PEP, its wcight aod thc weight of
tho contaninalcd rrilBtc, if applicablc, Bust
bG wdtctr on thc labcl (soc Appeadix I,
Drye 121).
7.t.r6 It is stmngly rccomoeadcd that the otrl
wd$t of ooaaincr aod contcots, including
dcacmitizing netcrial, docs not excccd 50
lb. h Do ssscr, shdl thc conbincd $cight
of thc conAiocr aad contcnts cxcccd 75lb.ltis rulc applies to both Cless l.l tod 1.3
nnstc natcrids, aad rcflccts thc safay
oonocm for tho liftiag hazad prcscatcd by
rnouats cxcccding 75 lb i! rcight.
hopcllaot contamiutcd wastc shdl bc
rconulatcd to no EorE rt'an 3/4 of oal
oontrincr volunc.
NOTE
Bofi rtc vnigfu of ary wastc PEP atd
incMd con onirutdwastc natqials nust
bc wba scparatcty in rtc ryantity blarrb
d, ury rcqnrd urgs or ldcls. Linc 4 atd
5,lor a nplc, on rtc Hqordous Wastc
Propcllant L&cl (Appcndb I) lor I h of
PEP nutqiol atd 10 b of contonimtd
wastc tvoud rcd 'l lb PEP typc' on line 4
arrd '10 b conaminotdvtastc' on line 5.
7.1.17 Whm solvcnts eru pftxrcnt in thc PEP
wlstc, thc ap,prop,riatc EPA wastc
nunbcr(s) must be includcd in tho
ooEDcotr scction of the llazardous Wastc
Propcllcnt kbcl.
Selvcrt EPA Wastc No.
Dispossl srta crunr will oot pick up any
livc nrtcrial at approvcd unsc doclcs unlcss
thc mrtcrial matchcs thc IMO, Hazardous
Wasc Propcllsot Ilbcl, or Scrap Matcrisl
tr8!, 8od the contrincrs arc adcquatcly
3roundcd. Melcrial aot cotrectly idcadficd,
with inadcquetc docuncotstion, of a
suspicions niimc, or nalcrial not having a*ri$t listod on rcquircd errchd labcls or
oficnrisc covcrcd as daeiled in this
dosuncnt will not bc picked up by disposal
arte crsws. A Wastc Disposd Notice (IC
BlZ-), Ffuurc l, will bc afrachd ro rho
itco outliniag the stcpc to allow a timcly
rcmoval of tbo marcrial from thc dock.
Buitdiag location nust bc indicctcd ot all
Scrap Tegs and Ilezrrdous lYastc hopcllatil
kbek.
7.1.15 Stslc aod Fcdcal EgulrtioDs rcquirc th.t
clcenup $rrst! itcms such rs gloves, wips,
sp.orLl, crc., nuit bc contaoimtod wi6
PEP nelccirtr in ordcr to bc disposcd of by
opco buraing. Wlstc itcos not
ooffiEiDrtcd wie PEP nrtcridc caomt bo
dbeosd ofby opco burairy rod oust Dot
bc prckryed wi6 othct PEP $rrsto
ueridr.
7.1.t4
Aoaorc
Mcthyl Chloroform
P!/ridhc
Frun/fA
F008
F(m
Fms
HTN
9,D:L9
GM-3.1
Issue No. lll
2l.September 1991
7.2 CI,I\SS 13 ROPEIJITNTS AND
IITI'MINANTII
NOtts
Scc PoagmphT.l fw gencml dispsolprcpatbnircffirc.
WANN/,/^,G
@npnrite and lllanduw3 scrap slullbc
grottndd or aoss$otdd thmugbu rtc
pnmess. StanM susuh propcllottt b
,n$fiy
'i[s:LO 9a
7.2.1
7.2.2
7.2.3
7.2.4
sasitiv€ o clatustar;r. disclwgc baausc
of ls cuau oontart.
All conpoaitc sastc propcllmts Gxcept iocrt
propelhot (scc Puagraph 7.14) md sliag
bqr nrt hevo r nrfficicnt amount of dicsol
fitcl poued ovcr thc surfeso of cach
coatrincr !o thoroughly $,ct cvcry surfacc. .
Scc Tablo V for dcscositizing rcquircmcos.'
Curcd loef srnplcs nadc from Class 1.3
prcpcllaot do NOT r€quirc dcscnsitizing
wilh dicacl fuel becausc thc pmpcllmt is
totslly cocasod in s cardbood cafion.
NOB
Ratfualsfrwn dtssrrr;bn and t*hg of bg
surpla nust bc daatsithd..
It ig rtaommcodod that wrstc propcllant bc
acotnulercd in rnounts up to 50 lb to hclp
Eininize thc lifring hsard. Tho
Ec.suseDcot includcs the propellant buckct,
rnd my dcscnritiziag liquids. hopcllant-
oonteEinltcd $rsto shdl bc accumulatcd up
lo 314 of totd conteincr volume. The
lordcd coilrincr shdl not rcigh 6s1p rhen
75Ib. Thir linit does not amly to treosftr
hoppcrs, sinoc thcy will bc handlcd with a
foflifr (sco ln-Ptaot Haodliag Manual
Scction tr).
NOTB
@runnatfilld wirt onous grao thotr
75 b fill na bc pbW up by M-136
dbposal crvtvr,.
Wrctc costrincn for qrcd propclla* ssnps
.t thc csctinS ard cutbeck buildings Esy bc
plrcod in r oarl pcllaeincr (four
oo0im! pctprllaaincr). Ar eoacptrblc
dtcoetivo uc0od for disposal is thc uso of
sliry be$ rad heodling filfiurs, or bins.
GM8.I
Is$re No. lil
21 Septcmbc l99l
Fach picoc of crued propellaat shall bc
pleccd in e heodling fixturc or bin linod
with qconductive lincr. 1\ro shocts of
coaduaivc Velostat must bc uscd if thcre is
r possibility of propcllant lcaching thmryb
e ringlc lincr. Rcfcr o Pangraph 7,1, for
gcocml instnrctions aod grounding
requircmcots.
Scrap flrrc cgadlcs shdl bc placcd ia e
Vclostrt bag aod theo placcd ia e haodling
aod curing frxturc QIJ26S74) or'in r form
shipping conteiacr. Caodlcs shall bc
pmtetcd from narcr contrmination.
Csodlos nust bc placcd on aa approvcd
dock for pickup by M-136 disposal crart.
Illunioaat cutbock wastc, nagncsiun
powdcr, aod floor s*rccpings nust bc
collcctcd in g $astc contaiaor lincd with r
Velostsl bag and covcrpd with diescl fuel.
lVist thc bog closcd and place it on tho
dock. SGc Tablc V for descnsitizing
roquircmcots.
WANNING
Do NOT allal'tlhailnant ymstc or
tmgnaiumpdaro conv ittto contut
wlthtlrtlr. Do NOT sal any containlrs
loUing illantnalltt or nugncsitun nuqial
daigrutdfor disposal u M-136.
NOlts
IR Fbc lllannnnt Wastc natqials rrust bc
prckagd scpoatc$from othcr vvastc
naqials. Spebl handling procdura nust
bc lollM by M-136 pclrotutcl durbg
hraing aad pst-bmting opaubts.
Anachdldcls nust clarty statc IR Fbc
Illutnont and stor;k nwro,lr.s DLOL12
utdlo DIOLSS.
Uoooncolidaacd illuninsot, or illuninmt
c,hich hrs bGGo rcoovcd fron e trnping
firtrrc, nust bc collcctcd in s $astc
contrincr lind wi6 e doublc Vdostrt blg.
7.2.5
7.2.6
7.2.7
,ES2.lO lo
GM-3.1
Issue No. ljl
2l Septonbcr l99Z
73
I\rfut rod trc& thc beg closod rad placc on
thc sasto diryosel dock.
PREPARATION OF CI,ASSI 13 AIYD
CTJIS|S I.I PROPELIJINI IN SLING
BAGS
NOTE
Thlt prudwc oppli* a bort snall and
bge slbg bags,
WANN,,/i,G
fuaury mixa sudt as PK will rcqdrc rtc
usc of a doubh lha a pr*ot naqial
Iront larlttng through rtc sams of rtc slhg
bag.
NOTR
Scvqal 'ncw' daips of slbtg bags atd
sltng bag lutldlhtgfrfrrcs oc in usc on
plottt Thcy oc typicalty designdfor usc
ta spadbfui$tfa. W wii[ bc rcfatda hac by rteir rapantilc frcilitta nurbq.
INAI dbrutsfons sc inchtddhacfor
tlosc rotfortlb wirt spaifo bdldfng
opaubns.
Buidiag App,twinatc ID (ItWrD)
Dcoh frontoo
Buibhe of contaho
IM4, 12'or gratrIil-ilrg 3 lD'or grataM-tn |E'or $ara(Cla nlrrig stobn)M-n0 12'or gratt
Soappfrng stotbn)
M-1O4O-| )3 I t2' or grata
M-504O-3)3 I D' or grcarcr
Apprminatc
wcielt flbs.l
2VX)
&n
MN
3(m
MNilm
Spcilb wight (ad caprcity) lbns fornocrials h thesc contalrl,qt MUSTbc
follovrd to allovt s$c llrltlrdltng ad dLspsal
of tlu propclla* Illrs,c limits arc spaifid
as d@t of ptopcllant swfrcclrunilu ap
of rte corutho. ltbbtinrs of thac lintits
rrsalt tn lwdlhg ootnqr|s (a dmppitrg,
spilllag, ac.)
7.3.t Prior to assombly of ray cquipnent, chcck
nrting surface aad haodling fixircs for
poealam cootemimtion. Rcmove aay
cootemiDrtion using a mahyl chlomform
&npcncd cloth. Clcaa all muing surfaccs
on thc mix bowl bcfore lowering thc nix
bowl oato thc rotetor.
WANNING
Atry ouof-pluc propcllant spilb rrutst bc
cla nd up bdtatcty. Ow.ofglcc
propclbtt is ory spi[ ucuning outsidc rtc
slbg bag or rtc dbpod araa $ hc mixW tilt sutblr. fu is ataru$ inprtant
a, prclrvrrt ndryl cltotofwnfum dripptng
ialo thc slhg bag lbrq. Matryl chbroform
h tttc linc;r bag wil cusc rtc propclbru to
lreh tlwugh rtc Eno *{tidt, h turz,
cotltas pnopellott conwnbudon in rtcWlbtgfi;;; c.
Do NOT disposc of mcthyl chlorcforn
coataninalcd rags, glovcs, or aoy othcr
forcig,n natcrisl ino sling bin linc bagst
@*ryeoedt*'
xm
M63
M-3@
M-n0
M-'U
i7'x 37'x 4i'i7'r 25'x lE'6{'x *1'x 26'i5'x 35'x 18'
,D2.u u
GM-3.1
Issue No. lil
2l Septcmbcr Dql
7.3.t Dudtrg all propcllaot dunpiag opcrations,
thcdingbeswill bc groundcd!o tho
building connoa grouod 3ystcn. During
tnnrportrtion of thc ptogcttaat in thc
hrodling firturc/sling beg, tho sling bsg
nut bc gpuodod or crocs-bondcd to thc
foflifi/tmryonvchiclc.
7.1.4 Follow slirg bsg iorpocdo! instructiong
fouod in Shop Planning.
NOlts
Slirig fugs trrlrst bc stod in their origirul
dnpphg oonbilalrs to prcvant bogslront
b@lang futugd ard o kcq thanlrcc
frwr. dirt or grit Usc corduaivc sling bags
vttrrlt dispasbg of ptopclla*
?'3'5 r1*\Cl:-g M 53r uc e orcP 'oCCcc € ft
hdda'
f,ilJulfirle
W
llffi
*a*a*l*Cftntur
7.3.6 Pls thc sliat hg ino thc handling firtue
and sccure in plecc by hooking thc lifiing
poim of thc sliry bag ovcr thc cotlcrs of
gf,s hmrlling 6rtrc. llc sling beg wil bc
pbcd inri& thc heodliry frrtrc eficr tho
hrodirg firule hrr bGGo poaitioacd iuido
6c building. Sprcad lho bcg out cvcoly in
1f,s hmdling firnup aod snooth out dl
tut&.
r$all Ita
7.3.7 Usc e rnall aylon ropc or topc to sccurc thc
sling bry tanOtcs (hfring poire) outsi& thc
ootriDcr.
+oeifiol+fptulA
7.1.9
t {rtr3firfo et ePte-tr hr.
bceac'ftlh
Ihnpiag opaations Eust oeasc bcfurc tho
slirg beg levcl is chekcd. Try o spli! thc
helc of thc throo topoff bowls into tnlo or
more sling bags whco sffapping top-off
nircs. Do not overfill sling bsSs.
t{B
p{cptta*
NM
tmr*@
7'3'll WLm chug--t frrr em's "!t! ftur
GM-3.1
Is$rG No. 12
21 Sqtcmbcr DqZ
'
il
A[.ch thc Scrap Matcriel Tag aod
Ilazardous Wastc Pr,opcllmt kbcl o thc
top portion of the sling bag conaiaing thc
scrry pmpcllsot. S€{rE thc lop of thc
sliry bg with tho duffcl tics.
7.t.t3 Vaify rhat the fo*lift chs,acls sse ftic
from propcllent costeniDstion. Clcaa with
e ncthyl chloroforn &npcaed
Rlmplcclot, if ncccssaty. Peeitiea*fo.eir
*ngryhF3.'+ Do not lemoye thc grouad
stnp ftom barrccn thc sliag bag aod thc
building sonmon grouad systcn until e
grouad silrrp os closs-boDding is ettach€d
fron thc sling bog !o thc fortlift (ratcd ES,
EE, or EXQ. Ptace on ao aplxovod wastc
dock aad oontsct E"IVD thc-forcleeor
hrdtroa-of;M-13,6 !o traosport thc
propcllmt in thc haadling fixturc(s) to thc
buniag grounds.
NOTE
h coA i,atlra (r.rrdct 32' F), qditc thc
runsport of wastc propclbat o thc bunbry
gmudso pr*ant sling bag ljaanfrottt
sffing o rtc stb olrte futdlingf&ra
,&iLv,t2
nS
ler-*c*1nU*'
ilB
i,tt
fr;qn<*e*
7.t.rs Thc heodling fixtrs(s) wi[ bc tmsportcd
to 6c M-l36Buaing Grcuds for disposel
of rliry b.g!. L.d tho handliag fixture(s)
aod sccurp thcm on r trarport vchiclc.
Trenspoft o an apmvcd wasa p,ropcllrot
stotego dodc so thc hrodling frxture(s) caa
bc tnoryortod to tho burdng grounds for
dispcsl. Do not cxcccd thc storaga dock
r*rstc propcllaot linit. AtBh ground
strry !o dl eling begs storcd at thc stonge
dock.
7.1.16 Vcri& clcaolincss of each haodling frrturc
8frGE it ir rctrocd fron thc buming'
grcunds. Usc g clcar rag lightly dampcacd
with mahyl chloroformo clcao aoy
coffimioelcd hmdting fixilrca.
7.4 IIIGH.ENERGY WASTE MAI"RIAIS
NOTE
9cc Paagrufit 7.1 for gawal disposal
Prcgfiorbn /{[st?[rtbrlJ,.
7.4.1 H[b cocqy nrtcdels irctudc XLDB
propclhu, IMEIN rrncrrcd pmpdlaot,
biDdcr prroix, Crg\{-3, HDD(, IIARM
Wrstc.d m8!o, Tonrhsurk Wertced qnsto,
cobcdncot pordcr, or $lrsto cont Einetcd
with ray of thcsc natcdals.
7.4.2 Hf[acqy prceafu $asto Eusa bc
Stoudd thrcqtout thc disposal pmc€8.
GM-3.1
Issuc No. 12
2l Sepianbcr l99l
It ig rccommcdod that high-cncrgy
mrtcridc eod dcscnsitizcrs will bc
eccumplrtcd up to 50 lb maxiuum wcight
pcr coiaincr (*Eight includcs colaincr).
thc nsimum u,eight shdl not not cxcccd
75lb to bclp minimi'e thc lifring hazad.
NOTE
fonu opafurc wtll prducc wastc
prupdlant pba thot oc haviq rhon 75
b (a9., bgc tttotor castittg ornces,
slags). A ontaincr nust rtcn bc providd
t ro will bA hc pmpcllant pi*c. Thc
conmba slullbc lhd wirt cotducttvc
plasfu adbc popaly sa urd to a palla
as diratdby Scctbn lI of tlu In-Plott
Hadltttg Monual Thc veight of rtc
aonmina tutrrt not acd 5@ lb.
NO7ts
@a&vn nay bc dastrsyd dwing
dlspasol pur'as.
Hth-cncrgy propcllaots (scnp mixcs) must
bG dcscositizd wheacver possiblc by addiag
tri.cctir. Conponcos of higb-energy
p,ropcllar nixcs nust bc dcscnsitizcd with
Hecain es dirwtcd by Tablc V.
NOT'E
High cnag XLDB propcllant disposd of
bt slbtg bags ba na rcquirc daasithing
wtttttriacaiu Tllc slbg bags slouAbc
btblclindwirt vcbstat
NOTR
No dcscnsithing agcnt is rcqubdfor wastc
aoilolncns of straight+ttd XLDB
ptopcllott AU ortcr pr*aufors usdfor
Wlhg high-cnog ptopclbnt slouA bctfut Daansi{ac wastc conpnans ofucrd high-awg propctlott os diratd
by TobrcV.
WANNING
Dlsposol of XLDB Bttda hailx or Bhdq
Srrap MbB rquira fia all hosds nust
bc &rasdby tltc soqping orptiafun
so fu @fia Wlhtg procdura caa bc
d.dopd.
7.4.'
7.4.4
,ns2.rt l3
GM-3.1
Issuc No. 12
2l Sepacmber Dql
T|dr will cnsllr:c tlu sdc Wling of
no*tal &ring tlp cntbc dbposal pocas.
Spafic bfontAnon ae&, contatt and
qnlrlttity of h$diqw nust bc provittdQ
tlu saapping oguttzu'on
Dbpasal nust bc sdtduld in dvotrc wih
Scianr;c ik Fnohcqine.AMu@
Dbpasal nuy bc dalsyd scvaal days
baarcc lt nast bc cudhntdwihtach
owibility, bwnhg sdtdulas at M-136 or
Plant III, ac. Tatgaanrc of rtc nwqial
nast bc kq dovcficahg &ring coW
w@hq utflc waitlnglor dispsal
Dbparaltnllbc ot ttp Plat III Bming
fuurrds iltlu nwaial wdll daonotc, ot ttt
hc M-136Bmnng tuunds (f the naaiol
caabe s$c$ bwadwttlotu daonotbnwrrins. 7}zlasportation ad disposal
natst t&e pbc &lring doyfigfu llrto x.
Slop plotnlrllg ntnst bc wih rtc notqial a
,t c tit u olpidup at rtc builtlbtg,
Itcms cootrminstcd with Class l.l
propclleat must bo loosely placed in c westc
contrincr cod must mt cxtctrd abovc thc
cdgc. No elcmpt wil bc madc to conpact
tho contaninetcd wgtc.
mg[-cDc8gy *nstc propcllaot conaincr:
Eulrt bc lind with a coaduc-tivc plastic beg
aod hevo 2 fo t in. of sandust in thc botom
(en cquinlcot enount of wipes nay bc uscd
in plecc of tho seudust).
NOTR
Hlgh awg XLDB ptopdlatt dfspasd of in
sltng bags fu not rcq&c satdlust ia rtcMott
If ray ligi& (rncluding dcccositizing
$otr) rr! I,!Etcd, doublo Vclost t bsg!
Eun bc urcd. If tc rcnp nrtcrid i! dry
rod no Oc*aOdtng li$dd is prtscd, thoaofriu Dry b lind with oac Vclost t
7.4.t Sctsp.In0(, RDX, CXM-3, HARM
Wsrtacd, or Tomahau& \lraftcgd wasto
mut bc placod in a nnstc conainer lincd
wilh tlro oonductivcplrstic begs bcceuso of
tho prcscooc of dcscnsitizing liquids. Scc
Tablo V for dcscositizing requircmcnts.
Totrl HID(, RDX, C)Od-3, aod triacaia
Gf uscd) conbiocd shdl aot cxcccd 50 lb.
WARNING
E*surc tlrd bulk ryantitia of HW arc
cotnplac$ smatdwirtdiacl, bw do rot
stfr or agituc thctucUr+ustc mifiurc.
NOTE
Opooon of HMX grtudlrl,g and drying
buiHings *lo disposc of Dollingofibcn
mst clco$ nar* on rtc Hazarfuus Wastc
Propcllant L&cl tlpt hc fiItcz t arc
i,tclr.dd in tlu Ycbsta bag. Thts v,ill
lacllitatc spaial dbpsal lundling. Filtcn
nutt bc prclcagd and disposd of
scpatdy fron orto natqials.
WANNING
AA HMX<ontonhotd wol;tc containing
HIfiX ntnst bc ldcld os contahkg HMX
onhc Scrap MataiolTag andHqarfuus
Wastc hopclbnt L&cl; lor aamph,
StanM BastlHMX+ontotnirutd filastc.
7.4.9 All filtas contaminatcd with HI\D(, RDX,
or CXM-3 Eust bc dcscasitizcd aad pleccd
in scperatc doublc.lincd Vclostat bags. Thc
Ilezardous Westc Pr,opellaot Iabcl must
clcarly strto thc prcscocc of HI\.D(-, RDX-,
or CXLI-3-contaninatcd filtcrs, to cosurc
plrccmcnt in thc corrcct tcoch.
NOIR
Iogcfiltqs mtst bc pbd in double-lhd
Vclostar bags ottd sanad o plla.
7.4.10 All wesrc E tcrid oontririDg nitoglyccdn
(oxccpt biDdcr prcmir| Eult bc collcctod
rod rrmovcd fron the opcrating eter wls6
shGd withia t ht eftcr plmcot in thc
shd. SEdl rnourr of bindcr Fcmin
b.g.
7.4.5
7.4.6
7.4.1
9:reaL l4
$,rstc (IlGsbey linir) Eey b kcpt in thc
opcrating boy. Thc prcnix ol,GralorB nust
coileclthc E[tD Buraing Area Crs$, to
pic& up thc premix ftom their building.
7.4.11 Irrgp $r.otitic3 of Cl0ul-3, still in is
origiDd coddm, will bc disposcd of per
rppliceblc phrning documcat approvcd by.
Environncol lYestc Disposel.
7.5 SI,BMD(ES At{D PREMIXDS (OTIIER
TIIAT{ BIIITDER, PREMIX)
Corcct dispos.l procednrcs for prcmixcs,
submixcs aod contanirarcd $rastas rcquirc
ao uodcrsauling of ccruia ground rulcs.
t.Only eluninum poudcr contauimrcd
with PEP E tssids may bc opcn
burnd 8t M-136. Any unstc
contdrcrr rcquirc e llazardous Wsstc
Pmpdlant hbd GC 8159).
b. Alumiaun poudcr that has not bcotr
thororyhly mixcd or combincd with
polynctc, ac., will still rcact with
rrrtcr. Thir is e hazardous wastc
ch.r.ctcristic. Disposal instmctions
rrc fouod in Scction tr, Paragrryh
10.10. A llazardous Wastc I$d CfC
7185) is raquircd otr aay wastc
ooatriEr!.
c.Aluniaun poudcrthat has beo
thorougtly Eircd aad combincd with
ottcr melcrials, such that it will aotret with rn[G(, docs not exhibit
hazrrdour wrstc chsras'tcristics.
CoDEEWD fordisposal
inrtructiooc. Any wrstc contrincm
rcqftd oood a W.stc I$d CfC
8125).
d. Any prcoix or p,rcoir-conuninafcd
tflr.tc3 xfiicfi rrc ooDtsEinalcd with
Dctyl chbroforu or o6cr rcgrdatcd
GM-3.1
Issue No. ljl
2l Septclnbcr f9ql
solvcats 8rp to bo trEaled as hazardous
tastcs aad disposcd of pcr iostnrAions
fouad io Scctioa tr, Paragraph 10.9.3
G.ldrrcdds rcfarcd to in this scctioa as
'livc' natcrials have pmpcllaot
oxidizcts such as HIUX aod/or
rmmoniu6 perchloratc (AP) addcd to
thcm.
f. Inert mixcs are thosc mixcs ufiich do
. Dot hrvc caough AP rddcd to then to
sugrort combustion. Incrt mixcs arr
diryoscd of in thc followiag *eys:
If the iocrt nix exhibits ao
hazsdous characicristics, thc
meEdal Eust bc dnrmmcd rad
disposcd of pcr instnrctions
fuund in Soction Itr, Pangraph
8.4
2. If thc incc Eir cxhibits
hezardous nastc charactcristics,
it must bc dnmmcd aod
disposcd of per instructions
found ia Scction tr, Patagraph
10.9.
NOTE
To cnsurc corract disposal pwdura arc
fobdby frD ll@ &avs,
tlufoVowbtg itfonrutbn nust bc clearty
nad on ary uuhd, rcquird l6cls:
&Whalw thc natqial is littud or soW,
b. If ai $itlizing agcn , sttch as AP or
sodlwtniiatc, has bccn &d in as@iar qruttty to st ppfi
orttbttstbn, o nake it a livc natqiol
c. Propcllottt TP-H or rypc nubo,
d Tlu Dlscrqoacy Rcpon (DR) Nonbcr
or rasoafor dispasol,
lf rte ,niailrc conuits nutqial wir/z
hqafuus wantc clwvlcraistlrr,.
I
a
gr*al:,r5
7.5.r Prenix-contrnioatcd n astc, conuiniag
dumioun pourdcr or mothcr udal powdcr
(not oxidia), htr no solvcot contaninetcd
netcridr, must bc prqorcd according o
iortnraiooc 6uod in Sostion tr, Paragraph
10.9. Thc nuial Eust bc ecconpenicd
with e popcrly prcpcrcd Ilezerdous Wastc
I$cl eod my othcr roquircd ta$ or label+
Coaais Ertthg, prcpcratiotr, aod labd
iogtuctions rrc fouod in Tablc IV.
7.5,2 If $rr$c oelcrid contrins solvent-
contrmiutcd wrgte nrtcdab, it shsll bc
dlspocGd of pcr proocdutcs fouod in Scc-tioa
tr, hngraph 10.9.3. lvlatccial nust bc
accompeoicd with an atbchcd Ilazadous
Wasto l$cl (IC 71tS).
WANN/,i|,G
Abnnon pe ond solvcns, stlah as
ndryl @onr, arc hongabla Do
nd mir afudnon po*darcontanbad
pmre tzgs wil1n solvant<onmmbutd rags,
wlpcs, Npn, a. Dbpa* of cdr
sqoaoJy.
NOTR
Anous ol fufiruan pado bgcr than a
fcw potttds mst bc kcp scparatctrom
tustc (witr, tugs,Inpcr, ae) and
rcycld e@rding o irctrwions fourd tn
Sabn I, PoagraphT.IZ2.
7.5.3 lto rnslc nlcdal will bc disposcd of pcr
procodnrcs found in Setion ltr, Prragraph
t.4.1 if it contrins m hrzardous wasto
conctiirm lod do6 oot havo cnough
oridizcr to sufoil comhrstion on iB owu.
A W.sc Irbd CIC tlZf) mut bc.sachcd
b tho nerhl.
7.5.4 WLco lis lp pursd in thc Premix
hildiryr' 6G F rtpd polyncn ad EcA
liquidr uttl bc dflEDGd in app,rovcd DOT
l7E o,pco,O,p &tnr lrbclcd rccordiag O
Ttblo IV, rod plecod or.n 8[rlnDved nrstc
doct forDi*Ep by hezrdous ursstc pichtp
[e-mail]*
GM-3.1
Issue No. Ul
21 Septcnrber 1992
7.6
7.6.t
FTROIECUNIC MATERIAIS
ryrcEchnic Erlcri8ls (othcr then
illuninm0 must bo lsbclcd usiag a
Erzadous Wastc hopcllaot I$d CfC
tl59), aod aoy othcc applicablc labels or
trgp !o iodicatc typc of natcrid. Conaiacr
mrrting, p,fcperatioa, 8!d labcl instnrstions
ltu fouod in Tablc IV. Conaa ElilD for
disp$sl inst$stioos.
7.6.2 Wrsto pylotcchnic metcrid Dust b covcrcd
with m approvcd dcscositizing egert bcforc
placcocnt on thc wsto dock. Sec Tablc V
for dcscositizing rcquiremcns.
WANNING
Spalific disposal pbrnhg rrust bc writcn
for propcllott-tacld tgnitrr.t and for
Flrtalalrnic or ordnatne rypc ignitcn.
7.6.3 Pfotcchdc maccrid scnp Eust bc
grouodcd throughout thc wastc disposd
Ptooc38.
7.7 L/TBONATORY SAIVTPLE HARDWARE
7.7.r Hscc sll adhcsion cups, platcs, etc., itr
Velosat-lincd propcllaot containcrs. Theso
Vdostat-lincd cootaincrs Eust prcvcot aoy
maal-o-maal contsst bctrpccn thc samplcs.
7.7.2 PacL tho contsoisatcd hardwero as follows
aod placo on aa E\VDappmvcd dock for
prc&np by Disposal Arpa creun.
a.Linc a compositc propcllant wastc
gpnteincr wfuh nro conductivc bogs.
b. Individually wrap each picce of
hrrdrarc with a raiculrr wipc or othcr
srftty-approvcd wrappcr.
Pls tho wnppd samplcs in thc
contrincr.
,rcL$l6
g.
7.9 DISSECTXD CASE PROPEIJJ\NT
d. \fc. Se.h thc wnppcd sanplcc with
dic.cl fucl.
c.Irbctr thc containcrs with a Scrap
lfrtcrirl Tag and Ilazardous Wastc
nopclfu lrbcl stating thc ptopcllant
t!"c! aod cstinalod gmtity (sco
lppcoOix D.
f. Nols on Ilrzardoru Wasc hopctLat
Irbd if rcslainod hrfilwrru is !o bc
rctmod to tho origineting sourcc.
LOADED !HN. CP CASES Ar{D
FOT'ITD CEARGESI
WANNING
Clmtb Pon (CP) catat rrulrit luvc a
hollow corc and laltst bc opcn on BOIH
atds o bc sant a M-136fo dispsal lf
cote is soW odlorbt t cnds oc NOI
opaL oonunt I-10 pcrsomdfor dfspsal
ttlJa-zrr,lforra,.
Ple lordd s-il. CP cEql or pouod
chrSc! in e conpermooncd nrcodco
comiDGE dcaigDd for thcso coscs. Rsfcr to
Scctioa D( of thc ltr-Ptsot tlmdting ltsnusl
for spccific h.ndling insnustions. Sirylc 5-
h. CP or pound ch.rgcs must bc shippcd to
thc appropriatc buaing grounds in a
Vclostal-li[cd nnstc p,ropellant s6nteincr
oDlo u,hich a llezardou $rastc kopellantI$cl aod othcr applicablc labcls hrvc bcon
.n chd.
If tlcrc rru roy Ercstions as to whic,h
diryos.l proccdurc !o follow, cort ct E1lrD.
Dilroctcd €ro setiou wi[ bc hrDdld rod
truryoftodpc tho applic$lc phoniog
doconcot rpprorrcd by Eavironncotrl
Wlsic Disposd.
GM-3.1
Iseuc No. ljl
2l SAtGmbGr fgql
7.IO GAS GENERAIYT
, NOB
icc Pbagraph 7.1lor gcnaal disposal
pr4oation twrrrctfuns.
WANNING
@s gawant v,astc rrulrt bc bt ut Aaqfid
ud scgrcgatd 0a on ilu vnstc dock
7.10.1 All gnr geocrlrt nasto barchcg shall bc
scsappd rs follows:
s. Waste containcrs 8rp to bc labcled:
GAS GENERANT
b. Wasc berchcs aod coataminatcd wrstc
.rt !o bc scot to thc M-225 gas
Scocrant buming pit aftcr coordinrtion
with Plaot III supcwisioa.
c.(hr gcocraat sunp wlstclt srl to bc
scol !o tho nastcwatcr treatncnt plaat
.t M-359.
7,10.2 Rcfcr o Tablc IV for containcr nulciags
rad prcpenrion.
7.II TROPEIIAI{T.CONTAI}IINAIEI)
SOLVENTS
ltis pmceduc outlincs instnrctions for
dispossl of solvcots coataminarcd $rith smell
.Eouots of PEP westas urhich havo ben
prcfiItcred using aa in-linc filtcr or o6cr
Ecsr3 iltcgrll to the process. Buildings
nltst coDt ct EHW to dcterminc if
prcfiltcriag mcthod mcas regularory
rcqulrcmcots.
NO|ts
SoAs willbc tcod the sorc as othcr
solld PEP v,astafor dtspasal pwVosa.
WANNING
Ptopcllanta ntallnnatdsolveng nay bc
cottsolibd onty f rtc rnnul conglbility
7.t
t[$r.r,r7
of ptopcllott typa andlor sohtants h rtc
,ntfioc tas bcu daatfud.
WANNING
XIDB- or Nfuntoninad soh,ans will bc
dtsgoa,d of by 'opan burztlrllg.' fuc ttntst
bc taka a minhtzc rtc anount of solvcnt
ganaud.
NOTR
9cc Poagqh7.l ond T&lc lVfor gcnaal
dfspsal prryrfun irrsrrcilrrlr,.
7.ll.l All solvent uscd iD thc cleeaiag of
p,mpcllmt coatroinrtcd tooling (ci6cr ia
buildinp using bubblcrs such as M-16, M-tl,M-ffi, or in casting facilitics aod
propclleot tinnins opctarions rh{ usc
solvcat !o clcaa thdr tooling) must bc
colletcd h DOT l7E,55-gal drums.
7.11.2 All bttildinp prcducing prcpclleil-
.ooatrEiDdcd solvcat arp o consoli&tc into
DOT l7E &uDs (scc Ffure 2).
7.11.3 Obtrin tho propcr dnm spccificd for
dirpo.l of tho nnstc nslcrid (sco Tablc
rD.
7.11.4 Visnlly chcck thc coatrincrs to cosure thcy
erp clcen rod undenagcd. Poly md stccl
&uru nust hrvc e D0l-agp,roved stilnp oD
ttc si& or booon. Se Figurc 3 for dnrm
inrpc.tion instuctiou.
NO|ts
hspat ofl, { nacssor-!, rqbc gasb o
a|gtoc a tiglt, tonl,g*I{,,g sal
GM.3.1
Issue No. tl
21 Septcmbc Dql
NOTB
Ifrorooria naro filta PEP<omoninad
sobanp. So/ids willbc tr@drte sorc os
otha loM PEP ttrastafor dispasal
pto'7oscs. (Scc Poagruflt 7. 1.17 fwlddhg guitlaljaa). @ntut illDfor
spa,ffic bbdfns bsrraibrc for furarutte
solvcnt conta nbutd PEP wasta.
7.ll:.6 Cooplao a Ilazardous \ltastc kbd GC7ftll) s,i6 dl aplicrblc iafrrmuion.
To oonplac lebcl, rtftr to Ap,peadix I.
A0rch lebcl !o rhc upper onc-third of tho
&un (scc Fieiurc 2).
7.11.7 Contrminalcd wastc oil scat !o EIMt/E'llrD
for off-plaot shipncat (propcllaat or
oxidizcr oontamisstcd only) must bo put ia
scalablc containcrs rh{ srt competiblc with
thc comcnts. BuildingF producing
prcpellant+ontsoi!8rcd nastc oil nust
consolidatc thc wastcs ioto DOT l7E
dilns.
7.11.8 Conaincr on thc westc dock will
bo dacrninod by typc of propcllaot
coabincd in thc solvcnt. Thc dnrns are to
bc groundcd ar all times utile on the westc
dock.
7.11,9 Contact EIIW for disposal of quantitics
S1tatcr or snallor th"" 55-gal &rms.
7.t2 PROPELIdI\N CONTAI}IINAIED
ALT'MINI'M FOWDER
Aluninum poudcr wiU bo disposcd of ia
orc of four *rys: (l) rcorrncd !o vcndor in
origirl shippiog coatdncr, (2) rccyclcd if
uoatruinercd with fotligin objccts, (3)
shippGd ofr-pleat ufico ooaoninatcd with
rohtcotr or foreign objccts or if solidificd,
or (4) bonod d M-136 if contrminrrcd
with propcllrn, AP, or HIIO( (uixcr $nsto
ooly).
7.1r.5 @solvcolssnntdodwithin thc lrboratory cra bc
flmrrmhlc Q.o., tolucnc, cthyl rcctdc)
rod/or nonfrnorblc (i.c., nc&yl
6lorobm). Tto coltcott nust bo
rordod on e lict with thc rDouDE
coroliddod rod typcs of prqelleotr in thccooiu. Ttir list Dtrst bc nrbnitcd wirh
ttc coois ufrco shi@. Tto oootcor
x,itl bc idcatifcd g flroneblo mrlcriel.
realt l8
NOIts
Wasu alumirunpodq@natlncrs nust bc
grottrdd dttouglou thc at*c dirposal
prlalccss. Nottcotdiuctivc containas nast bc
double4ind wirt Vcbstot bags.
WANNING
Do rot allottolunnonpovnqto corc in
con et wirt uraq or soltcttg arccp, asdirdd by q@ pbtudng fuururts.
Usc notspcldng tools wtm llrllrdling
ahontwt ptdo.
7.12.1 Aluninum powdct in its origioel shipping
comiDcr E y bc ship,pdboch to tho
vcodor uodcr mogt cireumstaoccs.
Rctunr of 6is Drnuc Ettst bc ecconpenicd
by e Discrcpcocy Rcport @R) or Exccss
Pr0p6ty Dcleration md coordinarcd
througL tho buycr of the metcrial in cirhcr
Stsocgic Opaationr, Spaco Opaations, et
I*rf#rctierlDivieier'
7.12.2 Aluniaun poudcr thu is not contaninrtcd
witt forcign objocts Dtrst bG collcctcd in
cominprs suitrblc for shipncot to aa
approvcd rcracliry orguizttion.
Umnuminarcd duninum poudcr wiU bo
nnncd to Sbrcs for excessing thmugh
Prcpaty Uaoagcmcot.
NOTR
@c nutst bc aqeisd a awid
con ornirntint afuUon pMo so rte
narr,as cut bc ra1rcld, sincc rtis b tlp
nost cast$atlvc fiuhd of dispasaL
NOTE
All anminat of tttlrrltttortttod abfuunpoda r*ad to $torcs for raylbtg
ntrrrr havc alll-6 nryto,rrx babdd on a@lts, arrd all AeqtTags witld-
7.12.1 Wctcd-duninun pourdcr ftou Econ4Bin
oi rts ogid aoilrig welhouf will bosnulacd in gnuadcd, doublo.Vcloctrt-
GM-3.1' Issuc No. ljl
2l Septeubc 1992
lincd contri&rs and pleccd in Vclosan-lincd
wrslc oomircts (prcftrably 55-gst DOT
poly {nlnr).
WANNING
Wu.sddwtp6 atdwaste fron clryogbrB must rurc bc pbd in drzrone wirtwd dtttninon po$o beausc of thc
porrsolinry of a rwion bawcan rtc t+atq
b rtc wipcs arrd rtc wad ahunnum
pofrq,
Complac a Ilrzrrdous Wrsto I$d GC7l&t) with dl applicablc infornation (sco
.lppcoaix D.
ltc eluminun powdcr.coatrninlcd nnsto
mst bc tightly pe*d in thc &uns. Whco
thc dntm is full, repleco thc lid and phcc it
on m appmvcd qrestc dock for tnosfcr to
tto M-lt6 storagc arca.
7.12.4 hoccdures for disposrl prcpanrions for
eluninum powdcr contaminarcd with
prcmix Ertcrials such as polyncrs, ECA,
I.ER, cts., etrd hrzsdons matcrids such as
solvcots arp found in Scction tr, hragraph
10.9. Qnotitics of aluminun powdcr
covercd by this procedure normdly will ao3
cxcocd a fcn, pounds.
7.12.5 Wastc aluminun powdcr tbu is
aonnrminrtcd with PEP matcrids, AP,
rod/or HIrrfX fron thc mixcr buildiogs will
bc dfuposcd of by opeo buraing at thc M-
136 Buraiag Grcunds. Follow gcacml
dirposal-prcporation instructioos fouDd itr
nngapU 7,1. Plrr*_ thc nnsc coatrincr
on ra rppnovod wasc dock for pickup by
6c ET,D l*.l36DicFrC Crsw.
NOIR
Fo onditbns brwlviag dispal of
furttwn pfia na dlscttssd abvv ror
in SadonII, ontu Ellllfor irctzlrrinns.
qlrD2.r9 l9
1.IJ PROPEIJJINT OXIDIZERSI
Oddizcr dispolil instsuctiotrs ia thit scction
rpply !o rnnonftrn pcrchloratc (AP).
Costrct EWD aod/or Sostion tr, Prngraph
10.12 for 'othcr oxidizcrs' suc,h as sodium
aitnla, potassium aitr:atc, ammonium
nopcltaat oxidizcrs, such as rrnrnoniun
pcrchlorrlo (AP), will bo disposod of ia orc
of four *rp: (l) reoncd to vendor in
origin l shiping containcr uficn
rppropsi.lo, (2) sold ir largp quaatitics, by
ooffiirct, furrccycling, if Cless 1.3, ground
or uaground, aod uocontqminatcd with
fonigl oblns, (3) sold ia sorll quantitics,
by contract, if pnro aod uacontaminatcd
with forcign objets, or (4) burncd at M-
136, if coatlninstcd, in snall quaatitios or
controinrnod or uDooDtenin{cd grouod
Ctrss l.l AP frou M-13, M629 or a
leboraory.
NOTR
Thb pr doepovida dbpsal
btslrzrrbts for conarrninord and goutd
CIasS 1.1 pmpcllotrt uidizqs. fuc
propcllnt oridlzcrx sudt as
unoon orritord, Closs 1.3 AP wtll bc
disposd of by ttstttcfutts fot td in
hogron Plaunng.
Dlspasal of stull qat titi6 of pwc
,t wn afraad pmpcllott oxidizqs
orfgiaalty ptsdusdfor tat or qainuntat
ptoposr slullbc cootdbutd through
fuwbomaulWastc Dtspsal HMX
dlspsol ptocdwa ot foutd tn Poagraph
7.4.
VANNINC
Do ra allow dtadltul o cana ino
ooute, wU, AP. brtonfuotd AP scmp
nust bc grwtdd tlvouglpu tlv dtspsal
Inoor, fue o rtc arcataary olilE dcgrccSorwfuet
NOTR
Vfuta &rg,nlha nuv bc ttsd tn olacc of
mttdrtlau llna a rte dboction of rtc
GM-3.1
Issuc No. 12
2l Septembq l9X2
t, llfiI8
{a Serq TaC (T€ t78 cr 81 87t/ b tot
NOTE
Druns going to M-136for opcn buttthg
ttust bc pbd on pallas wih onc palla on
ap of rtc druns atd onc on hc bouorrt
lhc bondd palla on bp allovusfor s$c
handlhg atd transpon by mD crata.
Butdtttg nust bc appltd po irrsfrzlrr;iorrs
ht td h tlp In-Plant Handlhg MMuaL
NO|ts
Llst *hahcr AP Wastc b Cbss 1.1 or Cbssl.i on ary rquird ldcls aouhd to hc
vlattc.
7.13.r Snall quentitics (30lb or lcss, totel) of
Clrss 1.3 propcllant oxidizcrs, iacluding
cononiratcd wastc and dust collcctor
socks, filtcrs, c!s., Ery bo disposcd of
throug! opco buning at M-136, following
Scocral dispcd prcporatioo instnraions
found in Peregraph 7.1. A comolctcd
Ilezardous $rastc hoocllant tabel fiC-
8159) must bo attachcd to cach vclostst boq
or disoosablc conaincr of wastc.
Itcm Dcscription: Class 1.3 AP
Contgninstcd Wostc
EPA Wastc No: D003 (Prc-orintcd)
Buildine Gcncrstinq Buildios No.
Prrt/Stock No: 1.3 AP
Onntity PEP: ll/cieht of AP fin munds)
otrntiw llrastc: ]llciqht of Contminrttd
Ullsr
Buildinq Contrct: FeBoa filtinq out 6c
hDc
Brdqc No: Badac No. of Ferson
6Sa'n
Datc: Datc first amount of nnstc rves olaccd
in container
RdNo: Scrao Taq Numbcr df aoolicablc)
othcrurisc N/A
Containcr No: Sclf-Exolanatory
Inrmraion Renarks: List thc contcnts of
thc containcr. Writo D00l in thc lowcr
riqht hand coracr.
wIfeocd-€ls+5't
UN Ne'r UNlll3
FPrlrlYrtc Nerr DeelEf€!1leil443
7,t1.2 Qnntiticr of contamioatcd Class 1.3 AP
SnalGE th.D 30 lb shalt bo peckagpd iD
lilod, DOT 37A 3&grl dnrms (suiublc for
slorago) eod tnosportcd to ro approvcd
loc*ion. A conplacly filld out llazsrdoug
Wrgtc h,oncllant Irbcl CIC 8159 7ft0 aod
e Scrap TsS CfC 087t, or SP 0t78) ot
Scnp I$cl (fC l(b4), as applicablc, Eust
bc anachcd b thc uppcr onc-third ofcoch
drun.
Itcm Dcscriotion: Conaminated Class
I.3 AP
EPA \trasto No: D003 (hp-orintcd)
Buildins: Gcncratine Buildinq No.
Prrt/Stock No: 1.3 AP
Onntity PEP: Weisht of Ap fin
Dqldr)
Orsntity Wastc: Weiqht of
Contaminatcd Wasa
Buildinq Contact: Pcrson Fillinc out
ttc lgbcl
Brdqc No: Bodqc aumber of oer:on
Datq Dafie first amount of nrastc was
olrccd in thc containcr
Rcf No: Scrm Tac No. df applicoblc)
othcrvir N/A
Contrincr No: Sclf Exolaoatory
Inmucrionr/Rcm.rks: Lis thc
contrnimtion in thc AP. Writo tr{l
in ttc lowtr riqht hand cotacr.
,DZ:D
GM-3.1
Issue No. 12
2l Scptembcr 1992
**r*rr^Wr- 'rr^n-*r*
fiun raP wastc in druts.
I*cacd€ls+-*t
gDI+I€i+gDIf4#l'W
ER€i+te+iHe
Da
7.t3.3
7.11.4
Ammonftrm pcrchloruc grouad smdlcr
tbra l5 microns is e Cless l.l explosivc.
Srdl gentitics (30lb or lcsa, total) of
contsninetGd or utroonteniDatcd Class l.l
AP, including contuiDatcd wasto, mry bc
disposcd of througb opco burning et M-136,
following gcoctal disposal prcperations
found in Pangr.ph 7.1. A complacd
Hazardous Westc hoocllant Irbd CfC
Utg 7l8t) Eust bc atrachod to cach
Vclostrt beg sldiog$ble.esltriss of
q,rstc. mo1ceol.De+efipp*rgffiehF
rDl44gl-
Ifrrc*€lss+-frfD
UDI+Iert-{DI€r4glW
ER'Cl{e't{.|5
Itcm Dcscriotion: Class l.l AP or Class l.l
AP Contaminatcd Wastc
@
Orsotity PEP: Wcisht of AP fin mun&l
orraotity llrastc: Weisht of Contsminstcd
!&sc.lh-pquG)
Buildinq Contact Pason fillinq out thc
hbcl
Badec No: Badec No. of ocr:on
Datc: Datc first anrount of wstcr wEs
d&caiL$csgnelgs
Rpf No: Scrao Tas No: fif aotrlicablc)
Oherwisc N/A
Conuincr No: Sclf EqilanatorJr
Ingtruction/Rcmerts: Usc thc contcnts of
thc conteiu. lllritc D(Dl in thc
lourr drht hand cotacr.
qr.oti6G. of ooooilrtcd or
umamiurcd Clr$ l.l AP grcarcr ths!
30 lb shdl bo prc&rged in doublalinod
DOT 37A 3O-d druru sribblc for
rbntp, tdplrccd oo m rppmvcdnasc
doct ftrpidcq by EWD pcrsoorct. A
coryUa bdour W.rE hooellaat
Irbd CIC tl597l€5) nust bc rtr ched !o
6c upcropthid of eh &un of rrrsts.
Itrn Dcscriotioa: Class l.l AP
GM-3.1
Issue No. Ul
2f Septdmbq l9lE2
Buildins: Giencratinq Buildine No.
@
Oraotity PEP: Wcisht of AP fin
DOUIG)
Orgntity Wastc: Weisht of
Contaminatcd llrastc fin mun&)
Buildiaq Contact: Pc6on fillins out
thc labcl
Badsc No: Badee numbcr ofpcrson
Datc: Datc fir:t amount of wastc was
d!4iLec-ee!trioerr
Rcf No: Scrao Tae No: 6f aoolicablcl
othcrtrrisc N/A
Containcr No: Sclf Exolanatory
Instnraions/Remarks: List thc contcne
of thc coatainer. Writc D00l in
thc lower rieht hand coma.
no+opc+gg*eHppirC{it}is't-
$fnSTE rll,ft{eNftIM P'n€In eR/rTErW
UN+Ie'FUNemit
FGrFWorc Nert r€gl; De03
8,6{Ie'+'f46
7.13.5 DOT llazad Class labcls shdl bc applicd o
thc &um as follows:
For Ctass 1.3, usc 'Exolosivcs B'
-€*idhorg labcls - thre cqrrs[y
spocd arouad thc top onc-third of thc
dnrn.
For Ctass l.l, usc 'Explosives A'
hbck - thrco cquatly speccd emuad
6o op onc-third of thc dnrn.
7.11.6 Propecly prcporcd &uns shdl bG phccd onu rpp,rottcd qnsc dock for pickup by
ED M-l36 pcrsonncl.
NOTR
Uslrr will bc raporciblcfor aswhg
dbpsalprudwa havc bcatfollavd. In
cz;sa tdrc:c iacota ptudura rtrlw bcat
fotlM, usqr wdll bc raprcblcfor
nfrag aq ffits na;nsart to allawpieq oldu nntatutby EUID.
m*a1 2l
GM-3.1
Issue No. 12
2l Septarbq 1992
WANN,Je,G
It b &oluety b,prrzrdru thot ro AP
ontonbntd wiih forcign &Jarr, sudt as
glova, wipcl, cE , bc san u, SS2&
NOtts
@ntu fnrcpWnfor novarcnt of
nsqfuls to ttu stonagc oaas. Sec Sabn
IlI, Pgag@t &2fo" dlsryol irsttzlrriots
lor baggd dafLTottfrwt Econ0-firc.
7.I1 INERI PROPELLIIIfT
NOTR
E*anu ccc rru,so bc t&ctt to kec?
ronhogfuus, inat pmpcllottt and vlastcs
scgrcgodfiom solvuts by ttsbtg scpo@c
oonloinlr;s dwhg tlv clututp pocas.
Solvatantonbwd rusrar ntdr as rags,
wiry, gbva, ac. 0c hagfuuJ u,rrras.
Ttu onty Mdonubtat oc DOT
17H 55-gal" dtu$, lind *fi*{ slhg bags(W), or S-galbuctafor
$uU quntitia.
NOlts
Only rdw (EPAlwofuttswastc cde
,t onbo D@3) toastat, sudt as pmpcllaas,qbsivw o" yytwldt tirs., nay bc opan
bmrd wralng b Stou and Fdaal
rcgul&ts. lnat popcllottb na arwive tustc ottd rtaclorc corrrrot lcgalb
bc opat bwltd. Do NOT satd bqt
prupellott b rtc M-136 Btrnbtg Grottttds
.ft disposal
NO|R
lhc lO- and 2A gal pbstu corubasfor
lhn noaful oc prastancild:
rD$2.1 2la
1.1 or 1.3
EX?
MAT
bt rd bqr
Thc stancilhg is o ernpty wiih'Statc and
Fdqal hogfutts vlaltc contabrq nar*ing
rcgt briorur. Do NOT pbc ttwt
pmpcllant, lr/tirlt b rcnhqarbul ht Evc '
norqbl conuittcrs. Ottly Etc naqial
shdbc pbd bt thac conmincn.
Corcct dbe$.Ierocodnrcs for inert
eropclfu rod conuminrtcd $nstG3 rcquirc
ra undcrstrqling of sonc inportant gouDd
nrlcc.
7.14.1 All rcquirEd r-gs aod/or labels nust bc
clcerty EerH incrt popcllaot aod whothcr
thc nlcdd is ao 'EPA solid'or 'EPA
liquid'. A wrslo is r! EPA liquid if it is
Etilo ruuy ard will pess through an
rppmvcd pint filtcr (Scc lppcoAix III).
Crll EIITY, ufico in douh, !o Ee&o 6is
dctcrninetion.
7.14.2 If tho iut proeettmt wastc contains ao
hrzsdou $,rstct (no solvcnts or tags,
wipcs, ctc. contanioatcd with solvents), scc
Se-tion ltr, Prrrgraph t.4 for oonEct
dispcd ionructiotr. lvlsrt all disposal
coDt iDcrl with a Wsstc Irbcl (Form TC
u25).
7.t4.3 Incrt p,ropcltrnt coatgnimtcd with solvcnrs
rod iDGd propellrot rryrslc contrniDdcd
udrh solvcmg roilor dicacl fuel Eust bc
tt.tcd ar hrzrrdouc unsilo. Disposal
Inrt$cions rrc found in Setion II,nqr+n t0.17. Errcry cffort shouldbc
Fl"Go !o nininizc thc anount of incrt rraac
cryo.d b rolvcot oonUnination in odcr to
roduao dirposrl cogtr. Hrzrdotts $restsl
c.lDot bc dirpocod of in tho M-136
Iadndrl ftoc TrGoch. Ltut
GM-3.1
Issnc No. ljl
2l Sqacmbcr DqZ
dl solvcot contuinrtcd dispossl contrincrs
wilh a llazardous Wastc kbcl (Form TC
7rt5).
?,15 PEP-COITITAIvIINAIED. ASBESTO$
COTSNNING MATERIAIS
7.15.1 h,oocllaat. F.olosivc. and 4[otechnic(PEP'I contaminatcd asbcstos cootaiilne: matcrials includo. but are not limitod to.
NBR flaoe trinmcd from RIiRM scencnts.
leboratory oocl saoolcs. dissostcd cascs.
esbcstos oufiy. crc.
7.15.2 Asbcstos containins matcf,ials can not be
buncd at thc M-136 Bumins Grounds.
Thc hcat qcncratcd durinc thc buminq
oocrations causcs thc asbcstos to becomc
ftiablc. Friablc asbcstos orcsents a thrcat to
human hcalth aod thc cnvimnmeat whcn it
is not conteincd.
1.li.l .fhc PFF contamination must bc rcmoved
fron thc asbcstos conaininq matcrigls
(ACM) aod disooscd of scmratcll firom thc
ACM. llrhca thc PEP contanination has
bcn rcmovcd to a miat thc matcrid is no
lonser rcactivc. Thc ACM may bc scnt to
thc M-336 Asbcstos Trench. Scc Scction
III. Faramaoh 6.6.
7.15.4 Compositc orcocllant contaminatcd ACM
should bc clcaned usins watcr and a
commtiblc daffscnt/soso solutioo. T'his
ncthod should rcmovc the reactivo
ingpdicnts to a lovcl that is no lonqcr
rcac-tivc.
2J5.1 Solvcnts should not bc uscd to rcnovc the
PEP contamination frorn the ACM. Usinq
rolvcntr to rcmovc thc PEP contamination
crpalcs asbcstos containinq hszsrdous $restc
nttich ir vcr.v difficult to dkposc of.
7.15.6 Lrboratow enelysig should bc comolacd on
tha clcancd ACM to vcri& rhc clcanine
omcc$. Contest S/D for Eactivc
nrrcrids lcvcls for land butid.
,D,L,2,t2
7.15.7 Ttc PEP/soao/narcr solution should bc
transfcrcd to a compatiblc matcrisl sunp.
NodS thc otno truck oocraror that thc
sumD contains soao/dcterpents. This is so
M-7)5 can treat thc untcr accordinqly.
7.15.8 lac rcmorrcd PFP contaninstion should bo
rekascd rs PFP contaminatcd unstc as
dcscribcd in Setion l. Peraeraoh ?.1.
L15.2 lliqh cocfty propglleil contsmimtcd ACM
should bc clcencd usinc qrsictr atrd g
conodiblc dctctpent/soao solution.
7.15.10 Solvcnts should not bc uscd to rcmovc thc
PFP contrmination from thc ACM. Usine
solvcots to rcmovc thc PEP contamindion
creatcs asbcstos contsinins h8zardow nestc
wtich is vctT difficult to disposc of.
7.l5.ll Leboraroty anallais should bc comoletcd on
thc clcencd ACM o vcriff thc clcanins
oroccss. Contact Elf,/D for rpactivc
natctids lcvcls for land burid.
7.15.12 Thc PEP/soao/watcr solution should bc
transfcrrcd to a comoatiblc matcrial sung.
Notitr thc suno truck opcrator that thc
srmo comins soao/dctcf,qcnt. Ttis is so
M-7)5 cal trdat thc watcr accordinqly.
7.15.13 Disscctcd casc setions that contain ACM in
tha ingnlabr gpd/or liocf, creatc uniouc
dirooaal situations. Comct EIIID for casc-
by.casc in<mctions for di.r*t"d o."
!r9s9!!.
7.15.14 Thc clcaocd asbcstos containins matcrid
(ACIiO should bc oroocrly oockaqed aad
olrccd on rhc ormellant dock for oickuo bv
thc ElltD crcw.
GM-3.1
Issue No. tl
2f September fgql
MOFPROPELLAIVT
AI{D ILLI'MINAI\TT TO WASIE
DOCK/SIIED
t.l WASTE DOCK CRITERIA
NOTR
PEP trutatuls wi;ll onty bc pitild up at arl.
EflD appovd wastc be* (scc Tdb I).M mirqio fr fturd h Sabn lI,
Pazgrailt 11.3.
t.t.r En$rG thc nnstc netcrial is scgrcgatod
mrdiag to p,ropclldnt typc et thc
docushd sod eosurc groundiog cablcs src
sfrchcd ftom cach containcr to the conmon
8rourd bcforc lcaving.
WANNING
Awld pbing pcnonnclh a posit'onwhoc
aunglarut with straps or thc vdtich
ouU pr*ant rapid ait
t.t.2 Prllcts, Htiog, stnps, or othcr approvcd
nclhods of sooriog loads must bc gvailablc
rod usGd as rc{1ufucd by thc In-Plant
Erodling Maoul, Scction lC.
9. PTEXUP CRITERIA
If tLe propcllaat or Edcrial is not peckagcd
mrding to thc abovc roquircnents aod
ttooc of Tablc [V Eovimomcntal Wastc
Diseosd is oot allowed to pick it up from
6c dock. frc westc Etlcrid Dnst bc
ptopcdy peckrgpd end labetcd aod shrll
contain no fotcfn natqial such as pop
cror, candy wnl[rcrr, discardcd lools, psint
clDE, Dutt, bolE, ctc.
NOTR
A Wastc Dtsposal Nubc (rc El24) will bc@ ou by M-136 pavmel ond cdw W
with bulkthg paxorncl or on an flflpllaae
t.
Garz tla
('t6l
R
H
l*i
EEE
FiEi
III
lr6
E
EI{
IE
$I
lr€
I: $$
*$I$I
SE$$E
$$
HH
I
[sE s
txil
isl$
r $$:
{$$$i
Iii$$s
;i$t;l
,fr
-GI
.SECTION II . IIAZARI}OIff| WASTtsSi
PREPARATION
I. IFIIRODUCIION
ltic scction providca instnrctions on
preeulng hsrdous $astcs for*erng+o
faa*ea
*of-pfmshipncnt. :
Ilrzrrdou Wrstc Acgumrlstion Arear are
thc oaly sufiorizod locatioog whcrp nnstc
mrlctielr Ery b sunulatcd bcfore beiagtnrPortcd"W$orr3re Scc Tablc I for e listing of
aproved suuulatiotr arsrs.
NOTR*xll hogfutts i,arstc conminqs nust bcrcffiWnidS an MfiSfor thc nuraiol
{f rostor*,nonboorMHSI is owiblc,(*Ming MqiB and light br.bs).
NOTE
AU rq.ird ldcls nust bcfilld h ushg a
BtnttE's Mitulc Pcn or cquiwlent (Stek
No. 51-5wA0.
NOTE
It b a vbbbn of Stotc aid Fdqal
rcgtbtbts b tnattr;prltt hogdotts trrostc onprbb lngrrtrrys (La, frutt Tcst, H-7, X-20,
A-16 o Plott III arcas o Spuc) withow
hc prupalbansc, corrtaina, oad nw$fat.
WANNING
fo&Un,alctcnutcrbls dgcribd in rtis
sabnnay bc rccuutbtd in 5- or l0-gal
bu&B or fr- or 55-gal druns in rtc w*ou. It b a fuory Air Forcc Safay
tdotul rqfuanmt for'lhn' opawbry
bttlld/ngs tls tlrrl,c conuincnt fa ilu w*oabc argcid '...as otlan as ncdd, bu
o last otsc dt wt*noy or
sl$...hoofutts wastc naaial wtll bctM ian 'llw' opaahg bulHhgs ort. eJpalol oa.'
g[srra
GM-3.1
Issue No. ljl
2f Septcrnbcr f9qZ
2. DEFIMIONS
A.uts llozardorc Wastc. Discardcd
comncrcid chcmicals u,hich hevo bcco
Sowdto bc fttal to huneos in low doscs
or aoy nstcrial carcgorizcd as ao EPA 'P'
unsto. Tho EPA wastc aumbcr for e
netcrial is fouad in thc IIWPD. Exaoplos
of rcutc hazerdous narcdds srs caston
disulfidc, nitmglyccriac, and sodium azi&.
VANNING
lf tlu cotubwrps rpA a v,oetc idcntfrd
as ai @utc hqardous wastc by U.S. EPA,b na disposc of rtc contaha. Thc
cofiaiit must bc triplc rilsd to bc
corsidcrd anpty, ond rtc rircatc rru,st bctatd as a luzardous*astc.
Buil&rglArca Reprtsentative - All
buildiogs/arcas u&ich havc aa ap,provcd
dock for pickup of unstc Earcdals Eust
hevc e dcaigDstod rcprescntativc. This
repfcacotrdve is assigocd by supcrvision !o
bo thc oontact person(s) for marcrs
conccmiry wastc disposal aad/or Wastc
Dispossl Noticcs (Forn TC 8124). This
rcprcsootat'vc is rrspoosible for thc timoly
rcsolutioa of poccdural discrrpoocics. It is
tho rcsponsibility of cach building/aree
sup*visor to inform Eovironmcnal
Ilezardous Wastc of thc name(s) of thcir
c{rllot rrprcscatative(s).
Ceution - DBigDatcs activitics in u&ich
&nego to equipmcnt mey occur.
CER - Codc of Fcdcral Rcguluioos.
Chcmical Common Name - Tho nanc
Dost oonnonly uscd b rcfcr to r choicel.ltir nano Ery or E y not be thc ssnc ac
thc tcchnic.l D.nG. For insteocc: (l)
ooEDoD DrEo - slodioc, tcchnicrl neEG -
chronic acid (2) oonno[ olnc - rcctoac,
tehniceln EG-acconc.
u
Gcmicel Technical Nane - Tho scicotifis
dceignetion of e chcoicd in accordaoco
with neniry systcos dcvetopcdby
crt blishcd oqenizatioos, such as:
Chcoic.l Abaracr Scnioe (CAS),
Ancrican Ctcoicel Socicty (ACS),
Intcrnationel Union of Pure ad Ap,plicd
Chcoists (It PAC), ce.
Ooecd Containcr - A conaincr must havc:
e lid firnly ia pleco !o bc coosidcccd
clocod. Forinrtrre:
a.A clorod-op, stel or poly dnrn nust
hevc 6c bungs scerred in fingcr-
dgtt.
b. An opco-op, stcol or poly drum must
hrvc ci6cr a ring aod bolt in placc
sod tight or e tcvcr action ring iaplc ad clogcd.
c.If e ftnncl is uscd in r closod-top
doo, it nurt bc thrcadcd gd scrarcd
ioto thc buug. Thc funnct Eust dso
heve e lid thrt complaely cocloscs rhc
top of tho funncl.
NOTts
I2vq aailmrhgs nulrtr na bc usd nllrllt
ilnppins drlons to M-16. Thc ring atd
bob nust bc in pbc ad ngfu nhenm a
dnonts ntM. Bwrg plugs on cbsd-ap
drztrs ntttst bc tightardwith a bugwdt tfwaE? drtrltt oc ntovd-
Colhcfbn Polnt - A conaiacr locetcd noxtb 6c p,roccsr for collecting rsgr, wipcs,
bnshcc, ac. Tbc contrincr Dust:
l.Bc copicd rt thc end of evcry
nortiry &y,
b. Itrrvo r DOT Ilsd Cless labd on it,
.od,
c.Corylywith dl.pplic.bb
rtqufuGocott.
GM-3.1
Issue No. 12
2l Septcnbcr l99Z
ComhsdHc Ltquid - Dcfircdby thc
Ocpcrtncol of Traospottatioa (DOI) as tsy
liquid hrving e flashpoint of > l4O'F eod< 2m?.
Cotrosivc lilatcriafs - Dcfud by DOf as
a liquid or solid that (l) causcs visiblc
dcrilnraion or irrevcrsiblc dtcratioo in
humao slrin 1fussg or intact skin of m dbino
rabbit; or (2) has a cormsioa ratc >0.25
in./yerr on stel. This itrcludca strippcrs,
stlotrg rfuls (aitric, srlfuric, or
hydrochloric rcid), eod stroag bascs
(sodiun hydmxidc, potessium hy&ori&, or
lyc).
Corrodvity (D0@) - Defined by EPA as a
solid unstc thar (l) is aqucous aad has e
pII 3 2 or E 12.5; ot (2) is liquid rad has
a oormsion rstc >0.25 in./year on stcd.
Dlscsrded Ililotcrial - Any natcdal which
is: (1) rbcodoncdor disposcdof, or (2) is e
by-product/rcsidual whcn in treamcnt, ia
slorrgp, or uficn it is uscd in a manner
u,tich consdnrrcs disposal.
IDT llrzord Oass Lobd - A labcl uAich
dcpicts tho DOf llszard Class of a
hrzerdouc q,rstc. Thc appropriatc DOTIlzed Class kbel must bc anachcd i! a!
upngbt position edjaceot to thc applicablo
Ilazardous Westc l:bd GC 7lt5) or
Sric[ito Erzardous Wastc I$d GC tlgO),
ol thc up,pcc ono-third of aoy bazadoru
wrst3 contri[cr thU is cqu.l to or grlalcr
rhm g 3e gd. Consult Tablc )OV, Figuroll, or Ffurc 12, aod Appcodix I for
infornrtion conccming thc cortect labcl to
uto.
NOIts
AIL orguia: pad6 and oxidEot rust
,uw DOT Haad Closs Labcb, rcgadbs
of rtc stc of omdno.
,[$r.2t E
Enpty lhun (containcr) - A conaiocr is
anpQy if:
3.All trrrsto firt can bc lemovcd hasba rcmoved using practiccs such rs
pouring, punping or aspiraring, Al.lD,
b. No morc tt.n I in. of rcsiduc rcE iDs
on thc bonon of tbc contrincr or ioocr
lincr, AI{D,
c.No norp th.n 3'pcrrcot by wcigbt of
fhc lotrl c{.city of thc conatincr
rtoeinc.
NO|ts
A dtlon is NOT anpry if ory orcut of
li4tid cotrbc powd ou of rtc drum Any
Itargfuttsvzstc ramining in tlp a nminq
ha can bc ranovd @ powing, putnping
or aspbathg Ls rcgubtd undq RCRA and
tnLrt bc haadld po applitfrh i,rstrzlrrriorrs
for,nd in rhit sab*
Environmcntal Semph Ctain of Custody
Reord (Corp l4f,l - A docuncot rcquircd
ufico tnosportiry e labontory saoplc for
&tcmi[rtion of hrzrrdoug rvastc
chrrac'tcristics. lac following iaformation
is rcqufuod: (l) senplc collector's Dinc,
meiling address aod tclcphonc nunbcr; (2)
laboratory's D8Es, nailing addrcss, aod
tclcphone nunbcr; (3) quaotity of thc
srnplc; (4) d.lc of shipmcot; 8od (,
dcrcription of thc samplc.
NOTE
|hc &ovc burunt (scc Figwc E) otttyqplb to Walr,c Marugatwt ottd
Envlmmatal S;rvica oil of-plat
facilitia. To &ain copia ol rtis fottt ,dtb0a.
FlennaHcUquid - Defiocdby DOf rs
ray liquid hrviag e flash-point < 14OT.
GM-3.1
Issue No. 12
2l Septembq l9Y2
Ilommable Soltd - Dcfilcd by DOT as.Dy
solid u,tich will ignitc rcedily and is lisblc
b crtrlo firc undcr ordinary tusportilioa
oooditioas thmugh fristion or retained hcat
frron nmufr cturiog/proccssing.
Ilrsh Poltrt - Thc lorrxt tcmpcraturc et
u,hich cvaporation of e subetanoc produccs
$fficicot vapor to ignitc ufien cxposcd !o e
fleuc.
ILzard Oass - DOT hazesd class as
dcfircdby 49 CFR 172. Exsmplcs of
hrzrd clrsscs rrc: 3 (flunablc liquid), 8
(conosive), 5.1 (oridizcr), and 6. I
(poison).
Ilsrdors Itilderial - Any material heving
charastctistics uAich car bc harmful o
huneo hcslth or thc cavironment.
Ilsrdous Polfmerization - A trastioa
u,tich takcs place et s rate which rcleases
large anounts of hcat.
Hazcrdous Wesae - Any discardcd, off-
spccification, or spillcd nsrcrid in onc or
uorp of thc following carcgotics: ignitablc,
rw{ivc, @nosivo, toxic, or listcd as
hrzedous wrstc in 4() CFR 261ot Scction
tr of thc Utah llazardous Wastc
Mraagement Rulcs. ltcsc natcrials arp
idcotifid on thc building IIWPD shccts.
Ilsrdous Waste Prolile lhta (Form TC
tl&7, scc Figurcs 9 & 10) - The Hrzardous
$hstc Profilc Data (HWPD) shca is e
ltio&ol docnnent which lists ell EPA,
DOf, srd chcmical inbrnatioo nccdcd for
nrrting, labcling, aod idcotirying wasto
sftrns on plant. Evcry building will hevc
copicr of 6cir IIWPD with uairyc profilc
nunbcrs.
ISDtasblG (Il(nl) - An ignitrblc conprcsscd
tlt, .r oxidizcr, e ligrid hrving a
0rhpoiat 3l4O'F, or e aon-liquid capeblc
of curiry firc, uDdcr soodrrd tcnpcnmrc
lnd
q[Jt"!26
[m3$rc, through ftiction, abcorption,
mois0uu, or slnnteooons chemical changes.
Irbdlng - Ferromcl rrc responsiblc for
hbding dl pac&agcs contriniag hazrrdous
wrslo for traoryortdon as rcquircd in 49
CFR, Subpsrt E (172.4fiL450).
Uquid - A DOT liquid is r Esrcrid thst
hs s vcrticrl flow of ovcr 2 in. within a '
ttrcc ninutc p6iod, or has onc gran (l cc)
9t DorD liqrdd lqemtio!.
Itlonifcat - A documcot rcquircd by thc
EPA tod Dqf wilch idcotifies hezerdous
wr*o queatitics rs thcy aro produccd aad
folloscd thmugt UterElcot, traosportation,.d diryosel by e sctics of pcrmmcnt,
tir&rblo, dcecriptivc docuocnts (pepcr
rdl).
Itil$ldry - Bc,forp tmosporting hazardous
wrstc, r gtoctetff nu33 n st eh
coabincr of 110 d or lcss with thc
rpropdatc h.zrsdou! nasc vcrbiagc as
ttquircd io 49 CFR 172.W.
Itilrtcrlel nesfh end Sofety Infotmstion
(!}lnSD - Ttc MIISI are prcpsrGd by ll/asc
morgcmcot and Eovironncotel Scrviccs
rod rcvicuted by Indutid llygicnc. ltc
MII$ dosuncnt conains chomical
idornation frrom veador-supplicd lvlatcrid
S.ftty D*e Shcas MSDS), safcty hazads
du, rod hcrl6 infomation.
NOtts
MHSI tnstrroriors arc.fu hc ptrc,
uwnta ninad tmtqial @ntofuutbn of
tlp ptrt t or*ful by oulur naabl nay
cnwc a dilfaar dispal pr durcfor thc
r.lstldntntlalr.a eUEIMfoi
bt*zrrbns b all strdt casa,
Nlncty-dry lladors WrS. SSorage
Artr - A ficitity 6er sumulalcs aod
rblta Doru 6.1 55-d totrl of hezardouswe frr lootcr thrrr 72 hr bot lcss thrn q)
dryr.
GM-3.1
Issnc No. ljl
2f Septcmbcr DqZ
N.O.S. - Not othcrurisc spccificd.
Orgrnic PErod& - A stong oxidizing
88cot ttrd firG hszrsd ufien in contact with
oonhrtiblc Drt€f,isb, cspccidly uadcr hfuh
tcopcranuc conditioos (c.g., mcthyl
cthyl kaonc pcmxidc).
WANN/a,G
Ov€ t't tu, orgoft paoila ncy
crystailfzc udbaonu pr*sutc or slock
sansdrdw. lf a dnonof orgoic pawbtc isav crcouttqdwirtdfic crystalt aruwd
hc vant or thc bwrg, b rot opcn; call
EIlllfor asslstanca
Peckage - All componcnts required to
contaia and tnosport a hazardous nastc
(outsido conteincr, fillcr, conaiacr, otc).
nOsaging - Ito contrinas aod aay othcr
oonponcoE Dcccsssry !o comply with 49
CFR, EilZls*eoa+
pII - A neesurc 6f th6 clkqtiniq/ or ecidity
of a solution, aumcrically cqusl to 7 for
nantral solutions, going highcr with
iutesing alksliaity rod lowcr with
incrcasiag acidity.
Placard - Fersonacl arc responsiblc to place
r writco noticc (plsrd) on all hazardous
$restc trmsport vehiclcs in accordancc with
DO|I rcgulations fouDd i! 49 CFR Subport
F (172.5@-55r).
RCRA - Rcsoutcc Conscrvation aad
Rccovcry Act.
ncactive (IXl03) - A solid nnstc that ncas
oD ot norc of tbe following:
Ir ungtrblo aad rcadity utrdagoca
violcot chrage without daoaeting.
a.
G 'n
b. Rs violcntly wi& $,!t€r.
c.Fotur potcntidly cxplosivo mixtr€s
witb uilcr.
d. Guetcc loxic gascs, valrots or
fincr in a quentity snfficicnt !o
prcrcot r &nger to humm hcol6 or
thc covironmcor ufrcn nixcd with
$rSct.
c.Ir e cyani& or sulfi& bcedng nrasto '.
u,tich cao gc[ctatc toxic gascs, vapots
or funcg in r Enotity nrfficicot o
prrrcot e &agcr !o hunen hcel6 or
tto covironmcnt uficn cxposcd !o pII
oonditioos baurcco 2 sod 12.5.
f. Is ryblc of daooetion or cxplosivc
reacion if snrblrtcd !o t strcng
iDidrfilg sourroo or if hcatod uadcr
confimcot.
S. Ir crpblo of daooation, cxplosivo
dconpocitioa or rwtion at staodard
tcopcrrtuc aod prcsstttc.
h. Ir r Chsr A or fo6iddcn cxplosivc as
dcfiDd ir 49 CFR 173.51.
R.portablG Quantiay - tls minimu6
qurodty of hrzardous unstc gcacratcd as a
rrsult of e dilchrg, or spill, which must bc
rcportcd to EPA aod/orthc Nation8l
Rcsponsc Ccorcr. Tablc )fltr contsins a list
of cornon rDslcdals 8od thcir reportablc
qurotida.
S.tdlilc Ilsrdous Westc Acomulation
Arc8 - A locrtion thrt h.s acqrnulstcd lcss
tbn 55-d lotrl of brzardous unstc or lqt
of m stc hrzrsdons ('P') wrsto. Oncc
60 55-d (or lat) linit is mchcd, thc
hrzrdotu wertc Dud bo shippd or novcd
to e 90dey srnulatioo uEl or I stonge
rrte wi6in 72hr.
NOTR
Tlu s&e uufunpdnt rutstbc o0 n&rtc poirr $ gatqfun and trdq
rte @rrol Srtc opawr. |he conuinq
ulrlr b ,lral*d wirh rtc v,gdJ 'Hogfuns
Voste'.
GM-3.1
Is$e No. 12
2l Septanber 1992
Srtollttc llezardour We$c Lsbd (Foru
tC SD0) - A 3 9l4 t 5 3t4 if.. rEd rod
nrtitc labd wilh rad lcfiedry. A Sale[itc
tLzrr{ous }Vestc I:bcl must bc placcd on
roy coataincr at a satcllitc econulation
rrre inncdialoly uficn my amouat of
hrzrdow tr'asc is plecod in thc conoiacr.
Aay conainas placcd in a satcllitc
ecsunuletioo arcr must hevc e Setcllitc
Ilrzardoug \llastc kbcl. If l3e galons or
grErlcr, a DOf llazasd Cbsi l$el is
rcquirod.
Smdl Quantity Gcnerator - Frcilities
Spoomdng or accunulsting lcss then 1,000
tglmonth of idcntificdhazsdons rmstc or I
lcg/moath of acutc hazardous wrstc.
Solld lVeste - Any discardcd matcrial thst
is e solid, liquid, somi-solid or coataiDcd
8tsous D.tcsid resultiag fron ildustrid,
commcrcid, mining, or agriodtml
opcretions aod is aot excludod undcr 4O
CFR 261.4(a),2@.30 or 2@.31.
Sohent - A liquid thst is capeblc of
dircolving aoothcr substaacc.
Spllt - Thc accidcntal discharging, spilliog,
lcr&ing, prnping, pouring, cniting,
cmpying, or dumping of hezardous wrstcs
ot Eelcrials which, ufien spillcd, b@omc
hazrdous ur.stes, into or on a[y land or
wrlcr. Itis mey dso includc spills ooto
eryhslt or ooosrrtc peds. Spills shdt bc
rtportcd by calliag tho Thiokol Encrgency
Rcsponsc Nunbcr (F-xt D2 at thc
Pmnontory location).
NOTE
ArE spillwhich accds tlu rcpotablc
quondty rquira rctitbatbn of tlu Natbrul
Raptsc hta (l.lRC) by llae
t4ougarcnt and Envimmutal Santtca.
t80.,?t
TCI,P - Toxicity Cheraacrisic l-ehatc
Procedurcc.
Todc Itilrlcriet - Aay substeocc heving tho
rbility !o c.usc daosgc to living tissuc,
inpoirmeo of thc ccotral ncryous systcttr,
scvcr! illn6g, or (in cxtremc escs) death
ufico ingpdcd, iDbdcd, or abeorbcd thrcugb
thc skin.
Tbcetmt - Any ncthod, tcchniquc, or
Inooerr, iocludiry ncutrrlization, dcaigDcd
!o charyc 6c physical, chemicrl, or
biologicel chrr&lter or compositionof rny
hrardour wrstc so rs to nantralizo such
rnttqt, or ro lg !o rlcovcr cocsgy or
Ealcrhl rcsoufiges from thc unstc, or so ss
!o rtodcr snch wasa Do[-hazardous, or less
hrzrrdour; s.ftr !o treosport, stolE, or
disposc of; or rncorblc for rccovety,
ancorblc for cbregp, or roduccd in
vOlunC. NO treatoCnt Of r hezerrdous nnstc
Ery b dorc without a permit.
TSDF - Trcatncnt, Storagc, aod Disposal
Fsility.
Uniforn Ilsrdous Westc ltflonifcst - A
doeuocot, EPA Form fiI/00XL (aod Formtr[I}I2r,,if ncccssery), wtich nustsEpcoy dl hazardons unstc tmnsportcd
on p$lic highunys. Ite complacd furm
Enst conply with all requircmcots found in
40 CFR 262.n. Thc maoifcst docuncnt
truEftr! outody of all hazardous wasto
fron tho tino it lavcs thc gcncraror urtil it
ic rcocivcd rt tho disposd facility whcrc it
recivcs fiad upormcnr.
Wrilin3 - Dccfnetcs rtiviticc in utich
bodily injury nay ocsur.
WrCc:
D Wrstc - A *rctc u,hich is hezardoru by
chrregrcristic of funitability,
corrosivity, rcecivity or
cxcccding TCLP linis for t
GM-3.1
Issuc No. lrl
21 Septeo$cr l99l
maals eod 32 orgaaicr (se
Trblo VII).
F WsSe - A hazardous wrstc which is
listcd io 10 cFR 261.31 rs
bcing ftom noa-spocific sourpc3
(F001-F005 u! eonnor liqui&
thet arc uscd for solveatc or
doSrcasers (se Tablc VI).
K Weste - A hazadous $as!e u,hich ig
listcd in 4() CFR 261.32tc
bcing fron a spocific sourtc
(s6 Tablc Vt).
P Wtsac - A hazsdous nasto which is
listcd ir 4(D CFR 261.33 sod is
a conncrcid chcnical product,
neaufacturing chcnicsl
iilcrmdiarc, or off-spccificdon
oomncrcial chcmical thrt is aa
acutc hez.rrdous n astE.
U llloste - A hazerdoug nnstc which is
listd i! 4O9 CFR 261.3t rnd is
e comncrcial shanicel pmduct,
nmufrctudng chcmical
irtctncdi.lc, or off-specificetion
conmcrcid chcmical th.t is
toxic.
WestG Disposot Noticc (Form TC tlZ) -
A noticc which pmvidcs infotmetiono
buildiry pasooncl oa how to corrcct e
Asccpeocy so that picknp aod disposrl of
6o itcm(s) mry b accomplishcd in a tincly
EerDGr. ltc Westc Disposal Notioe will
bc lcft with building paronncl or oE r
W.$o ltfianryencot md Eavironmcnal
Scoiccs-epprovcd nastc dock on any
itco(s) that catrDot bc pickod up by l*186
dispo$l crcw! bcc.lrso of a p,roccdurd
Orcrceeocy.
3. REFERENCES
@c of Fdaal Rcgulzrbts,'Iillzudou!
W.tto,'Tltb 40, p.fi 26() rhrougb 265
9D019 2t
Uc olFdcml Rcgttltuns,
'Trrnrportrtioa,' Titlo 49, perts lfi)
trough l99
fuural S$ay otd Hcalth Mailul, Cheptcr
4, 'Ileodling and Storege of Flannablc aod
Coubnstiblc Uqui&'
Ciawal Way aad $Icalrr, Maru.al, Chaptcr
5, Color Coding, 'Westc Irtelcrid :
Coffiincrs'
fuaal Salal arrd Habrt Marual, Ctspra
5, 'Ueing W.sto Contrincn in llazardous
Locrtions'
futcml Sdcty arrd Habh Manul, Chaptcr
5, 'Collcction end Disposd of Brplosivcs,
Propcllrots, aod o|hcr Hazadous
Iddcrhb'
Gqaal Sday orrd llcalttt Marual, Chapcr
9, 'Ileodling aod Traosportation'
Gawzl Sday aad H@ltt Manul, Chaptcrll, 'Uso of Firtr Synbols'
Hqofuus Wastc Motugatunt @ntingatcy
Plorfor Sprut
Hosfuus Wac hofilc Dota Shea
(HWPD)
In-Plott Harutlbtg Mail.al, Soction XI,
'Geocral llaodling"
Matqiol HeobL aad Sday Infornutilm
(MHSI)
t[oqbl86ay Dota Shca (MfiS)
Raouec @nsrrrrurrion and Rawry Aa
(RCRA),rs rncodod in Novcnbcr l9t9
Tdtnicril Disc/cg/w's (ID)
Utdt Hosfuus Yastc Marugatutt
Rcgnbtbtts
4. MAIERIAIS AT{D EOT'IPMEIYT
GM-3.1
Issnc No. Ul
2f Scpacmber fgql
Buony's ltfirrclc Pen or cquivelcot
. (No.5l-5tnD4)
Folyethylonc &um liners (aoaconductive)
Vdost t &un lincrs (conductivc)
DOT 3o'd or 55-gal l7E stcd druEg
DOT 3Gd or 55-gnl l7II stccl drung
DOT 30-gd or 55-gd poly dnrms
Bung plug wrcoch (aon-sporkiag)
Scrap Melcrid Tag CfC 0t7t, or SP 0E7t)
Ilezrrdou Waste I$d CfC 718:t)
S.fcty fillcr spout
Gmuoding stnps
.{pproved nastc contaiacm
I{ezerdous llr.sto Storagc Containcr
tnspocton Chccklist GC 8091)
Salcllitc Hazadous Wesrc I$el GC il90)
SPECIAL SAFETT AI{D IIEALTII
REOTIIREI}IENTS
PENSONAL PROIECTION
EQI'IPIVTENT
NOlts
Pbning or MHSI wi[ dictac pqtorul
plotmttvc quipnd rcquirarcnts.
Fcssonrcl henrlling hazardous malcrigls
mtst nprr flrnc retardant coverells or
smocks, safay shocs, glovcs, aod chcnical-
typc gogglca ot safay glasscs with si&
shiel&. All clothing musi bc closcd.
Ncoprw or Ddural nrbbcr glovcs should
bo r*om.
Fcrsomel rrcrting with sanic scnsitivo
Eatcrisk Dust wcar cotton clothiag, flenc
rccistrst covcrrlls or snocks, and adcquetc
cyc prctcction.
Whco hrorllint chemical strippcrs or other
cu*ic solutioor, oootec{ of thc Drtcddc
with cyes, sE!,.trd clo6ing nust bo
evoidcd. C{Gfully follow the sefay
pruntionr rnd urcer thc seftty rppsrct
dCIcribod in thc MItrSI.
5.
5.1
5.1.t
5.r.2
5.1.3
rst-J 30
5.1.4 ILsdlirS of noc hrzerdous nrtcrids
prcscots sonc dcgrtc of hcel6 haz.d.
Wrsh har& ofien eod do aot allow aoynuial to bo irypsid. ProlongC
csposurG to naly eoy y8[ror, func, or dust
Eay c.usc luag &'negp. Usc thc prcpcr
rccpirator listcd iD tho MIISI. Always wash
hrodr bcfurc csting or snokiag.
WANNING
lhc opa'wr rust dtdc plamhg, MHSI,
owith Indtstblllygiau o daanbp
protaivc q,A,n rt rq&d vdwt nor*tngwitltclwiul*
s2 IIAZAru' COMMT'MCATION
PROGNAI}I
Onc of ltiokol's forcmost oblrtivcs is !o
s6 thrt tho saftty aod hc.lth of csch
coployco is couidcrcd in cvcry job. All
cmployca cao hclp achicve this gpal by
beoming tbomugbly frmilir with thc
Ilrzrd Connunicotion Program rod using
it rc e gui& itr dispoel of all hazardous
mrtctiels.
5.2.1 New hire tniaing hes bcco estsblishd to
hfotu cmployccs of:
t.hoccdurcs cst$lishcd to covcr all
cmployecs who ney bc cxposcd to
hprrdoug nrtcdek.
b. noquircocot3 of thc lhzard
Communicetion Staodad.
c.Opcratiou in uAich hazadous
E rcdds arc pruscot (gcncral
ovcoicw).
d. Locetion eod avrilability of thc writtcn
brzrd oommunication lrmgren,
irclrding thc llrzrrdous lylrterid List
(HML),ldeocrial &ftty thtr Shca
(MSDS) or Mrtcdd llcdth eod S.fcty
Idomaioo (MItrSD, rnd Hazer&uc
W.stc Profilc lhb Shcct (IIWPD).
GM-3.1
.Issue No. Il
2l Septanber 1991
G. Tho significaoce !o the
cmployco of cach section of
infornetion on thc MSDS, how
, , rced it, aod urhd it ncans.
Pr,ocodurcs for training enployccs in their
rvort arca includc:
Information about physical and
hcelth hazsrds of shcmicals io
thc work arcc.
Dctecting tho prcscncc of
hrzrdorls Eetcriab -nonitoring proccdurcs, odors,
visibility, ac.
hopct sclcction aod usc of
pcrsonel protcctivc cquipmont
(PPE).
Emcrycncy proccdures in thc
cvcot ofrccidcntel crposur! to
hrzrsdons matcrials, iacludiag
cocrgcncy phonc numbcrs aad
thc locetion of eyc rrashcs and
srftty showers.
IIow to dctc,ruinc hazards by
rcading a labol.
The location of thc
MSDS/}4HSI and tbc proccdurc
for rwiaring thcn and/or
ohrining. copy.
8,How o obain thc correct
MSDS/IUHSI for thc hazardous
substsocc uscd by thc cnployec,
srch as uso of thc tmdc nane,
spccificatiou numbcr, part/stock
numbcr, ctc.
h.llow thc MSDS/MIISIiT
updatcd rod thc procodure for
obtririog updatad copia ftou
tho chcoicel naaufrcntrcr,
inponcr, or distributor.
5.2.2
a.
b.
c.
d.
o.
f.
,lsojr 3l
lto mcasuru cmployccs cro ta&c o
prcicct 6cosclvcs from chcoicsl
ctposurca including thc nsc of cye
wuhcs, froo shicl&, rtqfraor:, ctc.
j. Tnining u,Aich ig donc pdor to thchdliry of hezadous cheoic.b,
ircluding coployecs ufio mey only
tcoporsrily do thb umrt.
k. Updr0od tnining u,hich is rcquircd
ufico thc employcc hes tnnsfcmd
jobc or dqnrtncots.
Updrtod tniniag u,hich is r€qrft?d
uttco chaoges in chcmicals or
opcretions havc occrrrrcd.
5.2.3 Supcr,visioa will Gstrblish rn Area Speific
Hezads Tnining hogran.
Supcrvision ic responsiblc to: (l) crcato
rod nrintria e list of hezrrdous natcdals
foud in thc unrk rrca, @) cstsblish eod
Erintah e lIACS requireoart, (3) tr:ain
cmploya, in arca spccific hazrrds, and (4)
pcriodicelly urdit cnploycc conpliaocc
erilg tto wort pcriod.
6.DEFOSAL IMITRUCTIONS FOR
LIOTTD HA" ^ IIDOUS WASTE
ltc followiag stcpc must bc conplacd
bcforp. ooffiim(O b uscd forthc
smuluioa of liquid hazardous mstc.
6.I ES'TABLISH PROCEDIJRES;
Building pcrronocl Dust csteblish
ryrop*lo proccdures for tho arce speific
darib of thc hendliry of liquid hazardonstrrrt wrlhin thdr rcspccivc wort rrru.
Rcftc O Scclion 9, Ilezardoug ltrtasls Profilc
Dltr Syctcm for rdditiond infurmarion. All
rmlicrbb FGdcnl, Strtc, Loc.l, and
Thiokol regnlrtionr Eust bo follourod.
Buildins rupcrviriot ir
GM-3.1
Issue No. ljl
2l Scptanbcr 1991
62
6.2.t
recponsiblc for tho tniniag of buildiag
pertonncl ia thc erea spccific disposal
proccdures.
NTSTtCI CONTAINER, INTEGRITY
Sclcct g conaiocr thet is uitrblc for thc
liadd hazerdous wastc to bc dispoeod.
6.2.2 Uso only rcw containcrs froc of dcfccts that
unuld ceuso it to lc.k. Thc conaincr nust
bo froc of bufes, aod sbdl hevc no mrjor
dcog or crc.scr which could gffcct its
stsuc0rrsl intcgrity. Thc conaincr must
elso bc fr,oe from scvcrt rust (scc Figure 3).
6.2.1 fhc containcr must bc iospcctd !o cosurE it
is froo of rrarcr.
63
6.3.1
MARK THE CONTAINER,
Oblitcratc dl previous lrbcls ard
pmgictory infotuuioncf,ccpt for DOf or
tIN ccrtifications.
6.t.2 Complac thc applicable llazardous Weste
I.rbd (se Appcodix I, TC 7lt5), or
Setcllitc Hazardous Wrstc Irbcl (scc
Amcodix I, TC tl90) ia its cntirety with a
hony's Mireclc Fen, or its cquivalcot.
Arrch thc labcl to the uppcr onc third of
thc contrincr.
6.9.1 Thc applicablc llszrrdous Wastc l:bcl or
Srlcllitc Hazedous Wssto hbcl must bc
visiblc oa thc dnrn fron thc appmach io
thc nastc dock aree to eo$rrc thc seftty of
crncrgcocy respondcrs in thc cvcnt ofr
Eishsp involving thc nase druE.
6.3.4 A DOT llszsd Cless Irbcl is requirod for
contsincrs 5 qallons or qrt tcr for dl of thc
hrzrrds thrt rrc indicstcd for thc pedsular
wrsta bcing gcocraiod. Rcfcr o tho
Itzrdous lvsslo Profilc Drte Systcm for
infotuetion on e spocific $rrstc.
l.
l.
qD$13 t2
6.3.5 Anrch thc conu,t DOT llazard Class
bbcl(s) to thc containcr djaccot !o thc
Ilrzrrdour W.s!s lrbcfl or SaCUitg
Ilsdom WrsE kbcl (scc Figurc 12).
DOT llrad Cless Ilbcls nust bc afi.chcd
in m uprigilposition.
NOT'E
All pbsdt: clrltuitla,s trsdfor poisont,
(61), ttut* ltovc rtc tard 'Polson'pamiart, Dwlcd on rtc coubint.
6.3.6 Whcn norcdrra sas DOT l&zerd Class
I$Gl is urcd, thc lebcls nust bo adjaocat to
cach o6cr.
6.3.7 Multiplc DOT llazsd Class kbclr ney
dso bc atectcd !o diffcrcDt sidcs of thc
dfoD if rcoa3.ry, to wrs! pcrsonncl of
h.ards uttca appmching fton difrqcnt
ditcc-tiou. Ooly ono llazardous Wastc
Irbcl or Sadlitc Hrzcdorrs \lrastc Irbcl is
!o bc uscd oa r contrincr.
6.3.8 Couult T.blc XIV !o fild rhc corrcct DOTIlrad CLrr l$cb !o use.
6.3.9 Anrch e 3roond to mctal coataincrs thet
will conEin flemm$lc liquids.
6.3.10 lto abovc iffitrctiou must bc follorved
bcforp eay *rcto is placcd in a contahcr.
6.1 T!,ACE TEE WASIE IN TIIE
OOITTAINDR
6.4.1 Rpoove bury plug eod rasin for latcr.
Loocco lbc vcot.
6.4.2 Pls e ftd in buag holc. An
Eryircnncal Hrzrrdous Wastc approved
s.ftty frrdfi.t screur into tho buag holc
.od brs lo rbDrtic.Uy closing lid is
ercerrld (at., Prrotaoccd 5510).
6.4.3 Cmcr bood octl cootriocrs uficn
trogftti1g frnnehlo liqui&.
. GM€.I
Issnc No.ljl
21 ScptGlnber f9qZ
6.4.4 Crrcfirlly transfcr nastc liquid ino thc
fuoncl, avoid splashing. Clcea any splrshcs
or rpills iuncdiritcly. Witi r scoop or
epoole, llmovc my resi&rc lcfr in thc
collocdon cont itrcr and placo in ao
sppmpfttc conteincr for rclid hazardotrs
wrgto.
6.4.5 Whcn traasftr of liquid is complac aad
fitorcl is cmfy of uragtc liquid, renovc the
fitoDcl and teplrcc thc buog plug aod fingcr
ti$tco. ffusing a sefay firoDcl, tho funncl
Esy b lcft scrru,Gd tightly into thc bung
holc. Closc thc lid of thc asfcty fuold.
Tl3hleo thc vcnt plug fiager tight.
6.4.6 Conoincrc Eust not bc complacly fiIlcd.
Suffieicat hcad specc shall bc providcd for
all conteiocrs for liErids to cxpeod as
Eopcairres iac'rpasc. :Ifrcaaeiacranot
@Fill5s-g8ldilns !o Do grcatcr thaa 6 in. fron thc top
of thc &un.
6.4.7 All labcb and narting nust rpnaia legiblo
utilo conoircts 8rc bciag fillcd aad stored.
ncphce any labcls thar bcconc illcgiblc.
6J SEAL CONTAINER,
Rcnove safcty fuDrcl. IDstell bung plug
end vont plug. To eosurt e tight,
mnlcating scal, rcplacc aoy gaskcts rhrt rre
urora or brokco. Tightca with e bung
urrcocb. Corrcct bung plugr must bc uscd
utco scaling thc dmn. DOT l7E 55-gd
&uns arc manufacturcd with cithcr e
Rcikcs or e Trisurc port in thc dnrn bcad,
rnd c.ch hes e specific plug o bo uscd rs e
clocurp. Tho dnrns rrc idcotifiable rod
Eust uso thc plug I follo*!:
6.5.1
re0.s t3
L Thc Trinrc pott hrs a hcxrgon flloge
indcotcd in thc &un head to bc flnsh
with thc hced. Itfu pon BtIst hrvr
thc mundplug insallcdo ohaile
dght $rl.
EI"It
Trinrc Port ad Bung PlqB
b. ltG Ric&cr port ir rcuad rod
protrldcr rbovp thc dnrtn hc.d. Thi!
port Eust hevo thc hcxegoa plug
innrlld o oboin r tight rc.I.
Gil[-3.1
Issuc No. Lil
2l Septanbq l9tl
Nylon
Washcr
,dll,n6l
nHrc! Port and Bung Ptttg
PREPARE FOR, SEIPMENT
Irspcct tho connincr for overall
coadition
Rcoovc aay sludge,liquid, or rcsiduo
ion thc bp rad sidcs of thc
codaiocr.
Rlpls Sdcllitc Eazardouc Wasc l:bd Gf
u$d) with a llrzadous Wastc kbel.
Conplac dl rpplicablc infotuuionon 6c
Erzadous $/rstc IJbel. Tho acetuulatioa
strfi drr is tho &le thir lsbcl is applicd
Anrch S6 rll*ardom $/rse bbcl dircctly
o! bp of tho Sarcllitc lLzadous Wgste
Ilbd, ro 6rt thc Srlellitc Wasto Irbcl is
bt lly oblitcrrtcd
Eosrrc th.t dl l&lr rre lcgiblc.d thrt
6o Eandouc Wrsto lJbcl hrs bGGo
corylcrcd using e Buoay's Mireclc ko or
cquivrlcd.
6.6
6.6.r
6.6.2
6.6.3
6.6.4
tI$t..la v
GM-3.1
Issnc No. ill
2f Septanbcr 1992
6.6.5 Dnrms ma bc act on Dalla! for cesc of
novins thcm around in thc arca. Howcvcr.
it will not bc ncocssary to boad thcm or usctwomllas.ffi
ir
Cee*eerd*er
eenFdUdflil,
6.7 WASIEM
(oPTroNAL)
Ovcrfilld conldm:, or contrircrs rh.l arc
drnagd or bufod, will occd to ovcrpackcd
ot hevc thcir uresto tra$fcrrcd. Cootact
EHSI for specific iutoctioos if nastc
tnrsfcr fron ono containcr to mothc is
nccc$er)r.
6.t
6.t.1
PICI(T'P CRITERIA
EIflT
to hevo &nu(s)Digtg[& trlo?ortc+te
M.l86, All dnrns will bc oickcd ugwithin
Only drun(s) callcd in for oiclug will bc
lggggl. Earinarcd llezsrdous Urastc
DigXUD-elSe will not pick up thc metcriel if
thc hezrdous rmglc nrtcrial is not
pr*.Sod according !o thcso outlincd
Gquircocotr rnd thosc of Tablo IV, or if it
ir not pleod on ra rp[rrovod $astc dock
(re Teblo t).
tDt3.t4a
6.t.2 Any hazardous wrstc rh$ is treosportcd on
pnblic roeds (i.c., from Test, Ptmt Itr, H-
7, A-16, or X-A)) Dust bc acconpooicd by
e rigecd Uniforn Ilezardous Wastc
lvlroifcst (sco Appcndix $. l,{eteriCe.+,il1
e..+*oa*dob'
NOTB
All nahfar wdll bc comolad by thc
Haadous Wastc @nttocra?.
7.DISFOSAL INSIIRUCTIONS FOR
soLID HA-lltOOUS WISTts
Thc following stcps must be complercd
bcfore a coataincr(s) iS uscd for the
.cc{Euhtion of solid hazardous $astc.
7.I ESTABIJSHPROCEDI'RES
Building pctsonncl Eust cstablish
apprcpriatc eroccOnrcs for tho area spocific
darib of thc haodliag of solid hazadoug
rrrrtc within tbdr respcctivc nrcrt areas.
Rcfcr to Scstioa 9, Ilazadous Wastc Profilo
Doa Systcm for additional infomatioa. All
apliceblo Fcdcf,rl, Stetc, Irc.l, ard
ltiotol rcgutatoos Eust bc follonrcd.
Buildiog supc,wision is rcsponsiblc for thc
tnining of building pcrsonncl in thc area
speific diseossl procodurcs.
7.2
7.2.1
ESTABIISII CONTAINER INIEGRIY
Sclcct a coatrincr thet is suitablo for thc
solid hazardous $astc to bc disposcd.
7.2.2 Usc rcw coDtdnas frec of dcfects rhat
would causo it !o lc.k. lto coataiaer must
bc frcc of bulgcs, aod shell havc ao najor
dcog or crcrsa u,tich nould affcct its
stluc0lrd inncgdty. Thc contaiocr must
sbo bo froc fton sc'yetE nrst (sco Figure 3).
7.2.3 Thc cofris Eust bG ilsposrd !o cosurc it
ir frec of unu.
GM-3.1
Issue No. ljl
2l Septonber lgYL
infotuation cxcept for DOf or UN
ccrtifications.
7.3.2 Complcte thc applicablc Ilazardous Wsstc
Iebct (Appendix I, TC 718, or Sarcllitc
Hezadous lVastc labcl (Appcndix I, TC
tl90) in its cntirety with a Bunny's Miracle
Fen, or its cquivdcot. Atech thc label o
thc upper onc.third of thc conuincr.
7.3:l Tho applicablc llazardous Wastc l:bcl or
Srtcllitc Ilezordous Wasrc Lobcl must bc
visiblc oa thc dnrm fron thc approach o
tho nastc dock area !o o[susc thc safcty of
eocrgcncy rcspoadcrs ia thc cvcnt of a
Eishap involviag thc rursa dnrm.
7.3.4 A DOT llazad Class kbcl is rcquirod for
containcrs 5 qallons or gltater for dl of thc
hazards that arc indicatd for thc particular
uastc bcing gcacrated. Rcfcr to the
Ilezardous Wastc hofiIc Daa Systcn for
infutuation on a spccific wastc.
7.3.5 Acach thc corrcct DOT llazad Class
Irbcl(s) to thc contaiocr adjaccnt to thc
I&zardous \tastc labcl or Sstollitc
Ilezardous ltrastc kbel (sco Figurc l2).
DOT llazad Class kbcls Eust bc attachd
in aa uprigbt position.
NOT'E
All pbstb containqt usdfor poisors,
(6.1), rust luvc rtc vtord 'Poison"
pqaruaen ty n61d on rtc containa.
7.3.6 \thcn morp than onc DOT llazard CtassI$cl is uscd, thc labcls must be adjaccnt to
erch other.
7.3.7 Multiplc DOT llazard Class hbcls mey
dso bc anschcd o diffcreot sidcs of rhc
dnlE if OcqBsary, to wEr[ personncl of
hrzads whcn approachiry ftom diffcrcnt
ditcslions. Ooly ono llezardous llrastc
Irbd or SstcUito Ilrzedous W.stc lrbcl is
io bc usGd oB. coatrircE
73
7.3.1
MANI(IHE CONTNNER
Slitcrrtc dl prcvioru labcls aad prcpdaor
rctl'ts
7.3.t ConsultTablo IV oa how to obtain DOf
Ilszrd Cla$ Libcls.
7.3.9 Afrach e ground strep to mctal contaircrsrh$ will contain flamnablc soli&.
7.1 PT"ACE TEE WASTE IN TIIE
CONTAINER,
7.4.1 Drun bolt/nuttcogion riogs may bc
tcphccd with lcver astion tcasion rings for
crrc in saliry thc &un during
sunuletioa. Rctsin tho bolt, nut, aod
tcosioa ring for larcr shipmcnt
7.4.2 Plrcc only conpatiblc uatcrials togcthcr ia
thc srno dntn. lllhco disposing of
ditrcreot tlpcs of solid $,lstc, rcfcr to thc
building's Hrzedous Wastc Data Shoa for
thrt pcfiicrd.r prcccss urastc. If thcrc arc
roy qucstionr, @ntact rr!. westc dock
coordiartor or EIITY.
7.4.3 Unlcsr spccifically iostrustd ia writiog by
EXlSt, do not dispoco of frcc liquids iao a
solid r*eac dilm.
7.4.4 Conaincrr conteining solid hazardous nnstc
nust rlwry! bo closcd uficn nasto is not
bdrg addd. Ooscd contsinqs must hevo
thc lid sccurcly $rchod. Thc tcnsion dng
Eust bc in placc with thc lcvcr lockcd or
thc bolt aod nut tigltcocd complctely.
7.4,5 Rcuove aoy spills, sludgc or rcsiduc fron
thc outsidc of thc dnrn.
7.4.6 All lsbels rod nerting must rcmain lcaiblc
ufiilo comrisr are bciry filld ad storcd.
Rcphcc roy lrbclr ttrt bocono i[egiblc.
7.4.7 Fill tbc gonrrincr rs conplacly rs lnssiblc,conpcciry rnrto if porsiblo.
7.5 SEAL COIIITAINER.
Rcfle 6c lsu rcion tcogion riog, if
u$d, wilh r bolt-tcosimdry. Sbd &uns
nusthrrc 5/&h. bolUnutto sccrue thctobn riry, poly &uns Errst hrvc e 3/t-
GM€.I
Istrc No. ljl
2l Septanber 1991
in. bolt/nut.
, NO|ts
Sa,wc thc nu on rtc 5/E'bob tcttsion rlrl,g
to tlp gtoovd sidc.
7,6
7.6.r
7.6.2
PREPARE FOR SHIPMENT
Rcmovc roy sludge, liquid, or residnc fron
tho op aod sidcs of thc coataiocr.
7.6.3 Rcplacc Satcllite Ilezerdous $rastc I$cl (if
n$d) witb e llazrrdouc Wastc I$el.
Conplctc all applicablc iafornatioa oa tho
Hezerdous Westc l$cl. Thc accuuulirtion
strrt &tc is thc &lo thfu labcl is applicd.
At ch thc llazardous Wastc hbcl diroctly
or top of thc Satcllitc Ilazardous \lrastc
Ilbcl, so rhst tho Setollitc Wastc kbcl is
totally covcred ftom vicw.
7.6.4 Eosurc thu all labcls ers lcgiblc aod thu
tho llazedous Wastc kbcl has bccn
conplacd uing a Buany's Miraclc Pen or
ogivelcnt.
7.6.5 Dmmg may bc sa on oellas for easc of
movins thcm arpuod in thc arca. Howcvcr.
it will not bc necssary to band thcm to usctwopallc8.ffi
ceedilien'
?r5't hllcg nmt bc eitrrtcC te ^"ew fer mf,c
@
Itrspcct thc containcr for ovcrall condition.
t[}10.16 36
7.t
7.t.1
7.t.2
t.
7.7 WASrE OVERPACI( (OPTTONAL)
GM-3.1
Issue No. Ul
2f SeptGmber Dql
t2
t.2.r
PACKAGE WASTE
SneU quentitica of hazardous snstc thet
c.trmtbo disposd in e building
consoli&tion drun (rcfcr to Sostion 9,
Hrzrrdouc Wsstc hofilc Drte Systcm)
shouldbo left ta thc originel containcr if
pociblc. If mt possiblc, placc thc $nstc ir
s cofrircr rh{ wiU fotu r tiStt sc.l aod is
conpetiblc with thc speific rrrastc. If thcrc
ir r qrcstioa as !o thc appropdatc conaincr
for e spccifrc msto, oontact EIIV/ for
dircction.
t.2.2 Clcaa aay coatsmimtion offthc outsidc of
tho nasc container. If aoy contamination
rtm.ins on thc outddc of thc containcr,
plrco tho containcr in a hfgg-ee!tri[g.t3glscelit.@
8.2.3 If thcrc is my possibility of thc wastc
comincr leaking or brcakiag, or if thc
wrstc Ericrial is vcty hrzardons, placc thccomincrire@
@
Eratwlc:
1 oim wilJ fit iruo a I ouut.
I auot into I oallon.
I oollon into 5 eallon.
NOTts
Tainc rtc fids will funhq orqvcnt lca*ine.
t.2.4 It is pcrmissiblc to ple nultiplc cootrincrs
of thc srnc natcdsl (sanc stock nunbcr)
in e plestic brg or box for casc of tnosport.
lto containcrs must bc placcd so thet they
will not brcak or spi[ h tnosporr. Do notplu noru contrineo in soy beg or bor^'.n lto bq or box cro srfcly cerry.
t.2.5. Sbck aumbcrs tha consist of nore thraoBI[t, gnch u two pctt rdhcsiver rod
two Ftt p.i6, Enst hrvc c.ch p.tt
prctryod, lrbclcd, and dispoaod scpotrtely.
RGftr to Sdion 9, Ilurdous Wrslc
hofilc D.b SFtro frr rpocific dcoib.
Comaincn lh"l rrc dmryod or bufod, will
ncd !o bc ovcrpcckcd. Coatrct EIIIV for
speific instructioos.
PTCKI'P CruTERIA
Cell Ilrzrrdous Wsslc Picluo crctr,! Elnnt '
!o havo drun(g) DigIgUD trueoiC*e
l+136 All dnms willl bc oickcd uo
within ?^ hours of timc thc ordctr is
recivcd. Onlv dnrn(sl called in for oickuo
will bc rtmovcd. Ilazardous Wasic oickuo
etg!tr EX*II will not pick up tho natcrid if
tho hrzrdous unstc matcrial is aot
p.c&ryd mrding !o thcsc outlincd
rcquircocor rod thoao of Tablc fV, or if it
ir not pleood oa ao apptovod rrasc dock
(ge Trblc D.
AIy hezrrdous $rrstc thrt is tnnsportcd on
prblic rordr (i.c., frorn Test, Pt ot III, H-
7, A-16, or X-Z)) nust bc accomprnicd by
r s[ncd Uniform llezrdous Wastc
l,lroiftst. (scc Appcndix Q. Metcdels wiU
[ot bc tnuportcd unlcss thcrc is a conecfy
oonplacd E riftst on thc $aste dock with
ttc rryaslc nalcridc.
DISFOSAL IIiTS|TRUCTIONS FOR,
S|I}IALL OUAI{TITIES OF
II{ZARINT'SI WASTE
Thc following stcps Eust bc complctcd to
diryocc of e sndl queotity of hazrdous
'wrslc, lcs th.'er.oqn l-s 5 gd.
t.l EYTABI,IIIH PROCEDI'RES
hildins pcrronncl Eust cst$lbh
r1tpropri.lc proccdurca for tho ercr speific
daritr of tho hrodling of sndl qnniticr of
handou $rre wititr 6cir rcspoctivo
nort rter. kftr o Sc-tion l0 for
rdddood infornrtion. All rylicrblo
PGdGal, $Ja, Local, rod ltiokol
rGtuldonr uurt bo bllourcd. Buildins
qcrvidor b rapoosiblo for tLc tniniag of
bdldrypcrrooocl il thc rrce speificdirpd procotncs.
reI't7
t3
8.3.1
8.3.2
t.3.3
8.3.4
t.l
8.4.1
t.4.2
t.4.3
9.
IDEITTITY WASIT
Conplao a llrzsdous Wastc IJbcl ed
.rrch it !o thc contriacr or plastic bsg. If
tho oontainct is too smdl for a llazrrdous
Wlslo lrbd, rcrl tho $asto coot iDGE in r
plrrtic bry aod atrch thc labcl !o thc plestic
b.g.
It il Dot necarrr!, to Plrcc DOT Ilezsrd
Ct sr IJbeb on oontriDcr3 thrt rrc less 6"'r
l3e grl (cxccpt for oxidizcrs or o4roic
pcroridcs).
ilm
acroira+tc'
Only oac llezrrdous mstc I$el is
Fquircd for cach beg or box conaioing
nultiplc coateiocrs of thc sano wastc.
If r unstc retcriel has Do MIISI eod it
comt bo found in thc Hrzardous lI/astc
Erofilo Drtr Sptcn, m MSDS must
mEpooy thc westo. Contact Industdal
Ilygeoo fur e copy of thc natcrial's
MSDS.
PICKT'P CRITERIA
Pls thc nrstc on e llrzrrdou lV.stc
Dock, in r dcsigDdcd pellct iDGr.
Wr$o cofrim! thet arp Dot prcgcrld rg
dcrcsibcd rbovc will not bc pickd up by
Erzrrdous S/estc Pickug Crcs!.ESI'
Any contrim thrf b lcrting itr coatcolr
will oot bo pic&d up. Ary bry or box thet
@isovcffull
rod cromt bo tnorportod nfcly, will not bo
pi*cd ry.
IIAZARDOI It WASIr PROFrr x' n^TA
SilEM
GM-3.1
Isnrc No. Ul
2f SGp&mb€r Dql
wrcc will no longcr be foud il thc MIISI.
Gmrl wssu dfupcel instrustioDr.rE
fulDdtr GM 3.1. Speific ingtnrctionc for
thc dirposal of hazardouc uns3o ele fouad ia
6c Hazrrdous lllestc hofilc Dats Systcn.frir informrlion 3ystcm ig on thc VA)(
conFrtcr Dctu,o*. Ilerd Copies will bc
evrihblc to thosc disposcrs witout aoeasg
!o tho VAX.
INFORMa"TIONRETRIEVAL
IM'TRUCTTONS
Aoccrr !o thc Ilrzardous W.s!o Profilo Dele
Systcn docs not rcqufuc spccid uscr log on
idcotification. To gsitr.oeess !o tho
3ys!cE, using r VA)( tctuiogl, acccss thc
Nrnrrc clnsicr and catcr thc word
'WAS[E' rs tbo uscr idcotification. A
ncou will spc.r to assist thc usor.
EIT'IIDING SPECIFIC IIAZANDOUS
WASIE PROFILE DATA
Erc,h uort artl that gpocrara hazasdous
$rrno.will hrvo building plofilca that will
givc thc nnsto gcncrslor dl of thc
infotnetion loccss.ry !o disposc of spccific
wrsto 3[leEs.
ltcsc building profilcs will givc insruction
for tho consoli&tion of westcs ino dnrms
on thc hdldiag unstc dock. Thc building
speifrc profilcs will dc.l with proccsr
wutc dirposd, crsmple: disposal of rags
nrGd i! wiprng SF.sc offof parts usiag
rcthyl chlomfutu es e solvcot. Dispossl
inctsuctiou for stock nuubcrs thgt erc
blcodd with solvcotr, fillcrs, cts., arB
foiod in 6o boilding Ilezrrdou WsstG
Plofitc Ddr. Dlpord ingtrucioos for
co0oi[rtGd ur]sc, such rs re$ or
brurhcr, co bc foood h thc 'EdldiEg
Ef|3'Ilrzrrdour l[rsts Pmfilo DntrSyffi. CoffiEE[EericeroedItrrdedhr fur rdditiond
inbturdoD.
9.1
9.2
rs0,I
Imucdoar 61 tho direool of hrzerdouc
3t
GM-3.1
Issue No. ljl
2l Septcmbor 1992
93 MATERTALSI WIrfl MIXSI,
EAZANDOTXI WASIE TROFII,E DATA
Wrsto dispos.l infotuation for marcriab
with stock aumbcn eod MII$ numbcrcea
bc foud in thc 'MIillI'Ilazardous Wrsc
Profilo Datr Systcm.
t[Dror 3ta
9.1
ltir infurnrtion is for wastc thrt coosists
of only onc stoc& nunbcr th.t is esscntidly
pno. Dicposrl ingtucions for stoc'k
nrnbcrrrrgtc thet hrs bcco bleodcd, or
oontroinelod $,rstc ragg, cts., cao bo fouDd
il thc'EilCitg-bflg' Ilazrrdoug Waste
hoflcDc[. Systco. .Contrct EEffifor
rdditiond inf,otnation.
MXTXnIAUI WITII NO Mltril,
EAZANDOUIT WAS'IE PROFII,E DATA
W.stc dispc.l inf,orogtion for matcridc
wifiout stock nunbcrs or MIISI nunbcrs
cao bc found in thc 'NO MIISI' Hazsrdotts
ttrrsto Profilc Datr Systcm. Thb scction is
for thc disec.l of csscatidly puru nastc of
oD ty?c of meial. For blcndcd Datcrisls
or for comoiDrrcd ragt, brushcs, ctc.,
rcftE to tho 'ElilCil8$Qfilg' Ilazrrdous
ft*c hofile Dote Systcm. For additiooel
iofometioa, qrffict !@ ErrirearcatC
llsardore-tllrlr-
DISFOSAL OT' SPECII'IC WASTES|
AI'ID/ON. SPtr'CIFIC WASIE SiTREAIIIS
IO.I EMPTT OOITTAINERS
A cooriu6d hcld. hrz.rdoru Eatcdd
cen bc dilposd iato tho saoitery laodfill
only if it ir mpty and contains no 'ftcc
!g$&]. Ito RCRA &fioition of m cmPY
cooinct ic:
L All wrslc! hrvo ba rpmovcd thrt cao
bc rcoovcd using tho gactices
coooonly coploycd to tcnovc
olahlc ft,ou thst tyln of containcr,
o.3., pouring, punping, and
rrytuairy; AI{D,
b. No oors ltro I in. of rcsiduo rcmsin
or ttc booon of thc conoincr; AND,
g.If thc corrinct is lctt thra or cqu.I!o
tlO Snl in rizo, oo norp ttm
r}n,
GM.3.l
Bsuc No. Ul
2f SAtGmb€r DqZ
3 perccot by uteight of the totel
rycity of the coataincr re,oains i! tho
oo8iocr.
d. Conaincrs thu hcld rcutc hazardoug
$rrslo (P $,ir8ts, o.g., Cartoa
Disulfrdc, Nitmglyccrin, Sodiun
Azi&) nust bc triplc rinscd with a
sritrble solvcnt bcforp bcing disposod.
fho solvcat dnscc nrtst dso bc trc.tod
u e hrzardous ulastc.
RrftE to Scciion IV, Enpy Dnrms for
inrtnrctionr oa thc pick up of empty dnrns.
lOJ SOLYENT WASIE
10.2.1 Flanmablo Solvcnt Wastc
l. Ftennablc solvcnts art !o bo collcc.tcd
in thc *ort rrea ia eo epptopririo
ooDt iDGr. If tho $as!o is collcstod in
e nctd'conlaiDcr, thc coatgiDcf must
bo grouodcd. Whcocvcr the
flemmrble $asto is trarsfcmed or
cmprtcd from onc marl coataincr to
aoothcr mctal containcr, thc nctal
coilrincs nust bc grouadcd aod
crogs-bondcd.
b. Diftrent flamnablc solvcnts Ery b
conbincd, but pcrmission to mix aoY
ErEisb Eust first bc obtriaod from
EEffillh.t . R!ftrlo Hezardous Wsstc
hofilc Datr Systco (Building hofilc)
fur prcccsr spccific consoli&tions.
c.Flrmnrblc solvcots 6rt are
comniorrcd with o6ct nrtcridr, but
rG ctill liquid, mnrt bc dispoacd s I
huer&us wrEb. CoDt EinrtinS
ouielc ney chrrycthc
chrrectcriaics of tbc fleoorbb
rolvcd, so bc,forc dirpo3iDS of aoy
cootrniurcd frmneblc colvcot, refts
b ttc llrzrrdouc Wrslc Pmfilc Doe
10.
39
Syltco (Building Profilc) fur
inttrrcdos for th.t pertioilar unstofirrn. Contrct EIIST for additional
lnrilnctionr.
d. Wrsto lolid natcrhls thet rrc
sontrmin tod with flammablc solvcots
DodbG diseolcdrs e hezrndour
c,uc" ThL ircluda, but is not
linitcd to: tagl, prycr towcb, wi[,c3,j!ou, [n[rcE, slcocil boords, brushes,
rcmirebr certridscs. Whcvcr solid
relcdeb hrve bcco cxposod o
Ihmm$lo solvcot3 aod cal no longcr
bc ntry nsod, thcy Eust bc diryoscd
of rs e hrzsdotts rnstc. Difrcreot
sirslcr nry nood to bc disposod
scp.fndy. Rcftf !o tho llazardoug
W..ilc hofilc Drte systcn (Building
Ploflo) for ingtructiong for csch
nrticUr nrr0o sur.o. Coatrct
EIIW for dditionel instustions.
10.2.2 Nonflrnmeblc Solvcnt Wrstc
Nonf,enmablo solveots 8rc !o bc
collcacd in tho wort aia ia m
rym'pri.lc stccl containcr. Maay of
ttc oonflanmeblo solvcots erc
inoonprtiblc with tlic polycthylcnc
dnrn!, thcrpfore thcy should only bc
collcaed in stcl &nos. DitrGrat
rcn0umblosolvcotr Ery b
couUnod, hrt pcmission to mix any
nrtcrielc nrrgt first bo obteincd fron
EIIW. Rc&r o thc Ilezardous Westc
hofilc Datr Syctcm (Building Pmfilc)
fot p,roccsr speific consoli&tionr.
b. Nooflronrblo rohrcots that arc
comin tcd with o6cr orlcdals, btrt
rrt cill liquid, must bc disposcd of as
r hadour x,rr!c. ContrminetingnuLlr ney 6ragc thoctrruicdg of ltc oonflrnnablc
t[s!oa
GM€.I
Issuc No. tl
2l Septcnbc 1991
solvcot, so bcforc disposing of any
co[trDiollod nonflemneblc solvcot,
qrftr o thc llezrrdour Wastc ProfiIc
Dctr Sptcn (Buildiag hofilc) for
ingtrustion for thet partioilar nastc
s[Ean. Contact EII\I' for additiood
ingtructiong.
g.lll$tc solid Eatad& tbat atc
coDt Eildod with oonflrmmeblo
solvcots Eust bc disporcd of as e
hrzrdous $r8stc. Thig includcs, but is
mt limitcd !o: ng!, 1n1rct towels,
wipcs, glovcs, pqrcr, stcocil bosrds,
btusbcs. Whcocver solid marcrialg
hevc bccn cxposod to nonflamnrblc
solvcnts aod cao no longcr bc safcly
urod, they must bc dispecd of as e
hezrrdoug wrstc. Diffcrpnt wgt xr
nry nod to bG dispocd scponrcly,
reftr o the Iftzrdous lltasto Prrofilc
Dnne Sy*em (Buildiag hofilc) for
inrfrustions for cach porticular rrnsc
strcan. Contact EIIIV for additionel
inctuctions.
103 GREASE AND OIL
Most greaso and oil, thu has not bcca
co[trmiDricd with hazardous marcrials, is
rct hrzadous aad should bc disposcd rs
dacribod in Soction ltr, Paragraph 9.2.
To dacrnioc if thc nonmrtsnitrdGd gle sc
or oil is nonhrzrrdous, rcftr o thc
Hrzordous W.stc hofile Date Systcm or
oontlg3 EHS'.
10.3.1 ll/rsto gpasc or oil tbat is hezardow, ac
iodicatcd ia thc llazrrdous Wastc Profilo
Ih0r SFtcln, Dtrst be collcc,tcd in thc uottro ia en rppropdatc contrincr. Thc
collction contrincr must bc cnpticd every
*ortiry dey into en rcqrnuLtioa &un.
a.
0
Rcfcr o th6 r&rrdoru Wasto Prrofilc Date
Syrlco (Buildirg Pr,ofile) to dacruino
u,tich druu o smulelc nastG. Contrct
EI\[t for additional insmraions.
to.r.2 ftctc 8tr.!c or oil thrt has bcco
coatroior[od with hezrrdous ligi& nust
bo dispocod rr r b.ardous rvegtc. Tho
rrrgG Srprrc or oil mrut bc collcctod in
rglmpde couinctr in tho nrort rrce.ltc oomisr rrs to bc cmpncd otroo cvcry
*orting dey inlo snmulrtion dnrmr.
Rcfcr to thc llsdour Wastc hofile Drte
SlBtco (Suilditrg hofilc) for iofotuation
on lhe libclirS of westo dnrns. Contact
EIIII/ for rdditiooal infotuuion.
10.3.3 Solid r+nsto (rags, etc.) that he8 bcco
contrninrlcd with g1t.sc or oil nust bo
trcrld rs r brardolt8 nastc. Rcfcr o tho
Ilezrdour Wrsc hofilc Datr Syrtcm
(hilding Profite) for instnctiooc. EIIW
ory eufiorizc, in writing, difrcrcot dispos.l
oD l c.8o by crrc aoelysis.
WANN,NG
fucisc gnw arc to ruro nnx brcotnptiblc
noqials wlun cowolldoting oity rugs wil/zdw nwqbls.
10.3.4 ftsts dicsd rod ga! filtas must bc
dispmcdof in tho h.zesdons $asto rsg
&tmr. Itc filtcrs should bc placod on e
dtlin rack for et lcast Ab b prEvcot my
ftGo liqrdd fton accumulating in thc &uns.
10.3.5 Autonotive oil filtar E8y b disporcd s a
mnhrzrrdour srrto, pmvidod thrt thq,
brvc ba dtri$d.od do not contrin my
'frGc U$i,&'. Rcfcr !o Soction III,
Pngrryh 6.3 for instuctioor.
l0.a conRos[YB was'rE
10.4.1 Wrstc Aci&
{hta. Acidr, concdrlod or diluto^'-l codil no othcr hazrdou!
GM-3.1
Issllc No. liZ
2f Septcmbcr f99,1
chrnctcrisics E y bc scot to M-705
Wrsts lltrlct Trcatmcnt Facility for
urc in qrrlcr trcsEcot. A Hazardoug
Wastc Irbcl is not rcouirEd. dl thst is
occdcd is a Ilazard CommunicationI&.
NQfr.
Afr-nlant sitas srch as X-20. H-7.
Plottt III will ncd a shlooino neno
tTc-1ut.
lVrsto dodiac aod chrouic rcid nry
Dot bo usod diepeeoC h thb naotrcr.
Rsftr to thc llazardous Wsstc hofilc
Drte Systcm for speific inslnrstions.
Contact EIIW for furthcr inforoatioa.
b. {h.ac Aci& with a pH of lcss th.o 2
thrt rro not scnt to M-705 are
hrzrrdous, rnd ntrst bc disposcd es a
hrzrrdou $rrstc. Ilazardous westo
rci& rrc to be collcocd io an
rpp[oprirtc aonnctel containcr in the
wort rrce. ltc colletioa coatrincr is
b bG Gnilicd evcry urcrking &y ino
e polyahylcoc accumulgtion dnrm.
c.Uh.tc Aci& thu have a pII of grcalcr
thrs 2 aod hevc no othcr hazsrdous
drrestcristics may bo scot !o M-705
for usc itr $atcr tegtocot. Rcfcr to thc
Hrzrrdous Westc hofilc Dala Systcn
b daerninc if e specific acid ncr
Dry b tEC dhpe€cC in this Eantra.
d. *Jc Acid thal havc lo hezadoug
chrs.stlrirtics, o6cr thao pH, such as
rolvcog or hcevy mctrls, (c.g.,
Alodinc or Arostmng Strippcr) must
bc disposcd of rs a brzedous $asE.
Rc&E!o thc llrzardous Wasls ProfilcIb SFtcm !o dctctuinc if e spocificr[ unsto b hrzrrdous. Colloa thic
wros in u rppropritc nonmarl
cootris in tho wort rrca. Ttc
ollcaioo coDtriDcE nust bc cmpod
imo ra guuhtioa dnrn d lc.st
9[Slo.t
L
4t
orco clicry uro*irg day. Contact
EXISI for rdditional infornation.
c.Solid wrstc thd is contaminatcd with
ridr nuct bc disposcd of as a
hgrdour unsto. Collcct ecid
oontrninalod soli& in tho nnrt rrca
i[ ra.ppmpd.tc nonnaal contrincr.
Ttc colloaion contrim must bc
copld cvcry worting &y inlo a
polyettylcoc eosumulrtioa dnrn.
Rcftr to 6c Ilezardou $tsstc Pr,ofilch Systcn for additional
inst$cdog. Coil.st EIIIV for
additioml infutuation.
NOTB
Ary odd conupnitutdwastc tlnt bolbd ln a naal allqtbn conuiaer
nust havc a plantb lina.
10.4.2 W.stc B.!cr
Uh.a B.s6 (dkrli matccids),
onccotrrlod or dilute thst cootain no
othcr hrzrrdous charagtcristic Esy bc
scd b thc M-n)S Wastc War6
Trcrucot Fscility for uso in natcr
Uahcnt. Rdcr !o the llrzadous
Wrgte hofilc Daa systcn for spccific
iumgioos. Contrst EIIW for furthcr
infrrurtion.
b. Uhlc B.sca with a pH of grratcr th-n
t2.5 thrt src Dot scat !o M-705, rrc
hazrrdous ead nrst bc disposcd es a
hrzrdoru $,rsE. Ilrzadous nnstc
bscr rrc to bc collcstcd in an
tpptroprilto noonctrl ooatrincr in tho
sort rrtl Tho collcc'tioa coaainor is
!o bo qtid evcry mrting &y into
e polycdylm eunulaion &nu.
GM-3.1
Issue No. Ul
2f ScptcmbGr f9ql
c.{htr Boscs th.t havc r pH lcss thrn
12.5 rod havc no othcr hazardous
6rracncdsdcs Ery bo scor !o M-71)5
for uso in rrldcr trcafent. Rcfcr !o
thc Ilsrdous %stc Profilo Detr
Systco to vcrifr that a spccific'$restc
bccc mey bc gfd &F€.C h thi!
Eaorcf.
d. m.5lescg lhqt hrvc hrzrdoru
chanclaigtie, other rhrn pHl such as
colvcoa or heevy naals, (e.9.,
hydnzinc) Eust bo dispccd of as c
hrzrdous westc. Rcfcr to thc
Inrzedous WasE hofilc Date Systcn
to dctcrminc if a speific bssic $astc is
hezedous. Cootsst ElIl\I for
rdditional infornetion.
o.Solid westc rh{ is oontsniDdcd with
brrcr nrut bc disposcd rs e hazardous
wrstc. Collcct besic conaniorrcd
soli& in thc nort arca in an
ryFoprietc noomctgl coataincr. lto
collc'tioa containor must bc cnpicd
arcry *orting &y into an appropriatc
polyethylcnc acctmulatioa drum.
Rcfcr to thc Ilrzrrdous Wastc Plofilc
Dcr Systcm for additiooal
inrtuctions. Contrt EII\II for
rdditionel infotuation.
NOTE
fury basc conuminadwastc that is
collatd h a maol collcctbn contaho
nast lutv a pbstb lha.
10.5 WASTE PAINT
Mosa peintr usod on plent rrc e
hrzrdour wastc. Re&r o tho
Ilrzrrdour W.sile hofilc D.tr SFtco
for inbtnrtion on thc disposd of
rpeific pdos.
t
a.
Gro.t a
b. Mod p.iffi, *tco driod in tho
ooatlir, arc gtill hrz.dour $,utc.
If tto oortriocr docr mt Dcct tho
dcfinition of cmpty, (se Soction tr,
Ptrlsreph l0.l), thco it must bo
dhposcd rr r brzrrdous $ns!c. RcfcE
to ttc llrzrrdoug Wsstc hofilo D*e
ryclco for infrtnrtionoa spocificp.ifi. Drid FiDr c,hipc fton thc "cle-ning of sp,rey boothr should bc
onrklorcd hrz.rdou!, unlcss tbcrp is r
lrbor.tory aodysir to v6ify thc lack
of hezrdour netcrielr.
c.Solid $utc3 that arp coataminatod
with Fintr conteining hcary maals
us hrzrdO,us $lastc. llig ircludcs:
brurha, mllcrs, drop cloths, spey
boo6 filtcr!, slcocil bosrds, ragt, €tc.
d. hirrr thrt hrvo m hezsdous
chugistics, (conain ao hcary
EGE! , ac.) erg r aonhazerrdougwrro. Uquid nonhezudouspaiat
ntrt bG ecc offplur, but drid
Dohrz.rdour paint nay bc disp$cd
ilthc Infustrid Wrstc Trcoch. Solidouicb comoinrtcd with
onhrzrrdour painn ney bc Oisposcd
in thc In&utrhl V/estc trloch. Rcfcr
io tho llezrrdous }\Iasnc hofilc Dalr
Systro !o dctcrninc if e speific peiat
ir nonhrzrrdous.
10.6 SPRAY ON, AEROSOL CANSI
AIl sogol crns will bc colletod for off-
pleo disposel. All rcmgol cror nay bo
collcs'lcd rod/or concolidrtcd in tho samc
don.
10.6.l lJliulereref,r 55-d poly drum or ooatsircr
of 6c rppsopti.lc sizo fur Sc uount of
uoeol c.or &ocrd, ple thc sorol
cur ia thc aomir uldl ilb firtl, trking
cuc b Dot csocod ray rqulrtory tino
linilt.
GM-3.1
Is$c No. lil
2l Sepacmbcr f9ql
10.6.2 Ilezardoug Westc l$cb for acrosol cens
S.ll bc fillcd out as follours:
r. DOT Shipping Namo: WASTE
AEROSOI.sb. Ilzrd Clas$ 2.1c. RQ: (crvcbLot)d. IIN No.: t Nl95Oc. EPA Westc No.: D001, DOO?, D00E,
' D035#r*03#f. Accuulrrioa Strrt Drrc: (tbo dea
ntco tho first cen is phcod in thc
contrincr)
S. ERG No.: 12h. hofilc Stock No.: G5849(s
rpefrUc)i. Oocrgtor Fecao: (namc or badqc of
orcraror fillinq out labeD shn*;an)j. hrilding: (location of building
ScoctadnS the wastc/f1gggtr-el
ovcrtcad dcsictrstor/cost ccatcr) Rcfcr
to Aoocndix I for instructions.
10.6.3 lto DOff llrzard Class Irbcl shall bc,EI.AI\,TMABLE GAS"
IO.7 LIGIIT BI'IJTI
EFA rcgulstcs thc disposal of thc lead
soldcr in iDcsodcsccnt rnd fluoresccnt light
bulbo rs a hazerdous $astc. In addition o
lcrd, sonc tncs of lig[t bulbo mey conaia
hrardour lcvcls of ncrcury or other
rcgulstcd mctals.
WARNING
Fluorqccnt lieht bulbs out ofrnerctn
twrwhan rtct arc brokcn. PPEwirt a
raoirutoris rMd-
NO|ts
t'bthltgt t bt /Ds, sald ba n hdbghs,wttdvc iaoc*sor! bubs, crc. 0c
fushtdd.
10.7.1 For thc dbpos.l of wrrte $it bulbc oa
phm, pls thc spcnt bulb iD r comim for
tnryrotion. fro bor thrr thc rcw $[f
bolbr crnc in shouldbc dcqurlc.
,ETG'I 4t
GM-3.1
Issrc No. l.ll
2l Septanbcr 1991
Contriur forthc ligtt bulbs Dust bc
clocod uAco 6cy contein $astc light bulbs.
10.7.2 For thc tnospoc of rrastc ligbt bulbs off-
plrat, 6o cooiact must coDf,otD !o DOT
rquircncff for lcad coatradnrtcd wsstcxt.
10.7.3 Thc lLzudour W.stc Iebel shoutd bo
conplaod rr followr:
a. Dm Shiming Nanc: WASIEW
IIAZARDOUS SUBIYIAT{CES,
soIJD, N.O.S., (IEAD)b. ILzrd Clrss: 9c. RQ: @evc bLok)d. t N/NA No.: LIN307e. EPA Wrsto No.: D00t
,[S!O.g 4la
f. AEEtrLdm Strrt Date (tho datc
u,tco weste wrs frct put into thc
comrincgg. ERG No.: 3lh. Profilc/Stock No.: QlglllI{14i. ODcraor: (nemc or bedoc nunbcr of
mcrrtorfiltinq out labcD Fecanr
@j. Buildiry: QocetionofboildingScoadry@
dcrim.rorlcoet ccmcrl Rcfcr to
Amcndix I for insnuctions.
10.7.4 ltc DOf llrzrd Ctrss l$cl for nnsrc
liSht bulb. ir 'CIASS 9'.
10.7.5 Treorport tho nastc ligtr bulbc io thc
locetioa ufrcrr thcy eru o bc collcctcd for
ofi-plemdiryoed. W.rlc li3bt bulbc nry
mt bo storcd et locrtions which arp Dot
app,mvcd for hazrrdous rastc abngo.
10.7.6 Contra thc coordioator in eaeh srcs for thc
locetion of ttc Dcrrcst collcction srca:
IO.t BATTRIESI
Atl hcricr urod on plrot becono
hrzrrdour wuo rvhco 6cy rre disp$Gd.
fhcy oonoia nfficicat qurffltia oftardou ErEirb b rnrkc thdr bud.l itr
ludfllc erotiUrca.
G.[.{
GM-3.1
Isnrc No. Ul
2l Septembc 1991
NOB
TNs classtfuatbn includa bonqia frcm
f,oshllehg. mo*s. caladaton. oolooidfilnm&. ac.
f0.8.f Lc.d ecid bcticries, liquid eod gpl t)?a,
sru !o bo ta&co to thc M-501 Salvage Yard
forgdo b s relrincE.
10.t:2 All o6cr bcocdcr aE !o bc disposcd as e
hrz.dour mstc. ltc bencrics ar! !o bc
oollcctcd ia tbc wort arcas in m
rppropdatc plastic or plestic lincd
ooil.i[cr.
NO?E
Thc tqninal nust bc covod with taoc
bdorc oloche thant in rtc containo.
10.t.3 frc cootrincr is !o bc cmpficd daily ino rn
collcction mrrdrtiee coaAiacr. Thc
collcction Hilsl.tioe contriacr docs not
hrvc o Eca DOT requircmcots, but nut
bc ac.ld uficn wastc is nor bcing addd.
10.t.4 Tho Ilazadous $r8stc labcl should bo
oonplctcd as followt:
.. DOT Shipping Namc: WASTEW
IIAZARDOUS SUBSIAI\ICES,
soLID, N.O.S., (SILVER,
MERCT'RY, CADMII,'M)b. Ilrzrd Clasr: 9c. RQ: (crve bl.dc)d. IrNIN^ No.: UN3O77c. EPA WrstG No.: D009, D006, DOllf. AccunulUion Stsst fhtc: (thc detc
c,tco wrslo unr first plrccd iDlo thc
dtln)
S. ERG No.: 3lh. hofilc/Stock Nunbcr: G4s7OlllAi. Oocretor Femra: (nrnc or bedqc
mnbcrof oocrator fillinq out labcl Ctil*crn)j. Buildiry: Qocrtioa of buildia3
ScocruiDg thc *rrlqlE!e8g[9t
ortcrtced dcsimaot/cost ccnrcr) Rcfcr
O Aoradix I for insnuaions.
u
Arte Cmrdiaator Phonc
A:16 ,cff ILll 52t-z,90,
ftecport Timo6y Bamaon 55t4526
Pleil 3 MiLc SaoG 5X2-252r
Seeoc hrta Rogcrs 5X2-3T7
Stralcgic Corddl Cbriclcosco 5X2#t
Tcst Irrry King 5X2-tW2
x-?o Kco StruftE 551-5556
GM-3.1
Isore No. tl
2f Scptetnbcr Dql
10.t.5 lto DOf llsz.rd Ctess Irbd for rveste
bcncricr il 'CIASXI 9'.
10.t.6 Traosport tho nngtc bonaies to thc location
u,tcrc thcy uu !o be collcstcd forof-phot
dlrpor.l. Wrstc bcfrcrics Dry Dot bc storad
u locetioor u,tich rru Dot approvod for
h.zrrdou $rrste stongp
t:EtO.tL 4a
10.t.7 Comc thc coordinetor ir cach area for thc
locetion of thc Dcorcst colloction arce:
10.9 PROPEI.LATS PnEMrXr INERT
NOPELLAT{T AT{D PnETffi
CONTAMINATED WASTE
10.9.1 noecttrnt prcoix, thrt is still liErid, oust
bc thimd offplant o e disposcr. Rcfcr o
6c hrilding IIWPD for spocific labcling
inttructiors. Ctrcd propcllant prcDir,
witont any AP, crl bo seot to thc
Inendal Wastc Ticoch. Rcftr o Scction
III, 9.1, aod thc buildiag IIV/PD for
inrilnrstions.
10.9.2 Prcoix aod incrr orooellant Frheemrf***vipot thrt hevo ba
codninelcd with solvcott nust bc
dlposd ofrplrat. RGfu to thc btrildiag
IIWPD 6r spccific da.ib.
10.9.3 Prcoix or incrt oroocllaat co[trniDatcd
re3l, wilrccr In[Etr, phstic, ctc.,
coootoiralcd witt nG*U+efhofrmr
ethc-mremobh rolvcots f,eafrd
@DusSbcObpd otr-pleot for dirpocrl. Do mt nix
rolu.courinood ercoir n3r with
lluoimn goutOcr-contuioloa urrcto.
Ditpocc of crch scp.ntcly. Rc&r to thc
mdiDS IISTPD fur inrtructionr.
GM€.I
Issue No. Ul
21 Septonber 1992
IO.1O ALI'MINT'MFOWDER
l0.lO.f WastG }lemrtuiaetC duminun powdcr
thet has not bccn mixed with oxidizcr or' EiIl is to bc disposcd off-sia as a
hazardous wastc. Rcfer to Buildinq IIWPD
for Droocr di{nsel instnrctiotrs. eece*irC
*h
10.f0.2 Ahminum poudcr contrniDatod dry unstc
(rql, wipco, pspcr, plestic, ctc.) bd bo
di4oscd.s r h.z.rdou ur.stc. Rcftr to
hdlding IIWPD for firther instructiom.
10.10.3 DO NOT mir aluminum poudcr with
solvcng. DO NOT mir duminum powdcr
conrrmitretcd dry urastc witb solvcnt
contsEisdcd wastc. ltcsc wastcs Dust bc
dbposcd scpcratcly.
lO.lO.4 Rcfer to Scction III. Paraqraph 9.5 for thc
diroosal instrustions for sluninum nirod
with watcr.
f0.10.5 Alumioun @ntemin4cd rmrcr coaoining
diluto oonccotrations of aluninun nay bc
sGoa !o M-rcs for nastc u,rtff ttEstEeDt.
10.10.6 Rcftr to Scction I. Parasraoh 7.12 for thc
disoosal of oroocllant contgniaatcd or
oxidizcr conaminarcd duminum.
lO.lO.7 Rcfcr to Prrarraoh 10.9 of this scction for
thc dislosal of aluminun mixcd with rcsins
(omocllaat mmix).
IO.II DNAEGER, TT'BES
fO. t I .l Uscd Dramcr nrbcs nccd to bc taocd on thc
cnds erd dfuposcd of in thc res druns.
ArGs Coordinmr Phonc
A-16 ,cff ILll 52t-zl]fi
Frccpoc nnothy Bommn 55t4526'
Plmt 3 Mihc Saofi sx2-252r
Spocc hrtc Rogpn 5X2-t7ft
Stntcgic Cordcll Christcorca 1XL#t
Tcst hry Ifing st2-3w2
x-n tr(cn Stuffer 551-5556
Gn.'45
IO.1'I OXIDIZENS AND ORGANIC
TEROXIDESI
l0.12.r
GM-3.1
Issuc No. lll
2f S4tcmber f99l
of this rmsto to tnosport thc ngt€rial
ro A-2.
Traosport of this Estcrisl ovcr public
rco& rcquir€s a menifcst, ovcr 1,0(X)
lb rcqrdrcs placading.
Wasts Ammonium Ferchloratc (AP)
-.!d AP controinrtcd unstc b to bc
diryolcd rs decribcd in Soc{ion I,
Drra3raph 7.13.
NO7ts
UnemmdAP tlw is contottinarldts
to bc dlswd of as an oilhcr. Class
5,L
Excctn for qmund AP and thc
oildizcm listcd in 10.13. wasa
oxidizcrs arc o bc dismsed ofrolant
as r hazardous nastc. All rrasto
oxidizcrs nust bc labclcd with DOf
Ilezrrd Class kbcl. 'CLASS 5.1 -
OKDIZER.'. remrdless of containcr
!iur.
Wroo Orgrnic Pemxidca arc to bo
diry$Gd rs r hrzrrdous unstc. Refcr
!o 6o IilYPD for speific label
iutsnctiou. All nnstc organic
paoridcs must bc labclcd with a DOf
Ilzrsd Ch$ Ilbel, 'CI-A,SS 5.2 -
ORGAI.IIC PEROTflDES', regardlcss
of conrrincr sizc. All naso oridizcrs
nun bc hbelod with DOT llrzesd
CLrl Ilbd, 'CIASS 5.1 .
OXIDIZER', regardlcss of conuincr
fuD.
OTIIEN, OXIDIZENS
Souo crocsg oxidizcr Datcrids can bc
urod u ftrtilizcr. ldrrcrids thet can
bc diryosd ir thfu rrry ar!:
llodiun Mtdc
Foturiun NitrlE
AononiunNitnta
For dirpos.l of ttc rbovc nrtcthb,ffit OfEco Scrviccs at Ert 3337.
It L 6c reqonribility of 6c SpocratoE
10.13.3
to.r2.2
to.t2.3
10.13
l0.13.l
ro.rt.2
10.13.4 Regr, wipco, glovcs, Gic., rhrt g1o
cont nirstcd with thesc oxidizcr: arc
!o bo dbposcd according !o thc
dircctiotrs in Soction I, Prragmph
7.13.1. Consult IIWPD shca for
labeling informerion.
10.14 MT'LTIPART STOCK NT'MBER
MATERIAIS
Stock uumbcr natcrials thu coosist of nole
then sss prrt, such al two pen adhcsivos or
two pctt painrs, Eust hsve 6cir scperato
p.sts dicposcd gcporatcty. Rcfcr o tho
Ilrzrdous ll/astc Profle Data systcm for
ingtnctions on thc disposd of cach part aod
nixd natcrids.
IO.I5 I.EAI) SOLDER
All lcad soldcr from cithcr wclding or hand
soldcring opcrations is e regulatod
hazadous wrstc.
l0.l5.l Whcn lced sol&r scrap is placcd on a
sstcllito or 90day nastc dock, it must bc
in e DOT approvcd conteiacr.
t0.15.2 Inrzardous Wastc Irbcls for lcad sol&r
sh.ll bc complacd as follows:
.. DOT Shipping Namc: WASTEW
IIAZARDOUS ST'BSIAI.ICES,
soIJD, N.O.S., (IEAD)b. Ilr.sd Class: 9c. RQ: (cavo blrok)d. LTNINA No.: [IMX[7c. EPA Wasto No.: Dfl)8f. AccrEuldion Strfi llale: (thc dalo
u,tco rvrrtc rrlr firct plecod in thc
contrincr)g. ERGNo: 3l
r$rcal 6
GM-3.1
Issue No. 12
21 Septolnber f992
h. Ee8lctsto* No.: GIEIEi. QD@gQt Ferao: (nenc Af-tECgg
nunbcr of oocrator fillinp out labcl Cclift*lrm)j. Building: (location of building
8coctetitrg@
dBirpdor/cost ccntclr) Rcfcr to
AlEEndix I for instrustions. ..
10.f53 fho DOf lLz.sd Chss l$cl for lcod
coldcr i! 'CIAllS 9'.
relca 46a
10.16 PEOT(rcRAIErc CHEIIilICALSI
X-ny frciliticc rnd/or photo labo u,tich'
SpoGdo le4o anounts of photographic
chcoic.b urtich contrin silvcr must bulk
thqn im 6xcc (forfixcr solutioor) or
davclopcr (for dovclopcr solutions) holdiag
trob. Urct building penonncl Eust q|l .
Dd., E,cs7l2)455,to hrvc thcm
Freodby Hezrrdous U/estc Ptcluo
CIE! ESt uftco t-nkr arc wi6in t hr of
trdng ftll. ltir can bc rooonplishcd by
scrirs &c holding trnk alrso scosos or
li&t rt e lcrcl so th.t it will go on t hr
bc,forp thc trok will bcconc firll.
10.17 WASIE XSOETANAIE
DREPANATION
WARNINIT
Isoclonaa QPDI, ODI, ac.) 0c wry
hagfuus. Do notbralttclurnr or allav
tluno r"plttu bt contut wirt ski* As a
,rnln tnlrlznt tlv prupq rapirur at d rubbc"pradw clrdtttrg mst bc wont vlwt
dalitrg r*frh rttc ,mtetol @rsult thc
owogriac MHSI fo pavnal potabn
blfunJ. Do na nb dffocnt typa of
tsuyruu.
l0.l7.l lVhcocvcr possiblo, usc originel oontainer
ot 5gl cerboy fot disposel of sndl
.Dorutr of isocyaolcs 8Dd DO|f l7E 55-
grl drunl fot leep snouotl.
VANNING
Isayuaa 0c *arq rcrr,tiva Whotaq
a lrrwigt ulcorunna is usdfor
dftprsallt ttrrrtt bc dtM b antrpc rot@ls Faa*
NOTR
llqQinolotubw ts na usd, a clant,wd,IDT IlE srd drun mst bcedrdttil &GB aid vlilolly ttttpd
ft bagc, frtwbq aad DOT stotg oafuirywc usc (scc Figwc 3).
GM-3.1
Issue No. 12
2l Septembc 1991
l0.l7.2 Complac e Ilazrrdous Westo kbcl (Forn
TC Tltlt) with dl applicablo inforuetion(c ^{ppeodix t). Pte g Poisoa llszad
CLss Irbcl on lhc conainpr ocxt to thc
Hrzrdous Wrsto l$ef. Afr.ch thc labclg
to tbo uglcr onc-third of thc drum. Thc
proper senteincn Eust trot bc corrodcd rnd
c.lnot conoin rcsidual chcmicals. (Rcfcr
to Ffuure 3 for &um inspclion critcrie.)
10.17.3 Dndng rdditiong of westc o thc 55gl
dntn, irstrll m Envir,onncntrl Wasta
Olceos.l-rpproycd fillcr slnut (such ar
hotetoaal S5l0) which contrins e
urerfhcr flep or hood thet closcs
oltonrtic.lly !o prcyent raia or snow fron
cdcriog thc &un.
WANNINI.,
Awid horrdling isocyuuta and do rcl mix
d$aat typa of isoryamtcs llnlass
bntwdby EIIVI.
l0.l7.4 Ensulc thc cotrtct \l+in. bung plug and
3rr&a rro in plroc aod tighancd aficr
rdding boc,yttr$ca to thc drun to enlurt r
ti8tt, nonlcrking scal.
10.17.5 lto &uu Eust hsvc rt lcast e 6in. hced
sp.oc to ellow for crpaosion of tho liquid.
10.17.6 Ptrcc on aa apprcved uastc dock aod
ootrct llazardous Waso Plcluo Crqr,:
EXilII to pic& up thc narcrial.
IO.lt RESPTRATORCARTRII'GES
All rcspirlor certridges ttsod on plent will
bc considcmd hez.rdou nrr*o whco tbcy
uc dilposcd. Thcy coutrin cuffisicot
gendticr of hezrrdour E lcrids !o E ko
tldr buri.l in lendflls prohibitod.
lO.lt.l Thc crrtridfp rro !o bc g8g!90i[-Sesg
@E!.
rel.,(,
NOTts
All cotrillga tho ot ontontttdwiih
AP, NG, HMX, ot uE dw ptWdlott
nutaial will orntttntc b bc sait o M-136,
hafiry gor.t ds. (R{a o 8&n I.
LIW It AIERIAL PREPAMflOT.
l$lt'3 TLc eeil^'-rr -xt bc'g!t c'errd GtcGpt@
l+ls*.1+o.eet*rc,
eeaeUoa.r.ene*rt
wWWrc@#@ffi
@@Cr.-*S+e,a+tw@trm)
prf4-*s.)
'0'lt'5 Fc DOT I'^-{ 9m'rH fer rvrr
@
Mbrr
I
GM€.I
Igsttc No. 1:l
2f Scptcmbcr f99l
10.19 SOLMINENT
PNOTEI,LANT WASIE
Ist p,mpcllem clcenup regl, wipcs, Inlrcr,phrlic, ctc., contaniuicd with ncthyl
eiloroforn or othcr nonflrnnrblc rclvcmr
fton finel rinring of bowl rodor tooliag.
10.19.1 Rrgr, wipcs, p.pcr, phstic, ctc.,
contrining ncnhyl chorofttu or othcr
nonflennrblcsolvcotr tud !o clcrn up '
ist propdlrotontrninetcd looliag nust
bo shifd ofr-plrat for dispocel. Thc rrys
Ery b collectcd in ra rpp,tovcd cootriocr
in ttc *ort rrce. At thc cod of crch
opqrtilg shift, thc coilsntl Erl3t bc
tnosfcrrld to e DOT poly drun (Figurc O
loc.ld on tbc building hezadou unsto
doc&.
10.f9.2 Tho rrce oollcc-tion cont iacrs nust hrvc r
Ilzrd CLss 9Irbcl on thcm. hbcl nust
bc visiblo et dl tincs. frc arce collcstion
oofrilcrs do not nocd r Hazrrdous Wrstc
I$Gl. Tho containcr E y b lhcd with
plrstic or vclogtrt.
10.19.3 ltc ac$Euladon &un oa tho building
hrurdou $astc doc& must bc htDdtd
rccording to Scction tr, hngraphs 7.1o
7.t. Rcftr o tho building IIll/PD for
instilcrioos on complaing Hezardous
W.!ilc hbd.
11. WASTE ACCI'MT'LATION AREAS
NOTR
lf drip Elsys 0c ttsd ht wasu
wututlfun arrall, tluy tttttst bc bspatd
atd W dt!. Dd?t ntttst bc cla td up
whrrl, fuqtd"
NINETY.DAY IIAZARDOI'II WASIE
IITORAGE AREAS
ltb proccdno providca inrtnrction for
&.iSDrtcd 90.dey h.u{dous n'rrta stonSg
,D[,'},47a
11.1
rrc.r. 56 Tablo I for r listing of
provod Xldey storese friliticc.
NOTB
fuagcir rbnird to 90daysfrottttluutefun stnt dac, n*idt b t p dasc*latnqtul fsftrt pbd ho a
ou&w.
It lr reonncodod thrt buildingr
Scoctdry norp thra 55-8el of hazrrdoru
u,rdc wi6ir Zl hr hevc r 90day stotrgp
rrt. ltrltr. Buildinp E y oonvctt frcn e
sJcllito ecgnnulrtion rree by coatrctingW
ErF4il48. A ncaiog nust bc sct up to
dcfiD thc purpoeo of thc plemcd stongc
rrce. To clorc EPA rcgulalcd rrasto, tho
followiog rcqulrcom Eust bc satisfiod:
r" A! udit mutbc conplacd onthc
pmpocd arc. to d€tciminc conpliare
u,ith 4() CFR26lt, Subprt C,
'Plcercanc$ eod Pratootioo'. fris
udit cro bc achduld by coatraiagETUffi*xnrsi!4s
b. Tho llezrrdoug $/as!c ltrfroagcmcot
CondngeocyIho ed GM-3.1 mst
bc @td to rcflct thc cheoge in
c&uofthoerea Conra!flf
Ertrlt48 !o upd.tc thc Contingency
Plro.od GM-3.1.
c. Itc lilt of colid tr1316 mrnrgenrcot
udb (SWMU) il'tr bc upderod ro
rtdd tho rcw Xl.dey stongp lretComWe }Iroryemarod
Esviromcol Scwicer rt Ext 5390to
hrrc tho SWMU lfut updelod.
d" Pemmd urint 1ho 9Gdey storryo
uoil nur bc Edtrod ia thc followiry:
. tryccOouo Ltrbt. mrnr
GM€.I
Issuc No. Ul
2l Septea$c l99l
Contrct Environncnul Ilezardour
Wlrlc et Ext 41l$a lrzngp for thir
ttrining.
Aftcr thc'rcquiremcotr hrvc bco s.dsfid,l EGoo will bo isrud strtiag tha thc 9G,
&y atorrye arcl cr! bc uscd.
11.1.1 Wcc&ly Hazrdous Wrctc Slongc
Upocton
Ecrsonncl in dl9odey hszadortr nrdc
rtorrgp frciliticc urut pcrfotu a wcc&ly
dosuncoficd inspcstion of thc hazardour
rrrrslo storagc arce. Tto pcrsoo pcrforning
tbc iorpoctiotr Eust chek o assure thrt:
l. Hezerdous rrastc contdu! aro lrbclcd
eod nr*d propcrly as aotcd ia Teblc
IV 8rd Appcodk I.
b. Coilsincn arc in acccpteblc conditiong notod ia Ffuurc 3.
c. Oood housckccpiag p,ncticcc aro tdng
follourcd. Thir iocludcc propcc
grounding, ioconpatiblcc scpcalGd,
rod rrce clcaood 8!d frcG fton dcbdr
lod 3pilld natctid.
d. All fttll costrincrs must be movod g
quickly rs possiblc to M-lt6 to contc
ra cYGo flow of naste tbrougb tbc
mcility. No &uns nay bc k@
bcyond thc 90-dey stongc limit.
o. lto tinc rod thc drrc of thc inspoaion
ir rurdcd.
ll.l.2 Thc Ilezrrdour Wrno Slorrys Coltriu
trycsOor Cbcclilfut (ForD TC 8(Bl, Ratr.ll{t, Figurc O mlct bc urcd utco
pc*nniry rl iDspdim. Innodilcly
ooffi roy isrcsuLridcr or dilcrcp.ocict
.od Dtc oa ttc forn how 6cy wau
aon6od. Scod e oopy of thc coupbcd
ead rtpod foru o WrrE l[rnrgeocoud
rena tA
tt3
ll.2.l
tt.2.2
Eryircmcoel Sctrvica, ItlTS 3Ol. Thqr
will to4 thc form for6c rcqdrcd thrcc
ycrll.
SAIEI.LXrE EAZARI'OUII WASIE
AOCI'IilI'IJ\TION AREAII
S6 Trblc I ftr lising of rpp,mved Srrc[itcAmuldon Fsilitica.
Sdrllilo snuhdon rrrrs do Dot rlquirc
urcctly'domcotod inryoc-tiou but nust
bc nrintdaod er in Pang[eh ll.l.la-c.
ts mdntrin e srfcllitc stltrls, thc buildiag
Dut oot hrrc rnouro of hezmdorur wrstc
Gqud !o or c*cocding 55-gd totrl for
loryrrttro 72 hr et e tinc. Ptcknp of firlldrlo mrrt bo withh 72 hr by Hezadous
Wlgtc Plckrp Crgw:. lgSegi+ecOfa+aeertr@
GM-3.1
Is$rG No. lil
2f S4acmbcr f9ql
ll.l.2 It is teonocodcd tbet thc owDcr or
opaur mrintrin rislo spccc (4() CFR
2il.t5) !o dlow thc umbcmncd
DovGocot of pcrsonncl, firc protetion
oquipmcot, spill contrcl cquipncot, erd
dmmnination cquipncntto ray arcl or
ficility opaetion in m cmcrycocy, ualcsl
eirlo sp.co ir not nocdod for aay ofthcso
POIPOEC..
11.3.3 Ado$rtc li$tiag Eust bc providcd fron
ci6cr tho G:ds[ES buildiag, arer lightlng,
or by ligtting pmvidcd insidc thc shcd.
11.3.4 tightaing and gtrlic protcctioa Eust bc
Fovidd es rcquircd by NFPA.od AFR
9143.
11.3.5 A[ $ns!c nrtcrids nust bc honsod withir
r thresidcd, covertd building. Tho opco
d& of tho covcrrd hlildirS Enst facc
r*ey fmn tbo gua. (Aa opcuing on thc
aorth si& will not frcc tho sua.)
fro floor stilcoltr of eoc,h dock nust bo
rblo to support thc narinum conbincd
wdSLt of rll unslcs pleood on it rt eny
givco tino plu my hudlisg
nlGd to movc thrt $rr$c.
u.3.6 Acocss !o docb nust provi& e sa& aoday Ecrar of rpprooch. It is csscatiel thet
hrz.dr e$ocirtcd with b.clchg eithcr bo
clininetcd or coilrcllod. Doct
coordinrtotr Eust oontrct Eovimnncorrl
Qrcrations, H 4248 for hrzrrdou westc
docb rod Exr l}t{ 5905 for prcpcllrat
u,@ docb, for sgistrocc h dcvelqiag
rcocpt bb dtcrnetivcr u,tich oofiol
b.ctsry h.adr.
11.3.7 Imnprtiblo Dei& nust bc rcp.ntod
ton othct ucrieb or prctcaod frou
ttco by Eo of r di&c, bcru, wrll, or
ottcr dcvicG.
ll.3.t Coatrinncm 3hould bo p,rovidod u,tich wi[
coeol uy ryillr of rshb pLcod ird&
lho $Gd.
tt.2.l All hrzudour uruto ooltrinctl pleccd in
ddlilc enuletion .rprs nust hevc thc
ttrldlitc lbrdouc Wsso kbel (Forn TCtl$) rld Oc ryp,rcpdrto DOT llzrd
Ct .r bbd on thco.
U3 WASTE IIOCK CRITERIA
N(N'B
An dbrt o stanMEc all rwrstc d& lrar
ptaltgtd rte hcbsbn ol tlu followingtr{ontAn h ordq o give.uso
ogu&ubr tirrr to budga and Wanatdwqa.
u3.l All do& Eui bo sitcd by tho rpp,ropriato
rdority rod rh.ll diephy dl Equircd
idcodfcdm infrrnrtion such r bry
lioilr, crplcivc rynbob, .od tnodcot
lioilt.
Wo UofocoedEavimucol
Scviccr nurr rcvicrw rod sigrofrdl plror
forguo docb.
reloa 49
GM-3.1
IssuG No. lil
2f Scptcmber f9ql
It L ronncodod thrt contrinncof
povidcl e low ryot or snall srnp!o
cootrh ud dlow for cary rcmovrl of
spilld nlcrid.
11.3.9 It b reonncodcd 6rr dl ftcilitiec bo
Gqrippd (4() CFR 29.12) with 6c
followiry, uolccr norc of tho hrzirdt
poeod by wrsb hrndld rt thc frcility
coold rcquir! e prrtioder kind of
cquipmcm eocifid bclow:
l" A[ idcfa.l oonnunicgtiou or deturyrh cepblc of providiag inndi.to
cocrseoqy instnrc-tiou (voicc or
dSDrl) to ficility peaonnd.
b. Adcvicc, such s rtclcphono
(inncArtcty evrileblo et ttc sccoc of
opcretiou) or r hrod-hdd, t*o-wly
ndo, cqcblc of snononing
cocsseory essist re ftom locel polico
dcp.rtrrcat, firc @nucot, or Stroc
or locd cmcrg@y responsc tc.Dt.
c. Eocrblc fire cxtinguishcrr, firo oontrol
oqnipocot (inshding seccid
csdryuishitrg oquipmcot, sucb ac thrt
udrg forn, incrt grr, or &y
chcoicrb), spill oomol oquipncot,
rDd deoatrniorion cquipmcot.
d. Wrraet dcqudo volunceod
pirlmtG to supply nnlcr hocc 3tt!ens,
foru-produciag cquipmcot, urlonrtic
rprin&lcn, ot urttcE sPrry systcmr.
9ASn 50
SECTION rII - OTHEn WASrE
PREPARATION
1. INTRODUCTION
TLir acctim ptvvidcr ioctructioD! on: (l)
prGp.rilS RCRAdcfild mohrzrrdouc
srrlg Erla;ds for dirpocd h rhc M-336A
Sroitery Irulfill or thc M-l36 rndusuful
W.rtc Trmcho, (2) pmpntion of poly- :
&lciartcd biphcayl- (PC, couEi!.tcd
utuidr fur ofrahr diseod et M-186, (3)
dbeoo.l of ubcrto.conteninrtod itoor io
6c ubcrrcr hochcr $ M-336A, (4) rvua
oil dbpo..l ftoE M-186, (5) rccovcty of
rlvryo$lc ieor, .!d (O mn{rzrsdoul
*retc dispol frcm slallitc pleotr ruch rsHr.od X-20.
NO1tsn dy atadprizcdfu esrrtral6
tufr triol solidtnstc. @wban, od aserr;tos itans is th. M-336A
WlotdliL, ild the only aru
ulor*zctt for dil1aural $ nafuirAus
drllltnd walrtes iE dtc M-136 lrrdtlrt ial
Wastc ftadr. LoSUing olicc liqnds isafwbifutpoaie.
NOTBh*uda deffis gcnctd.d by a atmmn
Dulrlt b scgtotoud yior to tfrspol at tlu
M-336A tudtary lardill Saltagc&lcnal nut b tokst to tlp E-SOI &lwgcfud. futwl3alblc rlrudnust b tatan to
rt. M-ln Sobvlge fad. AA lds rrurt be
itllpc*a by &yirunatol Waste Dispaml
pcrsana d M-IEI pior to dspaal at M-fieL huws oEqdpn nt argbucrs
Iwn Snurrgic Aecntlas nuut cont&
citlur slraegic RedE ard Gruntds o, Eiffiil, Pago 100, q EWD for fu*udas6 @ Sanoae debis. @atrudors* Farilidcs aqinenfian fiae
Opcnmas a#*atrrl rnlJt oalrtart
dd,ct 8W Oplrorlas R@de od Gruuds
d Ei N\ Pago 129, or E|WD fwbtrcudo 6AENI {nuac dMl
hcrcte 6s vill na b dspacd $atd, U-$A &liwy Lqtfirl
GM-3.1
Issue No. ljl
2l Septanbcr 1992
. NOTE
Iilokfing pcrcauul nalst irl,srialre sdrv
,ndtd $nuurid hspccdott $,nhqgrhlJ wanu prior to pbaunt ot
anqpruvcdwastc d& orina bin o
anJtir,c @nvdprcFndon pruccdures luvc
balollowcd
WANNING
Alfia.th PC&<onnfitud dl arrd
asbstos arc nd dclned by RCRI as
,rgrrda.J rrtorfi4r, they aru ngfutcd by
EPA t rda IACA ard tlp Clean Air Aa and
nay dlcncty Sca fuorut tpalrt or tlu
ctwituutstt.
1.1 LAEEIING REQITTREME!{TS
All rohrzrrdorc wrstcs cuch rs wutc oil,
gbcgtoo-rchtcd itcmt, PCB-rcletcd itoms,
crrtoo, ed rcnhrasrdoru chomicel w.rtat
illcDdGd for pichrp by M-136 or M-lt6
direosd crws Etrst bo eccomponicd by eo
.trchcd Wrsto lrbcl (Foru TC 8125). Scc
Appcodix I for iostructions oa how to fill
ou lhc \lrrrtc lrbol. Complotc tho \Verrc
IJbcl iD ite cntircty witb e Buany's Mireclc
ho or oquivdont.
12 EIIITR,Y RESTRICTIONS
t.2.t Eotry iDto thc M-336A Ssnitrry kodfill is
rtrtrietcd. Irodfill houn erc 1300 ro 1500,
Moodey througt Fri&y. Eotry oey bo
ind by coatecting EltD pcrsoorcl et
M-381 dudng thcso opoa tiocs. Eatry rt
o6or tiocr ir dopcndent oa pcrsonrl
eveilrbility. A oomber of tho M-136
dirpo..l crar should .cconpsay pcrroorl
cdcfiog tho ercr end, u a minimurm
, Eust porrondly irpcct dl
lcdr to colurc uuutborizod itcu rro rct
pm.cof. Mircollercoru'propcrty' itcor
arci u hrgc motor c.!or Du$ bo
rcconpaicd by propcr disposd
docnooatrtioa. Furthcr infomrtiot Ery b
obrrird by coatuiog EIVD druing &y
fiift, Mo&y throuS Fri&y.
re..Jr 5l
t.2.2 Eotry into th. M-l36IDdustrirl Wrs6
Trclch b rtstdctd io M-136 or M-186 ersr
ecno@l only. Iootructioot for dispoeel of
oonhrzrrdon chcnic.l wutal in tho M-136
Indurrid \lrrsb TrcoA rrc found in tbo
EWPD.d irthir Scction.
2. DETTNITI]ONS
Asbcaaa - EitbGr of nro nonconbrutiblc, :
chcuicrl-rcrirtru, fibtorr niocnl fotus of
iryttrl r'Smtiurn riliceO uscd for
firproofiry, clcctricel inruletion, buildi4g
nrtcrhb, 16$ liaingr, .Dd chGEicrl
filtcn. Arbcrta tbet cnroblcs crsily or thrt
cro bc prltGrizd or rpduccd to e ponr&r
uDdcr hrDd prGrnrc ir cellod frieblo
rrbcrtor. Arbatoo tht ct"*.t bc oerily
cntoblcd udcr hrod prtssurc is c.llcd ma-
frirblc ubcrOe. Arbcctoc is I rcguletcd
cnb.trm undcr Subp.rt B, Netioul
Euirrion Strod.d for Asbcstoa, of tho
OcraAir Aa.
Asbc3ft fhoch - A hdfill tEEch
ryocificelly &rg for burid of proporly
ooatdoorizcd ubortoc end rsbostosoffiEirbd or rcletcd itcnr. ltcac
tmochG. rrc locrtcd.t thc M-336A StDitry
Wlrtc lJodfill.
A3D6aos Wlsa! Sblpmt Rccord CfCtl7, - A rtcosd which mut rccoryoy rll
rhipmoff of ubcclos-contrninrtGd unso
E ledrb on prblic ro.ds to thc qin pleat
frr dLpo..l ia thc erbcstos tneochoe et thc
M-336A S.dtrry lrulfill. Thc rccord
&cuacnlr dl tnorftn of ctatody of thc
rrbcror-omuirtcd w.$c fFoE thG tinc it
lcrrcr 6c amrtor trodl it ir fiarlly pLccd
iD thc M-336A Sroitrry Irodfill Asboloo
Tructc..
hlldqrAra ncfcscotrdrc - el
bdld!C.sG.. x,tich brvc ra epprovcd
doct fun&p of rrac nllcridt nurt
hrvo e dGdtrbd rterr*unvc. Ttitqrolotru ir r.rgpd by nfcrvirioo O
b. 6. cdct pcro(r) for oeoct
cilccd3 wc di4cd ud/or Wub
Dirpo..l Ndioc. (Fco TC 8124).
q[$a-n
GIt[-3.1
Iscuc No. tl
21 Sqtombcr f9q!
Thir rcprcrcatetivc is rcrporiblc for rhc
tirely rprolution of proccdurel
Arcrcpcoclcc. It ir thc rcoponribility of
crcf luildiry/rrcr to iabru
Ewidoncatel Wrstc Dispocel of thcr@e) of thcir currsaa rrprcscarrtivc(3).
Enpty DruD (contdncr) - A conreiocr ir
cryty if:
l.All u,rctc tbrt cra bc rpoovcd her bcoa
rrrct Gd uing pmcticcr nrch rr
pouriDg, punpirg or upiretiag, AND,
b. No norc th.o I ia. of rpddua lpmrinr
oa thc booom of tho coateirr or irerlirr, AND,
c.No oorc thrul3 pcrccna by wcigbt of
th. totrl crpcity of thc co"triocr
rrmri[..
NOIE
A dnonis NOT anpty if ory olottnt of
liqdd a n bc pottttd ott or lvard sbUng
amord dra tlo drunis sfun
Enpty Dnrm (contrlncr) - A cootdnor ir
cEpty by DOT dofiaitioo if it hrs bGGa
'clo.Dcd lnd purged of ell uiduc' of e
prwiouly hcld hrzrrdous metcriel, 49 CFR
l7l.2e(e)(l)(i).
NOI'E
lf a drunfin& prcvi*sly lpld alraarblt
natcial is ra clanud od pwgcd $dlruifu prior o bcing $ercdfor
ttuttpotanion ot pdlic higlways, t re drton
lrlnrr b rrrarfrd 'R.sidt Last btabud'
(otitttul lwttfus flstcrW esoipdol
0d b acotrydcd by shippdng WCn.
52
WANNTNG
lf rtc cantdner hars lpW a vmrsu idadfud
as an ette hoshts xlartc by A.8 EPA,b n dsWG firns M&iru". @r08c
narta, arcibdficdinthc MH&.) llu
culunurrru.* b rtfu fiscdWrcdswlwirtrtc rbsu ttatedas alwtrfuswn.
codri! rc hrardour conrtitru or fr.,oo
liqui& .rl to bc hnid i! thc M-136
I!&rtrirl Wstc Troochcr ia rccordroco
withlhc IIWPD. Exloplos ero curpd nro-
F t GPoI!, lGJilt' plgti6, ctrGd lirr
odcrid, rd dcriccrotr ruch rs thocc found
h AP EcoDO-BiB 8Dd RMC'g.
Itrdttsd.t Wrstc Trcnch - A hDdfll trcach
locrtGd rt thc M-136 rrcr, dug spocificrlly
for hrid of chcoicd wutG. rh"t contrin rc
h.zrdour cotiocntr u froc liquids.
Uqutd -TbEPA &fisr e li4rid er I
nrtcirl futwiU pr thrcqb la epp,rovcdpril filtcr (re Appcodix ltr).
Noo'lgilOal ltrstc - Ary colid lmstc th.t
doG. Dt ill uo&r ery Eaviroorcotel
Probaim Agpocy (EPA), Doprrtncnt of
Trrrportrtim (DOI), Toxic Subeteocc
Cootrol Ac (niCA), Netioarl Erniscion
Sbodrrdr frr &c Ilrzrrdour Air Folluteots
(NESIIAP), Fdcnd lorcctici&, Fuogisid!,
Rodcicidc Act 6IFRA), orOcoryciood
S.Sty .od EG.l6 Adniaistntioo (OSHA)
quletioo u e brzrrdour chbEic.l,
EaEhl, dCru or wrsb.
Ptolyctlorbrtcd Elphctryl (FCB) - Ary
ch.oicd n$trca or coobiortioa oftrE ([Di!d !o thc biphcoyl uoloorlc)
trthrvc ba dloriamd to vrryin3
dcarGa. h thc Frt, PICB rrco.ddd iDvrryfuclio bro@hy&ulic
db rd dolcclric @Lil oib ia clcctricelEdran, crFcioo, rwitcL 3cro, rod
b.lt o b iffi thc phpicd brcr&dml of
6c d. FCE l.rt Drv ruauletcd uadff 6c
Tcie b Codd Act (ISCA).
GM-3.1
Issue No. ljl
2l Septanbcr l99l
TSCA rcgubtct PCB io thrcc crtcgorio: (l)
thflc withlcrc thra 50 prtc pcr nfioo
(po) cooccotntion, (2) thoso with 50 to
499 ppm corentrrtioa, rod (3) thooc with
500 ppm or grrSor concootrstion.
Folymlzrtton - A chcricd rcrction,
uanlly c.rricd out wi6 r cetrly$, hcrt or
li$t, iavhich e lerge aunbcr of rcletivcly
rirylc rclcculor combim !o form r lergo
chri&li&c nologlilo.
Sdts? r rndllll - A locrtion for
phccmoat rod hrrid of oonhrzrrdoru colid
wrstar. Th6 M-336A Ss{t cr Irslfill is ra
'.G.'Lodfill uiag thc 'trcDch' of 'cut
rad covcr' mcthod of opcntion. \trctc ie
phcGd rxt !o e prcvioruly dug Ecach,
pruhcd ino thc tlonch, covcrcd nith roil,
ud thoa conpoctcd with r trrclor * thc cad
of crch worting &y.
Ind$gld.lq[t S.ilts, Wrste - All
3onl rcnliquid, rcohezrrdoua, eod
uiodnstrid w.stc! iocludiog grrbogc,
wattc p.pcr, c.tdborrd, qfctcrie rpfusc,
rolid officc rufirc, eod discrrdcd cnpty
dnru. ltGsc €6it 'r, w.stc! ero dirpoacd
of et thc M-336A €rait nr lrulfill.
lVrste Dlspoed Nodce (Foru TC 8124) - A
mticc whic.h providcs iaforortioa to
btdldiDg pcrronrl oa how io conlct r
dircrepocy so th.t pichry end dispooel of
tc ian(r) phccd oa r Wrslo Meorgemoat
eod Eavirooocotel Scrvicos-epprovcd dock
E y b ecconplishod in e tiucly E orr.
Tho $/rsb Dispos.l Noticc will bc lcft with
hdtdiDg pononrcl or oa tho wrrto dirpocel
&ct oa itcu(s) thrt ceomt bo pichcd up by
M-1364{-fE6 dispo$l crcrrr bcclrsc of e
erocoaU discrrp.ocy.
Wrstc Llbd (Foro TC El25) - A 3 l/4 by
5 ln tD. ycllor Lbcl with blrct lcucriog.
Ir u* bc plrccd oo dl rcnhrzrrdour
qpGs 53
Ertcrids dcstild for diepocd by M-136/Ivl-
l&t dilpoeel crswr. llrrltc I$cls Ety b
odcrcd from Storcr (Stock No. 26{Dtl25).
3. REI'ERENCES
U. 6blid Wa* Ddspsal Rcgfutians,
Utfi Solid eod l{rzrrdouo }lrrstc C.omnittoc
DoT*asportdut Rcgll/rriallr
&rnruoruul Protcaia Aecnq (EPA)
Toic fu*arc htrol Acr fiB@l)
N dul &dstianstalldardsfor Haarbs
Air Polbtans (NFSHAP, deon Air Ad)
Fcderal hscaici&, Fugici&, Rd.nticid.
Act (F'IFtut)
Gcrr.ral Safcty and H?alth Mataol, Chrptcr
4, Folicy Govctaiag eod Rohtod Prrticulrrs
for Arbostoe Hrzerds Scction
IlaM $ hfustrial Waste Dispaal,
Rich.rd A. Conwry & Richrd Rocs, Vea
Nootnnd Rciobold Eavironocntel Svcs
Iloshs Wastr Prqlc fuu $lrlcts
(HWPD)
tddcrial HeaM arrd Sdcry hfomudur
MHg)
Muriol Safcry Dau Sua MfuS)
Propcs H.odling lnd Diryosrl of Agbostos
CooiDing l\,fit ri.b rod Abmcrent of In-
phco Buildiry lv[rtoridr, GU-|.IA
&lid Ya* Displ, Volroru 4,
'Iocincntion rod L.odfill,' Boranrd Brum
eod Cherlcr Prrtor, Ats Arbor Scicnco
hrblirhcrr, Iac.
$uocgic Opcndas Pclicics od
hoctdrcs, Nunbcr 261o.?54
GM-3.1
Issue No. ljl
2l Septcrnber lgYL
R.sa.t@ @nsctvotiott atd Rccowry Aa
(R@A), as anuded in Naqrtcr D&4.
ToxioSubetrocc Cotol Act CISCA)
4. MATERIAIS AND EOTIIPMENT
Bunry'r Minclo tsk Pcn or e4uivelcat
(No.5l-5870O{)
Arbatoa trbcl CfC 4448)
Scnp hbcl CfC 16(}4)
Eupty Dnror
Scrrp lt[etcrid Teg (IC 0t78 or SP 0t7t)
DuopoarBep
lVrrtc Irbcl CfC tUS)
PCB hbcl
Bin Lincn
Tyvok Suit
Seety Gl$sca With Sido Shicl&
Dust lt,lesk
Rcrpiretor
Crrtridgcr, Filar H (hrplo)
SPECHL SAFETY AND HEALTII
REOI'IREI}IENIS
PERSONAL PR(yIECTTVE
EQT'IPMEIYT
hrronrl Dust wG.r propcr protcctivc
oquipmcnt, including lcrthcr glovcs, rs
roquird for srfo bsndling of thc metcriel es
dircctod ia &c MHSI.
WARNING
A COMFO II respirutorwith Ultm H 92
cauivolatt (putpb) fibcr cartridgcs ,nust b
won tdwt no*ing wirt asbcstos naterials
o ruisrcc drcts.
5.
5.1
t[sr.s.54
s2
5.2.r Pcrconrl mrst ridc only ia thc scrtiog
p,totidd for prcrcngcn in thc vchiclo boiag
urcd !o tnosport wrsto Ertcrhls.
5.2.2 It|larid eod/or &itns mrut bc sccrtrcd b
prorrcni felling or droppiag fron tbo vchiclo
&riog tilrsit to r lVrcta Mrorgcmont eod .
Esvironocord Scwicoe-rpprovcd westc
&kpor In-Plott Handing Mounl
irtructior.
6. LI\NDTILL
Oppntioo of thc M-336A Seaitrry I rndfrll
will bo in couplieocc with Utrh Dcpertmeor
of llcrl6, Codc of Solid \ilutc Disposrl
Rcguletioor. Only industrial solid westas
;r*.'3>iaa euch u tnsta pspGr, crfctarie
rcftrc, uurrrblc rcrep wood, ctc., ar
dc.iSntd i! thc IIWPD, will bc disposGd
of io tho Lodfill.
NOTB
All luc ppcr,fmnpclcing, oqnputcr
ppcr, sawdust, afcurio rcfusc, ctc., tutst
b plaedkpbstic }rtgs ad clacd.
WANNING
Ib pans or yfitt rcsifus nor solvatt-
anwfiatcd mgs otpW, sucl, tarobled,lnc liqddJ, cta, wiL bc plucd in
t rc lordiL. For all n'atttcs &furcd as
lwnrfuts, rufcr to &aiu II.
ttahqarbs cha niat wastcs nitl bc
plodd krtc hfu*ial Waste Traulus at
M-136 If Morizcd itans arc in a tmsh
Un, tlu driwr has ba instruacd na o
futp tlt bir Aw unalldlrrrizcditrrzrsnust
b mtowtl ftun thc bin ad prqcdy
pcprcdfo dtsposal
NOIB
bis rte rrs1,oariHliry dfuilfrtgloaqcnis* o ptwid. sdtablc or;ans
ttef6 fian pa*.d v€tdcles, aa ) to
v6ltu c!,thiturs so tha ficy nay b
bryf in a dnuty twuun
GM-3.1
Issue No. Il
2l Septanbq lW2
BASIC DOLICY
R.fusc dispossl fecilitics erc opcntcd eod
nrintdood !o cnsurc r public auis8acc is Dot
crlrtGd. Srnitrtion, sfcty, cfficicacy,
'oooooBy, ead complienco with
cavirooncntel rcgulrtioar erc thc coDtrolliog
fec-tors.
fcur<utierrrd Tresh bias erc phccd et
locrtionr.+DildhE whcrc e occd oxists.
@
u(moN
fiash blrzs ,ntst NOT bcfillcd dwc tlu top
$tlu counw, Bittsfillcdaban tlu top
will noc bc dtonpcd
Srod from csDdblrst or mol&, mctel chips,
ud crrboa dtut must bc collectcd i! liood,
.Fcisl tip or duopoar bior thet erc
tnospodcd, duopcd, rod rcoracd for rcusc
rod rct in regulr tnsh bior. This Ertcrirl
nurt bc rogrogrtGd fi.on rsbcstos-
coateminetcd wrstc.
Whou tho westo frrst gocs iao thc contrincr,
$tech e \lrrstc lrbd GC 8125) to rho lincr.
Whca thc bia is full, scel tho liosr with
trpo, orking ccrtria thc Wrsto Irbcl is
viriblo.
Asbcstor-rdrtod itcmr, reguLtcd undor thc
Clcen Air Act (CAA), will bo dieposcd of
by buriel in thc esbcstos trcach rt tho M-
336A Saitq I{odfill uodcr thc direction
of tho M-136 crcw.
Onrito eoDtnctoB cromt disposc of wrstc
is thc lrodfilt unlcrs it hr bcco epprovcd in
thcir cootnct eod p,rior ernngcncDt! brvo
bccn me& with Eryiroomcatrl Wrstc
DitF.d. All lo.ds Eust bo inspcctcd for
oodcDs bcforc.dniauco into tho Lodfill.
Adaiarocc rh.ll bo dudDg tho opoa houn
of 1300 30 1500, Moodey througi Fri&y,
or cpocirl effrnrcncnt with M-381
ocrsomcl.
TRA}{SIFER REQITIRDX}IEXYTS 6.r
6.1.r
6.t.2
6.r.3
6.r.4
6.1.5
,n}lrt 55
6.r.6 If conpct inrtnrcioo rrl Dt follorrcd in
direo..l of mnhrzrrdour wutc in tip, tnsh,
or &mpctcr biar, e ll/rsb Dispoul Notico
will bG filld out by M-136 pcnoorcl ead
lcft with buildins pcrsonrl or trpd on thc
bi!. Thc Wreta Dispos.l Noticc will dcfiB
thc dirrcplocy rod poyidc instructioos so
tbelprchry.od dfupo..l Ery b
rccorylirhcd ia I tincly DroEI.
6.r.7 Looec sEdl hrrrd itGE! such.! mts. bolE.
orvcl. oir fittimt. nctrl chip!. floor
gwGcoitrc. ccnctrt dtrt. send. dift. ctc.
rhould not bc oleccd in thc tnsh bins.
Thcsc iicmr cusc sevcrc demequ io thc
trrrh truck ncchenisms. Contrct E\[rD for
digoosd instructioru for thcsc itcm!.
62 CATEIERIA WAS'IE
Gerblm gefidaf,p firs6 dining trc.t Eust
bc plrccd ia cootrirn liacd with poly-
cthylcr brg. Thc bryr murt bc glegd
t+cl'elnt ud plrccd i! tnsh bir whca
tull.
WAN,,/NG
UEdd rt{usc (sudt as grcasc) ttpst na be
doccd in ttash birur. S;dtabh dnon wi// b
aryplicd, as raccsw!, by M-136 dsposal
pcnauul unless tlv afctcriavardor lrzrl
todc t?&le arrogqn rtefor liqdd rufitsc.
63 DRAINED OILFILTERS
NOIE
Wa* cilfibn nast b pbccd oa a rur*
arrd allaed to dnin cnryletely ro rcrrutc
at rdt {the 'fnc Agndds' as possible in
tlufilan pior to pbctunt in a DOT 17II
Wt tq 55-pl dnorr
63.r All drrird oil filtcn which wcro uscd to
filtcr e orhrzrrdoru oil, nurt bc dnraocdi! DOT lZI, opca*op poly dnror, (scc
Ffuurc 4), fq fiipocnr !o thc M-336AS.dFr Lslfill.
NOI'B
Smll4ruro,dcs dddrud cilfibn noy bcp in 5- o lo-gol sucl or pbstic bu&es
wirt rt. tdtqcd slut.
q[sa5
GM€.I
Issue No. lll
2l Septcmbc 1991
.. Obtdo e DOT 55-grl, l7II, opcrtop
poly druo thrt is rct &neged (soc
Ffurc 3).
b. Doublc lirc thc dflE with plastic bogs,
rad pleco 4 !o 6 in. of ebaorbcnt
ortcrirl on thc booom of thc iorcr brg
!o rc.& up .ay rocidrul-freo liquid
u,hich Digbt dni! froo thc filtorr
bciry plrcod in tho inu hgs.
Whco tho coateiaer is full, rurch.ltrrtc
hbcl (Fom TC 815) on thc uppor oB-
third of thc dnru or buc&ct. Plrco oo ea
eprovcd w.stc dock (scc Teblo D. Coatect
EI[/D to hrvc wrsto pictcd up.
NOTE
M-136 Asp*al cttws will rlot pick up ary
dnorrs mlcss thcy aru pruprudfor shipnunt
to th. M-336A &nitary LatSA wing
outlimd in the In-Plant Hodlingtlotul (drtont nust bc hrrded topllets
ploccd ott tlu top od Mdn of tlu drus).
NOT7E
Otly rugs gauratcd by changing cilfilun
nutt bc tfrspscd 6pcr instructiutsfotud in
Scdiott II, Pamgroph 10.3.3.
TAG ENIN, PHENOLTC PTECES, AI{D
PII\SIER,
Trg cndr, phomlic picccs, eod plrstcr mrut
bc pleccd ia Dempetcr - Dunpetcr bins, eadd is coomotr tnsh bio!. lf,rhca tho wuto
fint goor i!!o thc cont incr, .ttrch r llrrctc
Irbd CfC 8l2S) to tho lincr. Whca rho bia
ir frrll, scd thc lincr with tepo, urking
c.rtri! thc lVrsto hbcl is visiblo. In crscs
whcrc e lirr is not rcquirod, thc \lrrstc
Irbol oust bc ecrchcd to tho itcu.
NOI'E
All pbsur bils nust bc An d
UUNON
Tag ads, pluolic piccr,s, od pbstcr
plar,cdinDarytterDurpstcr Nns mst bc
omll autgh b pass thrugh the fuon af
tlre lin wlw Aerycd at t E landlL Hl
lrlll6tht ,rwdtnlrln),
6.3.2
6.4
56
NOIR
lf phewtic picca @upt bc ant in 4'
leagds, cdtxc EAlDfor dsposal
insfilrtiant
NOlts
Plurolic bins cottolllfitg &stnutst bc litud
wirt a drm?sur lhw od tqcd shllr"
65 NIIISAI{CE DUSrtr|
Nuis.occ durtl (c.rton" silice, eend, ctc.)
Eu.t bc plrccd ia liDd Dcnptar-Dumpstcr
biu rod/or rrdl tip bins. Whoa tho wrstc
fint goor iDlo thc cooteirr, rttrch r ll/rstc
Irbcl to tb lirr. Whca thc bio iE full,
sGrl tho lirr with tepc, mr&ing ccttein tho
Wrrtc l$cl is viriblc. Rcftr to Appcndix
I oo fi[iog ou thc Srrrta lrbcl. Cootrct
Ef,iD whca bin ir E dy !o bc dunpGd.
6.6 ASBESiilN WASIES
NOTE
Refcr to foile Nfot dspcal pfuging
ir{mnonat
All shlomrts of rsbestm contemlmted
rrstes lroltr off-olsnt thrt rcouir?
trrmmrt on oubllc hlefisavt fi.e.. Test.
Plrnt IIL E-7. X-20. etcl must be
rccomDonlcd bv en Abostm Wrste
Shloment Rccord (Form TCt175).
IrrstTcdons on hor to fill out thls form
@
Dcnqrardrmctarbins bcins rtscd for
ubcstoc or rsbG$B contrninrtcd itcp!
nrut bo lin-t wifi nro (2) 6 nil (mininum)
iqr
to rmr mrtarid bcinr ohccd into thc bin. A
dinl br nrv bc urcd ortri& of thc ohgtic
lir..'r. if d.",O.
NqIE
Arbcrto nrtcrirl nrgt bc hcot &Ep durinq
thc eccrrmrlrtion ocriod.
GM.3.I
Bsue No. Lll
21 Septanbcr f99l
iE
ii
i
At ch r completcd Agbcstos bbcl (Forn
TC 4448) md e complctcd \ilrsto hbcl
(Forn 8125) !o thc bog or plrstic lincrc.
NOTE
llu llaste Ldcl nutst sntc thc cantatts $
tlp bin and t E toltoru in anlic yrds.
All digcerdod egbo$os end rsbcciot-
contrminrtcd mrtcrials shorld bc wcttcd
with setcr sprrycd in r firc mist. Allow
tinc bctrrocn sprrytnsp for completc
pcrtrrtion of tbc rrarid.
Thc dirc.rdd lsbcstoo sbould bc collcctcd
ed doublc b.gged hGEil thickplrstic
bqp eod individrnlly closcd with hcrvyduty
trpo or olhcr ncrns !o cosurc e dust+igbt
sc.l.
NOTE
It is intptuttt a minimizc tlu anant $
wid spcc or air in tlu bg. This will lulp
findflnzc ory anissiots sW tlu fug burst
uder pnsatlr,.
Irbcl o.ch cofrirr of lrbostoc with 6c
Wub Irbd CfC E15) rod thc Asboto.
Irbcl @orn TC 4448).
Fc dirpord of othcr uborto or uborto.
cod.Eirlcd wt!t41, coonrlt Gcrnl
P!ocG.. hrtuction, GU-l.lA, or crll $rrsto
Mrngoncd eod Euvitooocotrl Scwiccl,
Ert 619f.
6.6.1
6.6.2
6.6.t
6.6.4
t[st,57
6.6.5
GM-3.1
Issue No. ljl
2l Sepaemb€r 199{2
WANNING
Asbstoe tryBtc narst bc pe;kagcd in sdt a
tnaruur fu it oareJal ru visiilc anissiqt
aW plesna$ in tlp asb?-ttr trstdt ot M-
33&t
7. DISIDOSALPREPARATION
7.I COIITTAINENSI
7.1.1 Ohrh prcpcr cootrirr! or urc origio.l
codiffi spccifid hcru.
7.1.2 Chcck thc couiron to nlhc suru tboy ero
clcea rod utdrm.gpd.
7.1.1 Excrcisc c.re !o &ccp thc conteiacrr from
boiag coDtrninrtcd bV hrzrdou mrtorids.
rD$..,57a
72
7.2.1
7.2.2
IJ\BELING REQIIIRDIT{ENITI
Prcprrc.od LbGl tho contrirrs pcrTeblo
IV rDd Appcodix I.
NOTE
Wa* ntaial Mun r.rt sdl bc pinud,
ta*ed, odlorprryndinrccotfut c with
Table N. .
Ittrb arrc ell tem end labcls Ssllp,{.Elt
@rrcpropcrly
fillcd ont eod ettrchcd !o 6c contriocn.
GM-3.1
Bsue No. Ul
2l Septonber l9Y2
Opcntionr. Rcfcr o Teblc I for rpprovcd
docL locetioor. Rcfor to Teblc [V for dnrm
prrpcntion.
,
All wrstor dcsigprtcd rs oonhezrrdoru
*r.tcr wiU bo propcrly brgged or druorucd.
A complcaly fillcd out \Mrslc Irbol CIC
8125) uut.cconp.oy crch itcn, blg,
dnro, ctc.
T2' AP DESICCANT WASTES
8.2.r Dcnpstcndumpsar biog locrted irr AP Srindhlildin$ whcrp &riccent is goncratcd nrst
bc li1d with r sting be! or plestic bg
lirr. Whoa bia is full, tho lircr Eust bc
ticd or tepcd shut. A lVesto bbcl nust bo
f,fly complctd.od 8!.chcd 6 3ling hg
with epprcprietc iafotuetion (sco Appondix
D.
WANNING
Dcsiccant bags natst not cotbin ary largc
arlruunet dAP. fuggcd &sica nt with
brgc qnundda, of 'AP wiV NOT bc acocptcd
by M-136 disryal ctcws util tu AP tlcs
bca runoud
t3 EA 934 Al{D SIMIII\R TWO.PART
ADEESTVES
NOlts
Wlunever possiblc, this natcriat slull bc
canpletcty uscd b sitnplily tlu d,spasal
prwcss. hrub IIWPDfoT cach pn to
vcifi wlutlur it is hqarfus or
nofuitfus.
NOTE
Wlut origitul oazairuta @ruut bc uscd,
&dn cl@r, new, pint,lulf gallar4 orgllal pdnttypc s?hblc usfiun Storcs.
t.1.2
NOTts
|lu Wa* Lobl rust stu dp wcight $tlpoiltqtls {tlu bin, bt, * drun, ctc., in
paerds (asbcstc rusaa rs in dic yards).
73 GENERALII{SIRUCTIOT{S
For *orego or dispocel of mnhezrndoru
srstc mrtoridc not spccificelly covcrpd in
6L pmccdurc, rcfcr to 6c I{WPD. If ea
IIWPD hu mt bcca prcprrcd, coDtlct
EN'D.
t. ITTTDUSTRIAL WASTE TRENCMS
NOlts
t{otcdal cnmining hoirdour cottstilllrlltts
lllrLJt fr bc pbcd an an appruvcd buildingddh, trutLtpulrt to tlu h&tsriat llasu
Trrrdt. Tlu,sc natedals nust bc dispucd
pcr pnccdttrts outlircd in &erim n of rtisfurunt od dnppcd fi-plarrthr Asrraol
NOTB
Wastes bcing prcFrcdfor dspcal in du
Itldglid Wa* fiaulu,s, rn,st noc colgin
orylnc tiqddr.
t.1
&l.r
NONEAZANDOI'S WASIES
Nodrzrrdour serlc prcpcrly i&atifiod by
Eatcrid nrm rod gtoct ouubcr on I llrrstcLbl .!d r Scnp M&rid Te3, if
rplicrblc, wi[ bc pic&cd ug rt ot$lishcd
brdldiry docb by Ewirooreatrl
t:[rDlJl 5t
NOTE
If rte cottdw is to orullfor tlu rcqdnd
labcl to b dud, plu cotairur insid.
a ziptd+W hg od pbc tlv lobct a tlp
a.tsidc drtc be.
NO|'E
In oincs wheru it is ron canwnicnt,
Werud rxrste ,rray bc rccvrulaed, &et ,
miing, in 5- or lhgl tpnl ht*tts in rte
bdkfrng ad canrcli .&tcd itrlo 55-gol DOT
1711, ry*tq dnons on tlu.building wasteM ot ttr ard qa$ day or qcruting
s,dlft.
Uring sbop plraoing, Prrr A eod Prrt B of
thcr rdbcrivcr shilld bc EirGd iD thcir
oriSiD.l couirn io cesor whca enountc of
Put A.!d Elrt B rrl cumcicot !o conbioo
thcu, pcr istruaionr fouod oithcr in thc
MHSI or oo thcir cont ioor
l.bch. Aarch r corylotaly fiIlcd out \[/estc
Irbcl GC El25) oo thc contdoor end phcc
oa ea rpprcvcd wuta dock for pictup by
M-lt6 crUvr.
WANNING
brum an sW b tatan to oaly mix
Part A qd Part B in rutios @lLd out in
inct zrrialtr. Mlraocs sW b pbccd k a
mfc aru awvyfia n heardr atd allowcd o
@l dowrt
WANNING
Wla s$ciatt arruuna arc tut awilablc to
nb Part A and Part B in rcsnnu&d
prryrtians, ca& prt tttlrJt bc tfispscd of
scptety.
If n niro4 scrl Prrt A itr it3 orfind
cootriu, if pooriblc, rod urch I propcrly
fllcd ql Wrrtc lrbcl CIC El5). Pt ccoouis on ro epprovcd *rrtc docl for
prchp bV Eryironacotrl Opcntionr rod
ultiE ta dieossl ia thc Indrutrid Wlstc
TrGoA.
cM-3..1
Issuc No. ljl
2l Septanber 1991
Consult IIWPD to dctcrmirc if Pert B ic e
hezrrdouc or Doa{rzrrdous Estcrisl. If it
ir aoohrzerdour, follow inrrnrctioor givcn
ebovc. If Prrt B is hrz.dou, seel in itc
oriSiD.l @ntrircr, if poosiblc. Coasult
Scctioa tr, Prngnph 10.13 for disposd
inruuctior.
NONEAZARDOUS INERT
PROPEXIJ\NT
NOIE
Thc propcr diryosd octhod for
Donh.z.rdous, iocrt propcllent wilt &pcod
oa ttc phync.l strtc of tbc metcrid. A
E tcrid ic rn 'EPA liquid' if it ir quito
ruoay eod will peer through ea rpprovcd
peiot filar (scc Appcadix ltr). It is rn
'EPA colid' if it will Dt p.ss thrcugh thc
filtcr. 'EPA liquid' incrt propclleat will bG
prcplrd rccordiog 3o iD$ructioor fouod ia
Scction Itr Pengnph 9.1. If in doubt u to
which st !o thc ircrt propcllent is ia, coatrct
EIIW.
If thc ioert propclhnt rrestc is not
contuinccd with hezerdous westcr (m
rolvcat conrrmiortcd ng!, wipcc, ctc.) eod
ir'EPA colid,' il sh.ll bc druoncd iD DOT
l7ll, opon-top drums for disposel rt thc M-
136 lodustriel }l/rstc Trcnch.
NOTE
*c *aion II, Paragroph 10.9, if irutt
prqcllat atdlor irca propcllcn lusra is
cata ninted wirt a solvcnt luving.a
lrogrdouJ wastc chaructcristic.
NOIB
$mll 4mtitio,s $ solid, irutt pqcllott
odlor itutt ptqcllott rl,ralttc nt6! bc pbccd
fB !-tol rncul h.*.a wirt du Udc sealcdwifitqc. Iartc gondd?snary b
prcprcd in lirad *11 sling Dolgs WW) acording b itutn ctiqvfand in
Scaia I, Parugaph 7i.
8.3.3
t.4
8.4.1
t.3.1
E.t.2
,E'.,59
GM-3.1
Issue No. 12
2l Scptanbcr l99l
l.Obtria e DOT 55-grl 17II dnrm frorn
Storcr 6rt is mt nutcd on thc cncrior
or idcrior or o6onrirc &oryod (acc
Figtrc.3 lod Figrt$ O.
rsa.,59a
t.4.2
9.
b. Iuurc tho tTlI drun lid her e geod
rorl.Dd plopcr hugl (sGo Soction II,
ErngnDh 6.5.1 r rDd b).
Whoa thc cocriocr is withi! 6 (+/-2) ia" of
tb. top, ettrch e Wrstc bbol (Forn TC
tl25) to thc rrypcr or-third of thc dnro or
Ec0.l bucbt Plroc oa ra eppmrcd unstc
docl (acc Tcblc t). Cootrct EIilI, to hrvc
NOTB
Dlsryal c:ravs will na pickup dtuttt
unlcss @ an pruprudfor slnput to du
M-136 Inilsfiial Waste ftcdt ttskg
prucdutu ulirud k thc In-Plant Handling
tl@ttol (dnon natst b fund.d oet pllets).
MAlERrar GIOTNG TO OlJlrr.rt
ONSITE COLLECTION/DISPOSAL
AREAS
NONEAZATTOUSI LTQITID WASIES
All li$dd w.dcr dccignetod es Donhrz.rdous
h thc II\I/PD such rr 'EPA liquid' ircrt
p,ropclteoq pleniror, HB polynors, IIR,
ECA, opoxicr, otc.; Eltsr bo dnroocd in
DOT l7ll, opceiop dnror for shipocat to
m ofralrot dirpocd oitc.
NOTE
&rull qruAdcs 6liqnd moy b pw in I qt,
1 tol, 5 gat, aa, cdtttdn ts.
.. Obt iD e DOT 55-grl ITII druu fron
Stoslr thrl is rct nrstcd oa thc cxtcrior
or iocrior or othcrwigo &oeged (soc
Ffuurtr 3 md Figun a).
b. IDosc thc lTlI &uE lid hrs e 3ood
!c.1.
WLon tbc aodirr fu wirhi! 6 (+/-2) io" of
th. top, rcech e Wrrtc lrbcl (Form TC
tl25) on thc rrypor or+hird of thc dnro orhrcbt. Phco oo u epprwcd rrutc dock(rc Trblo I). Cootra EIIS| to hrvc unrrc
prctod up.
GM-3.1
Issuc No. Lll
2l Septanber 1992
NOTE
Disposal cravs wi[ rn pick up dtus
urless tlcy an prcprcdfw sfiput a bc
rt&tt w b tlp lwadous wastc oichq
crcnts rffi tsing pocc&tlar-s outlbud in
thc l*Plott Horiling Matual.
92 WASIE OIL
9.2l1 llhcto oil mt contdning brzrrdous solvcotsmrt bc ecouulrtcd ia e proporly clcrood,
rpprovcd DOT l?E, 55-grl dnro (scc
Ffuurc 2).
NOTE
Ifrrxtste cil cquils hqarbus wastc
solvenr, rcfira &aia II, Patagraph
10.3.2 for dispsal insotaions.
NO|ts&n slull b tata n to placc wosu cil
ino dnons thot ate cmdrn cd wirtho$fuc vostat. Tlu rcsubing mi:orlrl is
a hoerfus vastc atd will rcsubin casdy
df"lont disryal ratlpr than inqatsivc
ncycling.
9.2.2 Obtrh r propcr druu from Storcc tbrt ic
mt rtrtcd or othcturiso d.Erged. Rcfor to
Figuro 3 for &un iorpcctioo critcrie.
9.2.1 Vinnlly chcck thc contriDctr to cosurc thoy
ero clcro, tt-l'm.gcd, rod mt corrodcd
ptior to uso. Stcol drurrr must htvo e DOT
3tup oD tho bocou of thc druo.
NOfr&n slnll b tot n not to pbcc mgs,
glova, netolfilkgst ppct, ctc. in waste cilffitian dnorlrr. Oil dnorrs wirt dcbris
infirrrnrna! ansa pwp furugc.
NON
Do na lziJa or! dnon stcruilcd 'RcutrrrlbhDtutt'o?'t _Dcpsit (c.g., t25Dcpit ).'
9.1
9.1.1
9.t.2
g[Oao @
9.2.4
9.25
9.2.6
9.2.7
93
Conplctc e Wrrtc hbcl (Fon TC tl25)
with dl rplicrblc iafurntioa (soc
Appodix t). Ahch thc hbcl to thc rrypcr
on{tird of thc dnm. .ilInr*ingl crcqrt
thc DOT mrsEng urut bo p.iatcd out.
Plrcc doo(r) to bc urd br ecctoulrtioa
of r ryccific w.rtc undcr e ghcd or o6cr
prctcctiyc rhcltcr oa ro eppmvcd wrstc
&ct
NOTB
@das b rtit fiep rrurt bc ratiawdby
ETIW.
Wbcn thc &un i! 6llcd withh 6 (+l- 2) in
of thc top, cor.tra EIISIclil:Scfut€ic
Wiohrvctho
dnlu tnoaortcd to M-186 for otoregc. If
rry pouiUlity cxigt! thrt thc wrstc oil is
comoiortcd with rsy brzrrdotu eolvcnt,cffictEINYffi
Wrtor =rt 5377 cr Drrcr 960.
Dirpo..l of wutc hydrulic oil contrining
her th.n 50 ppn FCts ir thc remc rs for
*rro oil.
NOTEhtodwa* Mamgatmt od
Eruirmtsul Scrtccs, Ea 428,for
dsryal of ttur* lrydxutic cil cardnngguur dlrllr 5O ppn PCB.
DEPIOSAL OF WAS'IE AII.IMONIT'M
EIDROXIDE SOLUIION
Itrtslc rmrrroroiurn hydmxi& frou blrrpdfi
nrchirr or o6cr sourrcGr ie highly irrit ting
b thc cycr, *io, uc, lod 6rc.t.
Anomfuu hydroddc c thc vrpon nry
crtrc tqecNr bunr on cmt ct (rcc MHSI
W2t3). Ar'miuu hdrcxidc ir oxic ud
crrt rhorld bc trbn b Dt ing$t thc
rolutio, b,rcr&c uilr of thc rohrtior, or
dhrr 66 rolutiootr cou in couctwith
rth or cycr. Thc GquipEod
d..cribcd b.h,w Drrt bc urcd whco thc
rolutioo ir h.odlGd"
GM€.I
Issue No. Ul
2l Septanbcr f92
NO1ts
Iltc priripl he,ardr $tlu solatiot arc
fuifuian, cdtt E wirt ory prt $tlu
bdy, N kgasdall.
93.f Whca h.Ddting thc rcsidrr, tbc followiag
cquiP'oclt ir nocdod:
r. Chcuic.l rorcgogglceb. R$bff glorcrc. Crrtrific rospintord. Wub I$d CfC tl2s)c. Bunqr'r Minclc pc1 or cquivdcat
9.3.2 If norc thro I qt of romoniun hydroxidc is
to bc urd or if thc rmmonii vrpor oxcccdr
thc TLV, MHSI rcgulrtionc rcquirc thc urc
of r crraidgc rccpintor. Cbcmicd
DorcgegSlor, rubbcr glovcr, rod e gnock
mtrt bc worn whcrvcr thc mrtariel ir
h.odtd.
9.9.3 Phco tbc unooiuu hydrcxidc ia r cuioblc
cootriffi (i.c., plrtic boalc) rod lebcl with
r Wrrto Lrbol pcr Appcadix I.
9.9.4 Phcc comirr on ro ep,p,rovcd wrstc dock6 rt so ep,provcd collcCion poiot.
9.4 DISEOSAL OF lV'a.TE FOTASSII'M
CEU)RIDB
Ercor potrrium chlori& (KO) is mt
cooridcrcd r hrz.rdou vestc rDd cen bc
urod oa phu for trrrlcwilcr proccssing or
rrcrr rpmvel oo rudr.
9.4.1 Ocu, uryrouod KO cen bc uscd by M-705
for wrrtcrretor trc.tEsnt. To diapooo of
clcro, uoglouod KO, coua M-705, Ert
3/lifl, to nr&o ernogeooltr io drop it off.
9.4.2 Fc dirpool of fmrnd KCl orKO which ir
comointcd wi6 dirt or 3nvcl coDtrct
Rcdr ed Grouo&, Eil 2865. It wiU bc
thc rorpooribilig of tho srro gorntd io:
E0a6t 6l
l.Trrolport thG KCl to 6c ..lt rad !.od
pilc ur lld-172.
b. Rcoovc tho KCx ft,oo tho coot iEr!
md ptecc it orr thc lrlt pilo.
c.Rmrc .od dilposc of cootrirrr,
pllcu ctc.
GM-3.1
Issue No. Ul
2f Septclnbcr fD2
WASAE ANITIINEE'ZE
ftrtc rntiftEGzs mugt bo ecsuouletcd il e
propody clc.ocd, epprovcd DOT l1E 55-Srl
dron. Scc Ffittrc 2 for offalrc shipooal.
A Wutc I$cl GC 815) must bc fittcd
od, Scc Ap,pcadix I, for inrtructiou.oa
fitlisg ort e Wrsb Lbcl. Thc lebcl nrut
bc urchcd b thc rryrpcr or-third of thc
&uE.
If rntifr,cczc contrior hrzrdour eolvcolr,
rpfcr to Scaion tr, Emgrrph 11.2, Li$dd
ILzrrdour Wrstc Prtpention, IIWPD,
ud/c sont ct EIIW.
SALYAGEABIT MATENIAUI
Screp mctrl h.vilg e selvegc veluc mut bc
rcaregrtod rod numbcrcd et tho collcctioa
poiot er pcr thc fo[oriDg trblc. If tho
rcrrp ir 83r'rtGd rt. coo$ructioa ritc, it ir
thc rcrpouibility of thc cootructioa
pceoarl to hul tho ecgrcgetcd acnp ncol
to BuildiDS E-501. BuildiDg per:oorl
lhilld couct Ro.& rDd Grouodl 3o hrvc
thcir rcrrp retrl hrulod !o Builditrg E-501.
95
9.5.r
9J..2
9S.t
9.6
9.6.1
No.Tpo of Selngerblc Metariel
1 Scrrp iroa eod rtccl roli&, forgior,
c.rtingr, .od lhcct of l/t-in. or Eorr
2 Screp iron lod slool of lcr tblo l/8-
i!.
t Scnp duoimo roli&, cutiugr, rd
rhcct
4 Scnp dnnimu titraiuu boriDg.odElilSt
5 Scop ooppcr wirc
6 Scrrp.hrnion wilr
7 Itfirccllcor (bru, crycr, lcr4
ctc.)
,n$a..n 62
NOTB
Pcl;ouul I rtc E-sOl Salw$ Yad wil/
d.cidc tfu nurid is salwgdc ad
tfunturidis na odnde anuqatuu
tolud tlu naulwgcdle mrial to tlp
M-33&l &rnbry Lqdfrll
9.6.2 All rcnp hrobcr, duorgc, .od buildiDg
E brids nud bc rogregrrcd t tbc
collcctimpdc. Contrct Rodr rod :
Grurodr !o hrd tho rcnp Drtcrid !o thc M-
172 Sdvqc Yud.
uanoN
Dona plu btg balrds ornutalintmsh
bits; thcy btugc rtc trunh tru&.
NOTB
Pcnoaul ot rtc M-172 Salwi$ Yardwill
d.cidc wb mrial is alvagdh odwb nuriolis ra odnde anuryarunts
btarl tlu naslwgde nuterial to thc
M-33&l fuitary Lonfill
10. @
10.1 GANAAGE DIIIF(NAL
lO.l.f Gutryc fto,D Buildin$ G-ll, H{, IIr,
II-9, .od Z-12 orutt bc plrccd in duupoton
fordiryosd d loc.l leodfiIls.
10.1.2 At 6c ond of 6c shift, Buildirg X-15/16
pcrrocl mrt trrorfor fillcd wrrtc
coueirn !o thc EriD pLn for dfuposd.
IO2 SATEI.LIIE PTJTNT IJIBELING
NE0IIINEMENnI
Mrrrirlr dc.itp.lcd by IIWPD frr dilpos.l
in 6o heutrirl lVrrtc Trcach mrst bc
lhfuFd to M-136 with propcr cfimiry
doqmotio ed r p,ropcrly corylcod
Wrlc lrbcl. Thc ll|rrtc bbcl mut bc
pleccd ia e plrrric bl3.od rouoly.rrchGd
b thc cooir.
GM-3.1
Issllc No. liZ
2f Sqtcmbor DqZ
rO3 ASBE IIXI WASIE SEIDDIEXVTT
NOTB
All sldpqls {asbcstos<oradnud warste
satltun sd.lliu plorrrs a tlu mnn pbnt atfmwwy rnst h wirt ilB
Asb.stosWa* $npat Rccord (Form TCAn). Tlu rccod prwi&,s 'choia 6 crlrtdy'
of tlu asfuw tsu otd fuutunts dt
totlltc" ddtttdyfton uu prty to tlv nlr.
hstnrcdas an low ofiA ant rtis fonn an
fqord in,lppadx I. lhe rucqd is a six prt
N6fl, ftnn wirt rte filo*'ing dirrritutian li*:
whitc -@urutor (rcanud b tcrpr@r
lran 6sryl site)
7ilDF (k pt by M-33&t)
fmacportcr Na 2 cqy tapt by
t @tJportcr No. 2)
Ttarcptta Na I cqy tkcpt by
tarsprtt t{o.. 1)
g"at -
ycllow -
ptt*. -
Ut. -
pldavd -
Filc or futc cqy tkcpt by
sgtcr@")fuerator cW kp by
saemta)
Ilc acrretor must h.vc Treosportcr No. I sigo
thc rccod rod thca rcteir thc Gcrnor Copy
Gpl&Eod) .od thc Filc or Stetc Copy (bluc) of
6c NCR fotu. Tnoeponer No. I kccpc thc
pink copy rftcr itrspcctios eod aipiog by
Tnorportcr No. 2. Eavirooooatrl \lrrrtc
Dispo..l mut gond beck tho froot Gcrnor
Copy (whitc) roB-7 or X-20 wi6in 35 &yr of
thc rhipncu. H-7.od X-20 nust kccp thcir
copicr of thc rccord (two gcrntor rnd or ctrlc
opy) oa filo et thcir ficility for two ycrn end
uurt fimirh thcn on rcqnalt rod meb thcn
rvrilrblc br irpoctioa by thc Adoinistrrtor of
6c EPA or hir egoot.
NOI76
EVD pcrsowl nrrct b stutcd k adwrwc by
H-7 or X-fr pcaauul to ctrllriln tha sanuairc is
a$ldlc to irspca od vrtily rtc w* od
s|gza rt. Asbooa Wa*
r$a.o dl
GM-3.1
Issnc No. lll
21 Sepacmb€r DqZ
$npat Reatd as ftarspttcr l{o. 2
Ilis u trwsfen
re4.6 68a
10.3.1
rt. anstr/,y ofdp*raste aldnust b dac
by pctxoul oontut bctwcot Trantprur
t&.. l0dTtssrutalb, Z
NOTB
Dllttprrrlr litts ttscd o tturnlpott asbe-stm-
catu n red vartalran H-7 ad X-29 ntttstb tur}rd at dlfw sides N,irt rte
followirq3 b$e
DAN'ER
/fiBAi1USDUST IIAZARD
CANCM, AND LT,T,T} DIfiAfi TTAIARD
AU|TTORWD PER"SONNEL OMT
th. bpdis to b ot aycllowScW 14 irl-
wid. by nitl Hih wirt Uact, bl&
lmringarlarrtlfufigh
NOT78
Rcfcr to Toilc Nlw dsporril W*aekeit{matiqt
fubcatoo filtcr cr&s from thc rsbcrto.-
cmninrtod liquid filtcr $ H, ir to bc
tnorfcrrcd o I dryrar lincd wirh doublo
ptutic b.8r. Df.tcrid nrrt bc &rycoGd
with rurtcr. ErA bry Eurt bc sc.ld
rerntcty rod rcr b M-136 for dirpood in
thc rsbG.to. ltochcr et thcM-336A
Suitery lrodfill. Erch bog Eu$ bo
eccouproicd by r p,ropcrly corylctcd ll/rstc
bbcl rd Arbcrtc Irbol md shippcd with
ro Acbc$o. Wrrtc Shipmcnt Rocord.
Snbocotr Erst bc rchcdrlcd in edvene rod
Erdc dudng tbc &y shift ooly, Moodey
throuth Fridry, rod erivc rt M-136 boforc
1500.
WANNING
,t$c.mchprcgd.d rubbo is na{ridlc
otd tE na nguld. Dry asfu.sta-sutdn*t &.fr crcdcdby b$ng or
grinfrtg tlds nudal is rcguled atd mtstb Aspcd 6 pcr fisanrcdols fa nd in dnt
scaian
GM8.1
Bsnc No. Ul
2f Scbaclnbcr 199,2
10.9.2 Asbcrb.-iEDrcgntcd nrbbor ir mnfrhblc
.od ir rct rcgulrtad. At thc X-20 frcility,
&y erbcrtor-cootroiutcd durt cutod by
buffiaf, girdiog, or chippiog thir mrtariel
ir rlguLtcd rod must bc diryoeoa of por
iortnrctioor fqrod iD Prqnph 10.3.1
.bovc.
11. PICKI'P CNTTERIA
Ooritc SEntor! Eust eoDt ct Westc
Urorgcoont eod Eaviroooontd Scwicct to
tnorftrv..tGr to thc atong!/dbposd
ficiliticr. Werlc E y b plrcod oa ea
tp,p,tuvcd w.stc doct or ia r trrsh or
drryrtcr bin prior to pickrry. If thc
E lcrid ir mt peckrgC rccordiag to tho
ontliocd rcquircDcltr eod thoso of Teblc IV
Wrrtc Mrorgaooat end Eovitonmoatel
Sorviccr pcrrond .ro rct elloncd to pick it
uP.
NOzts
AWastc Dispsal Noticc (rc E124) wi// bc
fillcd * by EAD od citlur lcfi
wirthilding pcnouul or ana'Flastc
ldougarcnt od E*iruarcnul *rtccs-qr*ed nlaste d& or bill. lhc Wastc
Ddsposal Naicc will spcll q,, tlv
dsoxpuy od prwi& irlJt zr,tia,r so tha
n@ atd dspsal6tlu itcnr(s) ntoy bcr& in a thwly rnaraur.
WANNING
8$c acccss to naste b& or bin nust bc
mfiuined at all tirrul.
WANNINGWda palLr t scdlot t wrrlrrlrt@ teaiste
medalc t ufr ,rDC, In-Plott Hotttling
lfuuol rritc 'na Pall6 rn nuaing tb
crttqia aarwD. b rt*ed ry by M-13## dspsol c?cut . Wcb bcl* od ory
bufing nuid drc" tlrannuml slnll noc
bc uccd to ECct ttc rtc fut prlLc.
re14 il
SDCTION TY. EMP T DRT'M PREPARATION
AI{D DISPOSAL
1. INTRODUCUON
fhir rocioo prwidc. iogtructior on
prGp.ring oryty dnro for etongc rt tho M:
136 dnru ilorrgc Fd. M-136 ir thc only '
rpprotcd rrcr for cryty dnru rtomgc eod
rcqrod.doo. Druot corrcrcd in thit
ccctioa m.t bc 'cq)ty' (coc &fuitioa).
Aly huudorr *rrtc rcorining i! th.cotrirr tbrt cro bc rcoocd by poriDg,
puopiry, or upintiag ir rogulrtcd uodor
RCRA 8od Eud bc h.DdlGd pcr iutnrcionr
forud i! Scaion tr of thir docrrocDr.
WAN/|,,NG
Bcforuhandliry atq enry drunrtdhas
cduirud ana.rial ibtdficd as ot uu.haarhs rl,clJtc, odttGt EWD. *e MHg
for infunda qt ew ,rasrdaB *tast4r.
NO1'B
If Uqdd an bc W slaling araed dun
th. dtionb sletslotif ory amnt Sliqdd ot bc pourcd e af rtc dtton, it is
NOTaryry.
2. DEI'IMTIONS
Acuae lr.trdoug lVrsto - ChcEic.l
guboteoccr which hrvc bccn ehorra to bc
htd to hro ol ia lry &ccr or try nrlcrid
crtcgorizcd u ro EPA 'P' wr$c. Thc EPA
*rrto mnbGr for e mrtcrid i! foud i! th.
IIWPD. Errylcr of rcutc hrzrrdou
ortcrielr erp crrtoa dia{fidc,
aitroftycorioc, rod rodftrn rzi&.
BultdDS/AE Rcprccntrdvr - All
tdtOodrrcu u,hich hrrc eo .pplut Gd
dock forprchp of *rrtc ortcridr urt
bevc r dc.iSDlrd rcprcrcntuivc.
Ttir rrprcrmdrc ir rl.iSnd by
suecrvtlon b bc 6c co6ct pcnoa(r) forutbo oryty &uu dfupo..l
ead/or Wrro Dirpml Noticc (Fora TC
GM-3.1
Issuc No. Il
2l Septembor 1991
ttr;2lr. Thb rtprcscatrtivc is rcspouiblc for
ttc tincly rcolutioa of proccdunl
Orccpocls. It is thc rcqooribility of
crch buildia3/ru auporvioor to infotu
Ewircnoootd Wrstc Dispoeel of tho
nro{l) of tbcir eurcDt rcprcacntrtivdt).
Enpty Ihum (contrlncr) - A conteiocr is
cnpty if:
l.All wrrtcr thet cea bc rcoovcd hrvc
bcca rcmovcd usiag ptecticct nrch u
pouriag, plopiag, or rrpintiry, AND,
b. No oorc th.o f ia" of roridrr rcoriDt
on thc bocoo of tbc cootrirr or inrr
liErr.od,
c.No morc thm 3 pcrccat by wcfht of
thc totrl c.p.city of thc coordrr
rcodnr.
Enpty Drum (contolnor) - A coatdncr ir
cryty by DOTdcfiaitioa if it her bcca
'ctcrocd .!d prrSC of ell uiduc' of e
grwlorty hcld hlzedou Erlori.l, 49 CFR
173.2e(rX2Xi).
NOTB
lf a drun w$& pr*i*sly held a hqarbs
naqial is na clanpd od purgcd of all
rui&u prio o bcing $ercdhrtaspuln an public higlways, tlr. &1on
,rutt b tw*.d wiffR.sidtr Pr*i*sly
bubted' labal (odginal haardour
tfrcrial &,scriptiot) arrd b accqnp*d by
slnping Wrs.
WANMNG
f t r. Mtdru? lrar hcW a *rastc ibttificd
at a @utc lwtrbs wastc by U.S EPA,b na dspsc 6dns oanlairur. (Iltcsc
tlntuE an ibdficd k rtc MHg.) n
canudrr."rrutt b rtpb inrcdbeforceswlwirtdp lnjrrrore wd as alwarhp wurrt .
,8 .6 65
lYstc l)bpocrl Nodcc (Forn TC E124) - A
mticc whichD,rovidc. infrm$ioa to
hdldiog porro@l m hm to concct r
dilcrcp.ocy ro thrt prchry rod dirpood of
oopty dnrn! pleccd oa I Wrrtc
Itfrn3cocil rd Eriromcatrl Scwiccr-
eppruucd doct ney bo rccorylirhcd ia r
tiocly E Gr. Thc Wrgtc Disposrl Noticc.
wi[ bc lcft wi6 hdldiDg porrorel or oa thd
*r$o di4anl &cL on ea itcn(a) thrt
c.omt bc pictDd q by ETrD dirpocel crcu,r
bccrulc of r p,rcccdunl afcrtplocy.
3. BEIBDNCE
dc $ Falenl Regtbians,'Iltzrrdour
lVrttc,'Tltlc 40, Frtt 26() thrcugh 265.
dc of Fcderd Rcgfuiots, Titlc 49, perts
171 thrcWh lR.
I*Plant lfadiry Mouol, Scctioatr
tfuerial Halth otd Sficty h{ondat
Nns)
MdctdS46yMogpB (MDS)
Utrh Ilrzrrdour Wrsto ltftoegcocnt
RogrrLtiou
4. EMPIY DRI'I![ PREPARATION
4.I I"ASDLING INITRUCTIOMI
All cryty dnror Drut bc Lbcldwith ra
EnFy DnrE Irbcl GC 7ll). Ttc Lbcl
mrt bc corylctcly fillcd orn uring I
B.'"'ny'r Ilrfirrclc p6 c cquivrlcd. ltc .
lrbcl mrt lirtoridn l oo&fr iocludiDg
ltoct uroba, building lnobcE, drtc
rooolrG4 rfurorc of pcnoorcryado3
pichry, rod d.tc of pichp roquc$. Ttc
lebcl out bc phccd oa thc rrypc crhird
of tho dnrn Ttc Eopty DroE hbcl it
dG.cribGd i! AppGodix I.
GM-3.1
Issue No. Il
21 Sdptember 1992
NOI'E
All rcamdlc dnorrnt rt b starihdwirt
dtc hlyclusc Orderl&ntrut ond tllr words:
nE;N'RI.AaLE CONTAINER
EXIIPIY DRI'M SEGNDGAION
DruE nust bc sq.rltcd by cizc rod
whcthcr rcurarblc or rcDrcarta.blc by tbc
uring orgroizrtioo"
All cryty dnrol Drrst bo cloccd bcforp
tcing tnocportoa. Buog plugr urut bc ti$t
.od in phcc end dl li& tidrtly gccurcd. All
oriSind ErrHDg eod hbcls oo thc doo
uut rcrriniaplrco u if thc druu wcru
firll of iB originrl eontcnts. No wertc
nrtcrid sh.ll bc on thc outsida of thc dnrn.
NOIE
Void all ac*?t btt.
MATERIAL INSIPECIION
EITAEI,ISIE PROCEDT'NES
Bnildiry proccerer eod feciliticc nurt
comrltb.t dl dflEs lrc 'copty'. Buildiag
Fflo@l must ilrtioo gomc ncthod of
nrtcdd iacpcctioo of cryty dflEs pnor !o
pleccoont on ra rpprcvcd msto dock !o
cDturt corrtst prcpandon procodum hrvo
bcca followcd rDd thc dnlr! hevc boca
Frgcd of ray liquids or soli&.
NOlts
Ittnory bc ruessary to tip a D€tF+78
dtlon trytidedown to dnin tlv
Et drdrs Aqdd Thc lcltdclr txlrrcollc*dms dst b dEpcd fpcrirutnaas @ in this furstt.*ctial<l+io*m*
42
4.2.1
4.2.2
5.
5.1
,ru.6 6
32 DRI'M INSTBCUON
Eq*v drmt nust bc ireocc,tcd rnd ncct
thc critair in Scction IV. Penqrroh l.
m*@*r
@
53 DnI'M TNANSTEN
NOTB
Wa* Maagqnat od Etwilulanenul
Sclvie,s wi[ b tlr dtb tasptcr S
dnow o rtc M-136 dnotpd ttttlcss dtcradstqrab haw bade.
All copty dnrnt will bo lo.dd onto thc
vGhiclc ia ecoordercc sith Scction lO of thcI*fut fladfu Matual. Oocc thc druDs
uo rcrmd b thc vohiclo, tb.y will bc
tru.portcd to tho oryty drtrrn 1lrrd or !o 60
mitrry l&dfill.
6. PICKT'P CRIIERIA
Oocc cryty fuim hrvc bcca prcpcrly
p,rq.rud.!d hbclcd, oontrc3 E[tI) o
rfiro8o forprchp end tnncftr io M-136.
Drm. uu.t bo pleccd iae rogruptod
pordon of e Wrrtc Meorgoocat rodErircmoul Scrvicct-lpprovcd dock
Ttc rrtr mnt bc clorrly D.tbd 'ErytyDtur for Dispo6.l.'
Bcfoc tnoreordag.ry cnpty druor, tby
willbo iryccocd by E'IYD ponorrl !o
.t$fc thcy etl cryty, p,ropcrly pEp.rc4
rod urcaty Lbclcd"
If 6c dnn ie n co6y, EWD will couct
thc rs orftatm. E-IYD will Dt
truport 6c dfla uotil it reu ttc crytydru rtrodudr. Thc dnro urut bc Lbclcd
.ccndbS o Appcdix I rod irpcaod u$ilr h Finro 3.
GM-3.1
Is$rc No. 12
2l Scptcmbcr Dq!
NO|ts
AWsu Diqposal tikricc (rc El24) wi// b
frUcdW by M-136 pcnawl od cidur lcfiwirtbddng oronaWastc
ldougctncttt od Enviruuuul Sewiccs-
qprwcdwaste d&. TlpWasu Disarsal
tbicc fiA spcL tu rtc &scruprcy ad
pravidc lrnstttrctiqu so tlut pifu ad
dis7osal 6rtc ita(s) nay b tdc in a
tttubrrroaun
WAN,/,,NG
S$c ue,ss to ntolsu du* mrst fu
m*ufiud o all tinto.s.
7. SATEXTITE PLI\NIS
WANMNG
In or&r to bc ssidcnd anpty by DOT
rcgty'rriant, all dnor nanspttcd a publicrds nast h 'clc@ud od pwgcd {dl,esid.a,' othcttttisc t u dnonnu.st b
nw*edRcsidue lzst bttdrud (oigirot
hoarfus not ial descriptiot). If nm-qnfy by DOT d$zidu1 shipping pctxnuJtewrpr! qry anry dnorydriclt
prai*sty lpW lwtrbs nscrial Dtutts*ln& praiaas$ lpW nan-nglaud wattcb n rucd slipping ruca.
Ir ir iopontivc thrt dl of thc instructioot
pcrtdliry !o oryty &urn! erp followcd
cooplctcly by off-pleat gercretora, b cllurl
cmpliuco with DOT rDd EPA
duriag trusportrtioo !o thc
reia plrot.t &oooototy. Thc dnro! Eust
coryly with dl rcquircncotr givoa ia thir
lcdiotr bcfom thcy ere oftrcd for
tnoaoOf,on oa public rordt. Nonr
cooplirocc with rcguLtory rcquircDcDt!
ory rtrult iD fia or pcrlticr.
,[oi'.0,6'
7.1
72
NOZ'B
Frnpt! dnow rrttst b wxlulty hspcacd by
ttsctpcnaaul bcforc dvy oe pbcd in tlu
cttgcy dnon scmialr $rtc w* dd.
Dtutts rrurst rrd bc plbdzcd urrdt thq lrawb ilrcpcctr;d by ll-t{dacaawtot tlu
tru* drivcr trarrsportfu tlu &uns to tluttdttplot Ihc drto rnary b pdlctizcd
itsrrcddeb 6q rtc ilrcpaiaris
canglctcd.
SEIPDIDD{TS trTOM 8.7
GLEAnUDX.D)
Eupty dflor will bo tnosporrGd b thc M-
136 Eopty DnrE Yud rr thcy ero
3wntcd cithorby thc Ocrrfrcld truckea
@Its,illborhctnorporsr'r rcrpouibility to iacpcct thc
dnror boforc thcy rrc pllctizcd snd locdd
on thc truct Tnorfcr urut bo coordiaetcd
thrur$ cithcr ETID or EIIW. All onpty
dnror which proviouly hold r hrz.rdou!
E tcrid Duil bo 'DOTEupy' (eoo
&ftitioo, thfu ecctioa) bcfor tbcy eru
shipcd to Pmoonoory. If 60 dnu is rct
Gryty by DOT&finition, thc rrordr
'Rcri&E llt Comind' (origiod
hrzrddrl w.stc Ererid dcrcripion) nrut
bc ctracilod oa thc dnru rod it nust bc
[e-mail] by e Bill 6f r .,ling or I
Shippiog Mcm (Fom TC qt04, Rov 7-8t).
SEII'IIIED{N mOM X-20 (BRIGEAI}I
cuY)
EEpty dnro will bc tnuporrcd to 6c M-
136 Erpty Drua Yrd by X-20
tnorpoildoo or tbc M-lt6 c'rcst u thcy
beul hrzrrdour rnrtc frrou 6c ficility. It
will bc 6c tnoryorrcr'r rurpooibility toirFct 6c dtur bcfom 6cy rrc pllctizcd
eod ladcd m thc truch Trrrfrrnurt bc
coodi!.lcd thure EIIW. All crytydrcr wti6 pruviouly hcld r hrzerdoururrirl Errt b. 'DOT Eopty' (ro
&ftitioo 6ir rcctio!) bcfrrc thcy erc
rhimcd to Pmooory. If 6c dnrn ir rcr
GEEay by DOT&fuitioo, rhcurodt
GM-3.1
Issuc No. ljl
2f Septclnbq lgYl
'Rcridro brt CoilriDd' (orieiorl
hrzrrdou E tcri.l doecription) mrt bo
ctooibaoo thc drur rod it mrut bc
ecooryuicd by e Bill ef I riing or I
Shippiog Mcoo (Form TC 0504, Rcv 7-88).
t. DISFOSMON OF EMPrY DRT'IIilS
Tfc cryty doo yerd is loc.rod rt M-136.
Tho dnror will bc udodd eod gtecbd in
8rurpo eccoding o cizc. All rcana$lc&rE eiU bc ect off io oE ri&. Thc
rrrrogsncot of thc dnrnr trill bc undor thc
dircctiol of Eavironncntrl \ltrstc Dispolsl.
NOTE
lf u anW dnonfrls to ncct tlu criteria in
tlp Drunhspaian, Figtrc 3, and is
dnpcy, Etuirutrmtal llastc Disposd wi/d
tokc rte drun a tlu sontary lad$Afor
dtspocoL lfth. drlronis in gd ottditiolt,
],€Jtd.
NOTE
Dotnpbcc cntpry eus ourJide tlufcnccd
etaa, M-136.
9rt+..6t
W
1. IIISM,ODUCTTON
Thir rcctioopmi&r dircaivcc for tho
rttrrgt of liquid erstcs i! buildiog luopr,
iutmctiou for irycting thccc nrnpc, rod
dirpo..t inctnrctior. Uqurd suq wutal :
.ru tnrportcd to cithcr M-705 or M-186
fm utrtrat. Couct HID to rrrrogo for
nrnp FrEpinS. Cootrct ghould bo pleccd as
orrly il thc wcck u pocsiblc !o hcilitsto
tchduling. Cootrct E1l/D for prcpct
dbpocrl ioruuctionr whon ir doubt. A ligt
of chcoiceb, with thc noge of dloweblc
cooccotntiou which cen bo trcetod et M-
?qt, ir p,rwidd ia Teblor VItr thrcugh Xtr.
NOTB
Sllrrry fiu* ogrrairy lrnnrr arc A3O tolfi, Mdtfuy ttmtih Fiey. ,lfur lunrs
ad wcctad scwiccs anc ot an crrurtcncy
Aadr.
2. DDUNIUONS
EulldltrS/Aro. Rcptrscntrdve - All
buitdiryr/rrcu which hrvc e nrup for
stonge of liquid w.ltc Estcrid! Eusa hrvc
r dcli3ntcd r4rGrootdvc. Thit
r€prc&ntilivc ia rsrigrd by srycnieion o
bc thc codct pcno(r) for metrcn
comniry rury dirpocd rod/or llrrsto
Di"p6.l Notica (Form TC 8124). Thit
rceramnt'vo ir rcsponsible for tbc tincly
rcrolutioo of proccdunl discrcpacics. It is
thc rccporibility of crch buildiag/rrcr
to irfrrD ElilD of tho nrmo(a) of
thcir currcu rcprcccotetivc(o).
Crrdoo -DcrigEE ecivitior ias,hich
&*go to cquipocu Dry occur.
nrzldoug Itilrtcrlrt - Ary nrarid bviDg
chnciGrirtic. which cro bc hrrnftl to
hrana hod6 m tho cwironooor.
Esr{our }Vrtc - Ary dircerdc4 otr
4rodfic.tioo, or rpillcd olcrid il or or
mrp of thc blloring c.tc8uiG.: igpiablc,
GM:3.I' Issue No. 12
2l September 1992
rprctivo, cotrocivo, loxic, or listcd as
huerdour $rstcr in,l0 CFR 2*265 ot
Soction tr of tho Uteh Hezerdous lVrsta
trl"rigr*or Rulcs. Ttcrc ortcrielr ero
idcotificd on thc buildisg TIWPD shccs.
Erzrdors lVrste Sump - A covcrcd
cooincr uscd !o collcct hrzrrdous
wutowrtcr. Such e nrnp chell hevo doublc
coDt iDEcot eod r lc*dotcction syetco ia
cerc of d lc.k or spill of itr cootcats.
Erzrrdors VYostewater - lVetcr cootrioiag
eay qrnatity of hrzrrdous chcmicel westa
crlrtod from e nroufecuring ptD@ts,
housceccping, cquipmcat clcraing, crc.
Leelsdetccdon Systcm - A Erodrtory
rcquircncat for hrzerdous w.st6 suopd to
p,rovido a Eo.a8 of moaitoriog (dGtcctiDd)
eay loo of tbc wrstcwrtcr froo thc prinrry
coMi[tDcnt vcssol.
Itilrterlrl Eeollh end Sefety Informrdon
(MESI) - Thc MHSI.rc prcpored by Wutc
Mrorgcocnt eod Eovironmcnal Scwiccr
end rpviowcd by InAstrid Hygicm. Thc
MIISI docunoot contrios chemicel
infonurtioa from vcodor-srrypliod Metcrid
Seftty Detl Shccts (MSDS), sefcty hezrrds
d.tr, .rd hc.tth informrtion.
Sccondrry Q6arqhneoa - A! euxiliery or
oucr wdl in r suap which coateios
hrerrdou ur.stcs. Thie sccoodrry wdl.h"ll
contein eay liquid which lceks or asc.pct
througb tho priory or iorcr wdl.
Wrrnlng - Dcsigurtcs ectivitics in which
bodily i$ury nry occut.
lilretc Dtpcrt Nodce (Forn TC El24) - A
otico which providGr iaforurtioo to
hrildiDg porroul oo how !o oorrcc r
Oecrcplocy rc thrt eiche eod dirpocd of
G{O 69
Uqui& pLcd in r \[|rstc lvlrrgeocot.od
Egyiro@ul Sonriccroprovcd sury Ery
bc ecoqlirhcd ia e tincly uorr. Thc
Wrrb Dispo..l Noticc will bo lcft s,ith
building p6!o@l or oa tho wutc dirpoosl
arEp otr itcE(O thrt e'r'.ot bc pickcd rp by
EIWD disposd crrwa bccrusc of r
proccdnnl
3. RET'ERENCES
de $Fcdcral Rcgukfraiu (4o CFR)
Cia.rul Sdcty and Health ldou\ Chrptcr
5, 'Collcctioo.od Dirpocd of Explorivor,
PropclLot , .od Othcr Ilrzedour lt|tcrids'
tdd.dal Hcal$atd Saftty lrfomAqt
NHfl)
Uuh Ilrzerdor Wrslc Menegcncnt
Rcaulrtionr
Utrh Follutrat DLch.rge Flimimtio,a
Syrtcn (t PDES)
OERATIITTG REOT'IREMENTS
EAZAnI'OT'IT WASIts SI'MP
NDQT'INEX}IEXYrII
4.t.1 All hrzerdor wrstc 3urp! mrut bc
idGdifid by ro Em,iromoatrl Wutc
DLponl-errypliod eigp dc.igDrtiDg it rs e
h.zrdon&$rr$c arop. All hurrdou{msto
mqo Etlrt bc Ftnpcd wi6ia 90 deyr rftar
rccumilrtioa hrr bcguo.
4.t2 Thc &b thrt ecqnillrtio! bcgir EE t bcpccd@oothc
Srry Acctofitim Rrcord (Foru ST 9062,
Rtr 441) Grch tiEc thc ory ir prryd.
h@
GM-3.1
Issue No. 12
2l Septembq 1992
Ttc nrry truck opcntor will eign.Dd &tc
6c puryGd gccionrnd rcqtmulrtion $ction
of thc record foru eftcr poping tbc runp.
Foru ST 9062 nry bc obtrircd by ocndiog
r Spccd lrncr (Forn TC 1557) b EnD,
Irilril Stop 3018. SGc Appcodix I for
iortruaioor oa hw io fiU out thc Suop
Aceuoulrtioa Rocord (Fora ST 9062, Rcv
++r).
NOTB
If ihc Stotp Acfutia fucord is last,
onte WDfor a nat ard
4.1.3 Urcntuildiry pcrrool Eust coDtrct ESID
et thc cnd of 60 &yr of clongc or whcrvcr
thc nrry is rpprcxinetcly l/2 full
(uAichcvor ooEG. 6rt0. Thi! will ellorr
roplo tioo for thc ruop to bc punpod
bcfor! thc 90dey linit is rcrchcd or thc
ruop bcconcr full.
4.1.4 Thc ary tructopcrllor will digcusr with
6c rcrponriblc building opcntor thc 5pc of
wrrlc Erbrid in thc nrmp bcforp puopisg
bc3in . Thir infrroetion $,iU bc rcleycd to
thc M-705 opGnlor by thc sunp tntck
opGntor upon errivd rt M-705.
NOIE
httqts dory surp wild bc stbjca n
astysis pior to punfing o tlu discrctiqt
{du olonytnrrt opctaor.
4.1.5 Ilrzrrdour wtrtGwrtcr, cootrinioS godiuo
rzi&, coraing froo hdldiDst M:75, },l{34t
M.3B4, M-345, M-355, M-360 md othcr
ASPD feeilitia will bc puDecd rad pleccd
h thc ASPD wrt r tprurcil pleot, M-359.
42 NONEAZANDOIXI WAS'IE SI'MP
NEQI'IruMENTS
4.2.1 Nodrzrrdour nrry $rnar ftou A-l will
bc tnufrrrd toM-?Ut.
4.
4.t
tD{'70
4.2.2 Ardidog nrry wutc! fro,E E-517 wiU bo
tnorfGdGd to M-7qt.
4.2.3 Noohrardour sury wrrtar froo E-516, M-
2,M-55, rnd M-36 wi[ bc tnosftrcd io
M.NE.
WANMNG
l}dldlngpcnourullrrust aettisc g@ alrc
b paqrt ary lwnrfus rrlarlrafiuln
audng tlpir nalwarhs t$atu &on?J.
lhc tcsu&tng lrottb,s w* miratlro nast
b arotyzcd @d pr6bd by tlr. M-ffi platt
arghucrbefonqptwl brynp tlu sunp
b go&A
5.WASIBWATEN. TREAIT'ENIT
FACILITT
5.1
5.1.r
GE}IERAL IITSIRUCTIONS
M-7(Xi ir.tc.iS!6d b hrodlc r vrricty of
chcnic.b in thc wertcwrtc. Teblcr VItr
fuotrgh Xtr list tb hdlding, coutiiror,
rod ellov$lc cooccotrrtion ru8es.
NOIB
Ifyottr btdldng gqurat4, i,asuwotc? to bc
ttaadd N-M ilHc[ ir noc liscdin
Tabla WII rtlan$ )(II, cqtu, tlr. M-Mfut hgincct orEwiruonantal Wa*
Dispocal b gyour bdkfing ot tlu prryrfre Also, ifyar hdldng is catdy
&ing ois ptounng to bfitauc xo*wirt
a dsntal nd listcd, frc a sirrilor cate,
so fu a rcvicv ot b cnfuacd. n
rcvicwis rcesury to detemhu rte
fraobi@ drt. drlrlrncrll
5.t.2 Tcdilg of ttc wutawrtcr in thc nlry ir rct
rtqdd if thc ruutantcrir gcrretcd fronuorl dry-todey plDccrtc..
s2 Sf,lII.s OXACCIDEDITAL
DtrNEAXGIEI
Il tb crnc of e rpill or ecci&ml
drcf.r3c b . ery of r &micrl int@ mdiDg 6c linir ebUirhod in
TrHc. Vltr trugt Xtr.d DrDd dey-to-
&y urqo, thc rcrpooriblc hildiDg frrcnra
rI{A
GM-3.1
Issue No. 12
2t Segtember tgYl
or ntpGrvild Enst rtpod thc informetion to
th. M-705 pl63 Fnginccr or Ewiroaocotel
Wrrb Dispood pcnoorl.
fhc rcport mrut inelu& tbc iaci&at
locrtioo, aroc of puron rrporti[g, chcnicd
irolwd, eod epproxiota gnatity. Ttc
M-7qt pcilorl u,ill thca bo eblc to
&bruiDr hos boot b hrodlc thc
q,ttttlmt!f,.
WAN/i,/NG
Adwtian $rtc hilAng &bgc systlzn wiL
,torrrolly olllsc tlu slrlnp to otctfla* nns
is Msidcnd a spr,I/., as is ory dhe? sfiU
ruscd by a sug otctflan, and nust b
rcprtcd to nn&d Enurgacy Rcsptttc,
Er 222:2 o tlu Pratwttory lmtiqt
DAILY ST'MP INSPECTTON
GENERAL IT{SIRUCTIONS
Evuy arap oo pleat thet cootris brz rdour
wuta Eurt bc iupcctca by eo opcntor
ovrt1r oocntinc {rer5r3 dey. An oocntinq
&v ir enl drv e fecilitv is uscd for itr
imcndcd oumoec. Thcrcforc. if ocrsonncl
ctcr e frcilitv. thc sump nust bc iospGctcd
tht &v. Tho oporrtor uust chock to.ssum
tbrt:
6.1.f Thc trcach lG.diog to thc euop is frcc of
cflcb, holcr, or lcvrctc corrocion.
6.1.2 Thc lid or top portion of tb trot ia frcc of
cncb, holor, or rcvGrc cormcioo.
6.1.3 Thc tlal hu m oigu of ovrrfrlliag or
teilliDs.d ir frrac of visiblo cnclr, holcr,
of acvcrc oorrocioo"
6.1.4 Thc Su-n Accunuhion Reord @oru ST
906il, Rov +91) it ia plrcc lad shotm thrt
nry hrr bcm Frycd withia 90 &yr of
thc rccuouldoo irst &rc.
NOr,A
lf dtc slrltp is rwe dn Wfit\ ttoofr@wi// otw EtD to haw it
enVca
6.
6.1
7t
62 SDCOIT{DAXY CONIAINMENT
Tbc follo*,ioS rcondrry comimcat itcos
mrtbc clcc,&cd to rscuoth.C
6.2.1 Ttc rccooduy cootriucat ir frcc of vieiblc
crre.[ holcr, or rceorc corosio[.
6.2.2 No *retc nrtcridr rrc obrcrvrblc ia thccdi@n ud m lcrlr rrc
&bccd by 6. lcrk dcactio ryst6u.
6.2.9 Tb qrcrfill eod spill coffol cqdpmcnt b in
wortiry ordru indicrtcd by 6c lcrk
dccctioo probc, ctc.
7. W
Rcnrlu of 6c iorpccionpcrformoa innqnen 6 rbovc Eurt bc rccordcd oa tbc
Sury frcility - IXly Incpoctior R.cord
(Foru IlC 79tli, R6v G90). Thcrc
inrpcaioo rGcordr rru p.il of thc officid
opcrdrS rcood E ld.tcd uodcr Strtc eod
Fcdcnl rc3drtior. Tho iorpcction record
mtd bc oo,rylcoly eod rcomtcly fillcd ort
by tho opcrlbE eorfrnhs thc inrpcctioo of
thc rury. Frihrc to conduct thc rcquid
illFcdoo, ilriryisS thc iaopcctioa, or
fild&ing tho iorpociondoctncot mry
rlolt iadidpliny ection roilor othcr
ectior tV Egnt tory egcacicr. Scc Figur 7
for u cxrrylc of honr to fill out thit foru.
At 6c cod of crcb wk, rcnd conplctcd
fuur to W.nc MrrgoEont md
Eaviromcorl Scwiccr .t ltrf/S 3Ol.
NOTB
In q*r to prwid. a crltirlllolit nord $
sutg itspeclia arriulicr, bdkfings nuttllrffi rtds n@d we,ckt!, *cnif rtc surq.ssddm Uqrdd &ring rt.w*odrc
irltpcaiarr td, ploe. tdo* rttwlgh dte, colrantt'NlA'tbtdusc days furt.rcw rD Uqid in fic sutp. lh* al,zw thc
lu oft. adcfult '&onp wan aryy'il
rte llrrtp w antry all rlrch
t. DISCNEPAT{CIES
tutz
GM-3.1
Issnc No. 12
2l Sqtembes 1992
If r dircrrpocy i! foud dusiog tbo deily
arry irpcctioo, imncAraf mtify yor
ryGrvircr.od EIYD. Not6 thc dircrcpocy
oo tbc.inrpcction rccord rod list corrcctivc
rctioa trbn in lhc 'corocntr' scction.
t.I GDNEBAL II{SIRUCTONS
Ilrzrrdour v.s!c nropo hrvc bccn fiocd
wi6 e lc*dctccrioa rylbn which rctivetcr
e rcd prl $bt whcn liquid ia &tcctcd ir
thc erco bctwccn thc inrr end outcr
@frimGd vcrrolr.
NOIE
f;atu storgs hovc bcatfiwd wirt a tmdng
ruc Utht in dfrtim to tlu rud pnel light
wli& alsoirufratq a lc&.
Thc firrt tirc tho rod li$t ig ectivrtcd,
couct illD o hrvc thc ceusc of thc
ectivrtiol imlltiptd eod rumovo eny
liqrdd fouod in thc inrcr sp.cc.
NSIE
7lu sl/,,t'D tntc* cwtn ranovc all the liouid
,ucd to b cwtac'tcd to ttnow th. ,tsieol
wer ad tlwsfarit into ttu sl/,,r,,,.
t.1.3 If 60 rod ligbt should bc rctivrtcd epia
rftcr thc atcpo ortlircd ia Pengnph t.1.2
hrrc bcco teba, thcn roy liquid ford by
pnopiag tho iffi sp.oo Dnst bc sroplod
rod.o.lyzd to lcc if thcru erl h.zrrdous
$,rr!c chuctcrirtis ia thc liquid.
8.r.4 If tfc rulyrir doc. Dt indiceto tho prcroaco
of hrardou orcrielr,6c liqrdd Ery br@od. If ttc urlyrir showr thc puooco
of hrzrrdour orlcrhlr, tbcrc ory bc r lcrt
ilthc im*rll of 6c nrry.
r.l5 Ttc dbmry of r lertiar priorryodioffi vcml coutiorcr e rpill of
trzudotrr e.rtr.. Eaviromconl W..tc
Dfueo..l mrrt bc cooctcd irocairoly ud
rucdirl &tioo Drrt bc inrtin d b trry
6c ntry lod rcg.ir 6c lG.t
t.1.1
t.t.2
T2
t2
8.2.r
8.2.2
NOTB
Aw lakcd Updd;faod sloll bc pbcd
citlpr h&irlro rte prinury cazunorlrrltt
vqscl ovirt fi. Aqddr trusfcrndino tlu
sllnq. tn&.
NO|ts
Itis a lcgal rcqrdrunwt tlra a lo.&ing
,roordouJ *nrnc iltp b tatal art $
scrtcc raol tra ldrrar bcatfi*d
SI'MP IITTDICAIOB PAI{E,
All hezrrdou euE arrys hevc bcca 6tcd
vith e ory iodicetor pracl which &picts
nntcr lcrcl .od lc.t datcctioa cooditionr in
thc hrzrrdour errra rrry. Buildiry
pcrronrl Du$ codiuD !o rtly oo &ily
yinr.l chcctr oa thccc conditioor.
Unnlly. grrcs lid* dcprcr e cetirfrctory
coodition.od rd ro uoretirfectory
cooditioa. Aa crplroetion of crch iodicaor
oo r tlpicrl prl ir u followr:
(l) Grtca wrtcr lcvcl setisfectory lig[t.
(2) Rcd wrtcr lcvd uoretisfictory $bt
ildicrtiEg wrtcr lcwl ia thc nrop irur ir full cepcity eod roquires
puryirg. Coua EIYD.Dd rcquet
th.t tb nry bc prrycd.
(3) TcstBuomvhich whsapre$Gd sill.cie.t both rd lighs (f,Ieod #5) o
indicetc thd 6sy both urort If rct, e
uoublc crtl rhould bo plrccd with thc
.pDropri.lo divilioo o hrvc it
rq.irtd"
(4) GrcGo li$t iodicrtcr thlt thc lcrk
dccaiou rylEn docs Dt sGDlc r
lc*i.g cooditioo.
GM-3.1
Issue No. 12
2l Septembet 19Bt2
(5) Rd li$t iodicetcs thrt thc lce&
dctcctioa systcn scare s lcekiag
condition. Rcfsr o Peregnph t.l, thir
ccctioa, for &trilcd i8t$ctiosr oa
wlht ectioa to trb.
TYPICAL SI'MP IITDICAIOR, PANEL
9. ST'MP PT'MPING
9.1 DEIERMINING WEEN TO PT'MP
,gtTr',it
Wtca thc suop ir orhrlf full, or if it hrr
bcco 60 &yr sincc rcctnulrtioa of liquid ia
6c rury bcgro, couct EltD o hevp it
pttoFd. Sehcduliag it rdvrooc ir
n'ndrtory. Wort should bc cchcdulcd rr
cedy io 6c wcck u pooiblc.
Thc wort wBk ir liloadry trurgL Fri&y,mD-l@. Atl o6cr rcrt rrill bc oa ro
otEl
SA'E Urcry:g
(11
WA1ER TEI'EL
g
Ilol.EJlK tEAl(
(41
llATDEIE6NOil
ottg.
9[L.a 7,
92
coGrSpoqy bub only. For off-shiftrtcc&cod , @ntrct E:WD.
NOIts
lf a bdldng *zsfuw is plouud od rtc
suttp is norc dwtwfull, cotua EWD
bclorc bdunng wsfuw operdidt b
rlro.oc fu rtc sutg ltac autgh rycity a
ca unn rtc nsfuw nnun
SI'MP TAUCT OPERAI'OR,
ASStr'TAI{CE
Urcr urr rqcrviriol ir rcrponriblo for
providing .o opdrtor to udst ia pooitioniag
fu truct md prying thc arry. Thie
opcrrtoE ut t bc frnilierwith thc locetioa
of rrte re&ty cquipoaat auch rs aefoty
showcl, tclcphorr, ctc. Almyt dlos rs
Eoch lc.d tire u pooeiblc !o.s8u!c timoly
pchry whca oofrctiog EWD. Thc EIYD
PtoPGlLil Crcw p,rwidor b.chry opcntiona
fccncrjeocicr oo rwiog, gnvcprd, eod
wtcbad thiftt. Ttcreforu, opcntor
cflcrrg! b liEitod einpc thcirpriorry
rcqooribility is hruliDg end dirpooing of
*rrtc propollror.
NOB
Ihc EWD opawrwiV radfy btdldrng
pcnauul pior b ponping to crut tE tfu a
lulpcr is awnldlc da rlr. nory tru,&
anivcs. If a lulpcr is na pruvi&d by t E
fuiWtag, rtc sutq. wi// noc b porycd.
Pmgingrra,st b rusdt d.Ld.
93 SOLUXI
It il iryortrot forrucn b p,rurrcu oolid
hildp in oryo. It ir ortrcocly difficult
to SS toli& orr of thc nry truct.od M-
705 crmt rccGpt hqo lotru of roli&.
Tb bcrt pncicc ir o pruvct roli& fi,oln
SodoS ie 6. nrq. in 6c firrt plrcc.
IliEiDS 6c nry whilo puopiry will
rmec mrll rmo of roli& ed prcvcnt
bdep. Thc EWD opcrtor will
GM-3.1
Issue No. 12
2l Septembet lW2
&t tuiDc thc uotrot of goli& thet mey bc
punpod.
,. NOtts
Awoerlwc sW bc pra'ided o nnsc tlp
clonp; tlis wiV pr*ent resid.c AnWup k
ttu fualrr. nu bdldng qcrutoris
resporrsiruhr fising tlu stottp dwing tlu
pton?iry opctaian
10. PICKI'P CnIIERIA
Bcforc prrping rry sunps, thc E1VD
opofirtor mut inspcc thc aunp to cogurc dl
rppliceblc rcquirnoatr src Ect. If eay
{ilercp.acicr rrc notcd, thc opcntor will
co6ct tbc uscr orgenizrtioa.
NOlts
AWastc Diqposal Naicc (rc El24) wiU tu
flled u by WD pcrcauul od citlur lcfi
wirt bdkfrng oi o, th. rn'altu
sunp. Tlu Ya* Ddsporal tloaicc wiV spcUN du dsctcprcy od provi& insllraiaza
so tha rynpkg Stlu stottp nay t&e placc
ina tfiruty noruur.
NOtB
All lwtrbs srorrp narJtcs ftun tlu Tcst
and Ptott III atrts rnust bc acconpncd by
a Udfom Hqtfus Wasu Manifcst.
fueric cqias 6rtis nnnftst arc aricd
by rtc suttp tru.&opctato?. Tlu building
qa@rrucd oaty write tlp fuiktng
,aertcr and ulcdop rrrordr,r ott the
,nanfrst.
WANNING
S$t arct-ss b tvolJte slrzps ttutst b
ndunrud o all tinu.s.
qptil<.il 74
GM.3.I
Issuc No. Ul
2f Septcmbc f9ql
IJST OF TABLES AND FIGT'RES
TABLE I WASTE ACCT'MT'I.A'UON AREAS
TABLE tr M.I36 WASTE REACTII/E MATERHL DISPOSAL CATEGORIES AI{D
CIASSIFICATIONGROT'PS . . . . .
Paqc
n
7t
a
t3
t6
t6
t6
t6
n
tt
t9
90
v2
%
%
95
96
n
99
l(x)
l0l
rg2
103
l04
TABLE IU
TABLE IV
TABLE VII
TABLE VIU
TABLE D(
TABLE X
TABLE )q
TABLE )qI
TABLE )qU
TABLE )(Iv
FIGT'RE 1
FIGT'RE 2
FIGT'RE 3
FIGT'RE 4
FIGT'RE 5
M.I36 TRENCII LOCATION BY GROI,'P TYPE
CONTAINER MARKING, PREPARATION, A}.ID I-ABEIJ
APPROVED IIAZARDOUS WASTE DISFOSAL CONTAINERS
APPROT/ED DRI'M LOCK RING
APPROVED BT'NG PLUGS
DOT IIAZARD CI-ASS I.ABEIS
TABLE V WASIE DESENSTTIZING REQT IREMENTS
TABLE VI IIAZARDOUS WASIE FROM NONSPECIFIC SOI,'RCES
IIAZARDOUS WASIE FROM SPECIFIC SOT'RCES
CEARACIERISIC IIAZARDOUS WASTE
NO WASTEiIATER
EMX WASTE*'ATER
MDGD CI.ASS I.I AT.ID I.3 WASTE'II'ATER
INERT WASTEWATER
AP }I'ASTEWATER
REPORIABLE QUAIITmES
DOT IIAZARD CI.ASS
WA.SIE DISPOSAL NOIICE
DOT r7E (CLOSED TOp) AI{D FOLY DRT MS
DRT'M INSPECTION
DOT t7H (OPEN TOP), 55-CAL DRt M
DOT FOLY DRT'M PREPANATION FOR WASIE RAGS
retr 7S
GM-3.1
Issuc No. Ul
2l Septanber l99l
FIGT'RE 6
FIGT'RE 7
FIGT'RE t
FIGT'RE 9
FICI'RE IO
FIGI'RE II
FIGT'RE 12
IISI OF TABLES AND FIGITRES (con0
IIAZARDOUS $/ASTE STORAGE CONTAINER INSPECTION
ST'MP INSPECTION DAILY RECORD
:
ENVIROT.IMENTAL SAT,TPIE CIIAIN OF CUSTODY RECORD
IIAZARDOUS WASIE PROFTLE DATA (FROlrD
IIAZARDOUS WASTE PROFILE DATA (BACTC)
SATELUIE ACCT,'MT'IJSION AREA DRI'M PREPARATION
gO.DAY STORAGE AREA DRT'M PREPARATION
Prqc
lqt
l06
to7
r0t
109
ll0
lll
rGtil 76
GM-3.1
Beire No. U!
3l Septanber 1992
. TABLE I
WASIE ACCT MULA-TION AREAS
APPROI|ED 'LI\IE' WASIE DOCK L@ATIONS
ASP, M-f3 l{-?fp^ M-519 Ild-fff2lM-60il M-638ASP,3 M-57A M-nA M-523 M{04 M-676ASP-354 M-76/M-163 I!,[-2/l M-52t MOs M-690M-13 lvl-79 M-303 M-5t0 M-606 M-693M-r6 M-126 M-309 . M-5&r M-621 M-694M-l9A M-t74 M-3IA M-590 M-622 M-705M-26 M-191 W M-59,yM-595 M-6TI T-4CM-n M-19:l M-504 I!,,,-59f/I0,,,-5n M-628 T-zt'M-t2 M-tn M-5t2 M{Ol M429 T-92M-34 M-z)t
SDAY IIAZARDOUS wAsIE ACCI MU!-A*TION AREAS WASTE DOCK LOCATIONS
A-2D
E-512
E-516
E-St7
H-7 (ClearficlO
M-16
M-I9A
A-2 (Pallaaincr)
n#E
E-5t2
E-515
E-516
E-St7C
E-5t7
E 5l9D
E-529
G.12
H-5H{
H-7
MAM{!&l
MA1
M-f3
M-53(A)
M-68
10,,-79)
M-52/M-Ill
M-l13
M-lz)
M-137A
M-179
M-t9l
M-193
M-237
M-303M-tzr
M-12
M.19AM-n
M.35A:
M-{3
M-45
M-48
M-53
M-55
M.57A
M{OM{7M'I
M-71)
M-l@
M-l04r
Nt-ln
M-50t
M-512
M-573
M-585
M-590
M-593
M{28
M-689
M-705 (Roll-offbia)
s-633
T-4C
T-92
x-16
X-2() (Brielan)
EXEMPT HAZARDOUS WASTE RECYCLE AREAS
A-l (Colorod fixcr aad &vclopct) M-39 (Fixcr aod devclopet)A-2 Uppcr (Colorcd frxcr aod devclopcr) M-ll4 (Fixcr aad dcvelopcr)
A-2 l.orvrr ( Colored fixcr aod dcvcloper) M-lyl (Fixer and dovclopcr)M-9 (Colored fixcr aod &veloper) M-5O8 (Fixcr rad &vclopor)
M-35 (Flxcr aod &vclopcr) M-636 (Fixcr aad dcvclopcr)
SATEIIITE THZARDOUS WASTE ACCI MULA*TION AREAS AI{D/OR WASTE DOCK L@ATIONS
M-52/M-Iu
(Insidc)
M-ll3A
M-l15
M-120
M-136
M-174
M-179
M-184
M-l9l
M-tv}
M-lqlM-tnM-llc
M-208
M-200
l,,.At2
M-XU
M.AI
M-303
M-304'
M-t2o
M-321
M-3668
M-504
M-50t
M-512rf,{{5
M-514
M.SR
M-585
M-590
M.IYL
M-5qI
M-595
M-598
M.599
M-600
M-@5
tn-623
M-6TT
M-62t
M-643A
M-689
T-{
T-0DT.ITTA,'
T-24
T-298
T-91:r-ee
T.YP
x-zJ
' Moves u,rste to M-303/9GDryDocJc for pickup ' Moves wrsltc !o T-9/AgUDrty Dock for pic&upt Moves $,tstc to T-4C/9G'Dey Dock for pickup ' Movog nagto to M-62t or M{89/9G Dey Dock for pickup
' Movcr wssta !o M-ll3/9O-Dey Dock for piclcnp
trean TI
GM-3.1
Issuc No. f.il
2l Septeobc 1991
TABLE tr
M.I36 WASTE REACTIVE MAIERHL DISPOSAL CATEGORIES
AND CI.ASSIFICATION GROI'PB
A - Cless 1.3 composito pmpdlmt witout HMK aodor RDX
B - Cla$ 1.3 oonpositc propcllrnt with HMX aod/or RDX
C - Cls$ 1.1 nitdo cslct cont ining Detcrids
D - Itrgh crplosivc netcridg
E - Pyotcchrica/i[uninaots/naelpowdcrs '
F - Oxidizdr (docs oot irclu& Iil,O$
G - Iaboruory $astcs (mu* bc scgxrsptcd as dirpcted by GM-3.1)
II - A.F. Pt ot 78 nircr nastc
Rcactive Ilezardous
Matcrialeesrn
SRM
Fotnulaioa
TP-HI1,l8
TP-HIl78
Ctass
1.3
1.3
Grouo
SRM \trastc TP-HIl4t
TP-HIr78
1.3
r.3
A
A
A
A
A
A
A
A
A
A
B
A
B
H
A
A
A
D
D
D
D
ASRM
PK
TP.H1233 1.3
PK Wastc
TP.HIZJTC
TP.IIII37
TP-HI129
TP-HIt29
1.3
1.3
1.3
1.3
cestor l2o Gt (E.L.v.)TP-HL246 1.3
AAAM TP-Ht247 1.3 HII,D(
Steodard
Staodard Boost
Stroderd Wsstc
Frou A.F. Plail 78
I6ixcn Only
TP-HlZ)5C
TP-Hrz)6C
1.3
1.3 HLO(
l.l
1.3
IIIvO(
IIARM nopcttrat
Ignitcr
IIARM Wrsts
IIARM W.fic.d
HARM Westc.dWrnc
TP-Hu59
P-Hrr51 IIII
.3
.3
.1.tPBXN-I(}? GlTo t)
PBXN-I()7 CD,pc D
RDX
Tonrhrutt Wufcad
Tonehru& Weficed$/rsto
PBXN-lo7 Gypc tr) 1.1
PBXN-IO7 Crypc tr) l.l RDX
,[sttt 7t
TABLE tr (cont)
M.I36 WASf,E REACTII/E MATERIAL DISPOS.qL CATEGORIES
AND CI.ASSIFICATION GROT'PS
GM-3.1
Issue No. Ul
2l Septcrnber 1992
Ilzerdous
Matedal
HMX
HIr,D(
NG/HI\,D(
NG/HI\,D(
NG/HIVD(
NG/HI\,D(
NC/HI\,D(
NG/HIVO(
HIID(
HIID(
Proqmn
PAIVI.D tr
IgDita
PAI{-D tr$reste
Fron A.F. PLot 7t
Mherr Only
c-3
C-3Igtritcr
C-3 Waso
Dcmo Motor
FhrG lgnitcr
Flsrc \ilastc
SICBM
Minutcnan lgBitcr
Stegc I
$$p m
NIES
Fotnulation
TP-IiNM
TP.HTZB
TP-HIr23
TP-HI097
TP-HI241
t,RP
TP.IIII37
$rN(-2
Wasto
TP.HINA
TP.HT23O
1?-H1016
TP-HIol6
TP-N1040
TP-N1039
TP-Nl03t
TP-N1037
W.stc
TP-,lt?2z
Wsstc
TP-HI0l6
TP-Hlolr
Wlstc
AI{83066
TP-HLX2'
W.sto
TP-Hl2r4
l[.sta
Oass
1.3
1.3
Rcestivc
Chouo
B
1.3
1.3
1.3
1.3
t.3
A
H
A
A
A
A
cc
A
cc
A
A
A
A
c
ccc
B
A
A
A
A
A
A
A
A
t.l
1.1
1.3
l.lt.l
1.3
1.3
Westc
ISiDit€r
ISnitcr
Iguitcr
c4
c-4
c-4
D,,5
D,5D5D5
l.ll.l
1.tl.ll.l
t.3
1.3
1.3t.l
t.3
1.3
1.3
1.3
1.3
1.3
,[$t19 7t)
TABLE tr (cont)
M.I36 WASTE REACTTVE M/SERIAL DISPOSAL CATEGORIES
AT{D CI.ASSIFICATION GROt'PS
Rctivo
Fotmulation
T?-,tt232
Westo
TP-HI194
Wrste
Ctass
1.3
1.3 ..
t.3
1.3
Grouo
GM-3.1
Issuc No. Ul
21 Septanbe l99Z
Ilrzedous
Msrcrid
HI\,D(
HI\D(
HII,O(
HLD(
HII,D(
HItD(
Prcqnm
AIVIS
lvfalcmutc
fxecrincatat
BiDdcr hcmix
Flsrc
IlluminaoU
Mctrl
P;Trotcchnics
DI-Mtt
DL.IBY'DI-ID9t
W.sto
DL.H4?S
%sto
DllH429
DLH433
DI-II435
DI-II44t
Dl-H49
DL.II4'2
DI-H491
l.t
r.3
1.3
1.3
1.3
1.3
1.3
1.3
1.3
1.3
r.3
1.3
1.3
1.1
l.l
NG
NG
NG
NG
NG
A
A
A
A
c
A
B
H
B
H
A
A
A
B
B
A
A
cc
ccc
D
D
E
E
E
E
E
E
TC-LL32
TC-LI30
TCdl,A
TCdt40rilrstc
HIr,O(
EEbdEGot
FoudcE
ltiolitc B-7,Bt, B2l,ba
W.sio
Ittryrcsiun rod
Coatdrcr $rastc
Aluninuu god
CofriEWlsto
Bomn Doqrdcr
Vuioru Pymechnic16r fton I-10
1.1l.tl.tl.ll.l
,E.D t0
TABLE tr (con0
M.I36 WASTE REACIIVE MATERHL DISPOSAL CATE@RIES
AT{D CI.ASSIFICATION GROI'PS
GM-3.1
Isguc No. Ul
21 Septanbcr 1992
Ihzsrdous
MaicrialProeram
IR Flarc llluminaot
IR Flar€ llluniorot
ASP
FN-1060
FN-106l
Oridizcr
Ieb Wasto
Fornulation
Ittrg Tcflon aod:Cortrig W.stc
DLQ152
wlsio
DLQ155
Itr/astc
Bomn Fotassium
Nitdc (t D(-171)
sod $/sstc
FN-1060FN-l(rl
Ctass
1.3
1.3
t.3
Rcacive
Grouo
EIA
D
E
E
E
E
E
E
E
E
AP Cont Westc Only 1.3
AP Cont Wasc Only l.l
Fotossiun
Fcrchlomtc
aod Slastc
Anmoniun
Nitratc eod Westc
Sodium
Nitmtc aad \Mastc
Fotrssiun
Nitmlo aod Westc
Nl, cxccpt HMX rod RDX
a(M-3
Fhro Itrrg WasEi
F
F
F
F
c
D
E
9:[$ur il
Grcuo
A
B
c
D
E
F
G
H
GM-3.1
Issuc No. lil
2l Septembq lW2
TABLE IU
M.I36 TRAY *EI{€II LOCATION BY GROT'P TYPE
.M-136 Trav :foreh Location
Cra 3o iD dt 1.3 traF trm[.. aod caa bc trscd rg e dooor in ell trays rcrehoe
Cro go i! dl 1.3 Eyg smh* on thc south ends with e sling bag holc uscd !o kccp A aod B
Ceo go in all 1.1 leyg tca€hGo
EIiO(, RDX, Crg\{-3, 8od conttEiDdcd rmstc (includiag nasrcs from M-57A, M-585, and dl
othcc HItrD(, RDX, CrO{-3leb wastcs) will go in leyg Plre{+
Flerc uastc @withasmellClassA donor.ffi
Pyrotcchnics fron I-10 may bc
plecod with A wlstss
Oxidizcrs (cootroinarcd wastc only) burn with Gto.up A trrastcs (AP, sodium Eitratc, dumiaum
eourdcr)
hb nasc (cxccpt Class D aod E rrastcc) wiU bc placod in travs. ffi
Eutedmcot poudcr md boroa potassium uitratc will dso bc buracd in tra:rs TcreFfg
Pteat 78 mixcrwastc (includingStaodadBoostaadHARM Warhcrd) will bc placcd io trays Pireg'r+.r{T
t[sr.a g2
II
llr
III
ItI
!
I
I
TI
E
I
Il
taF€?
la
cizJ
EU'
E.D
al
trto
Eth-E@
E
.g
3l{
t
00E0,,o
8
rtrtI
eC
a,t6
R3aI
I
I
I
C-I
75
g
I
7JA
IE
).ttI
tlaI,
r3
iie
I
II1
tt
u1
T
t
Io
IE
1I
l
fliilr
ih
I
I
3,t
e
TI
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I
T
IIr
iEr
II,.t!
6Itt
t2
tI
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I
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75al-,P
t2
t1
f
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T
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T:T
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,
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IIt
i,li
I,t3
TI
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t
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it
fi
l
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TI!rilIT
it
,
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fuiri
il
E
TiI
1..
T
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I
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E
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I
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fuiri
tliil,
il,<
llt
T1tii
Eil
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ll'
3
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lr
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t!
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a-
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(l) All requircd labcls are to bc flld out ushg a Mireclc holy Pen or cquiydcot (Stock No. 5l-5tnX)4)
86
M.lGridr
U{nGsinEPorrdcr
Aomium Pcrchlonto
Iocrt Propollmt
CoryoEitcfrceafot(SE ll Amtots)
Coqocitc Propottant .
@ulk Amuats)
UDsurcd lligh-cocrgy
Propcllrst (nitdo
cstcer rnd SErll ICBM)(Sull rmuatr - lco
thro 50 lb!)
UmrGd High-cacrgy
ProecltrotE (Bulk
rmuots ia sling beg!
BiDdGr Prcoix
C\uod Higbacrgy
Pmpcllrot (XLDB)
IIARM Wrrhc.d nogdfat
HMX (Bulk emuae)
HMX (Sorll emuots)
Ft sc
Unrdnrae
P:rotcOalsMicrids
Boroo Potrrriun
Nitnlc (t IXlTl)
No. 1 or 2 Dicacl Frd
Noc Rcqufued
Noc Rcqriirod
:
No. I or 2 Di6cl Fucl
Noc Rcquircd
Trirccti!
Noo Rcqufucd
Triroain
Noc Rcquirod
Nooc Roquircd
No. I or 2 Dicscl Fucl
Trircctir
f0l[t MiaGnl oil or
No. I or 2 Dic.cl FuGl
lOW Miocml oil
No. I or 2 Di6c[ FrrI
TABLE V. WASIE DESENSITIZING REQT IREMENTS
OcocosiUng
Mrtcrid
cM-3.1
Issuc No. 12
21 SGptctnb€r Dql
OcccosiUry
Ingtetiqg!-
Eoougb !o corrcr rod
kGGp $rfrcc ret
EoolSh !o covcr rad@ surfrcc utct
Eaoqh io covcr rnd
kccp surfrcc wct
,14 gtl Triecctin por
25 lb of bin&r premir
3 !o 4 gd of dicscl pct E
lb of HMX; do not
stis or rglt lo
ln-$l Tri.cetin per l0 lb of
HMX
EDough !o covor rod
kGGp surfrc! wGt
Eoough b covcr rad
bcp nrfico urGt
Corylctcly So.lrcd
Corylototy sorlc individuelly
urnppGd prpcr
Adbocio C\rp! lnd
CP Crrcr
No. I or 2 Dicscl FEI
r Cotrct Ewirm''atrl W.sb DigPo..l for uy urcrid Dot licd in TSlo V.
,G7.O n
GM-3.1
Issue No. Il'
2f Scptctnbcr DqZ
TABLE VI
EAZARDOUS WASIE FROM NONSPECIFIC SOUnCES
40 cFR 26r.3t
Inertry rod
EPA Ilrzrrdoue
Wrdc Nrlpbcr
Gcocric:
Fml
FOO2
Fm3
Fm4
F005
Hrzrrdous W.sta
Spcor hdo&ortd colvcots nod in &grE sing includiag tGtnchlorccthylcoo,
tsic;hloroothylcac, octhylcoc chloridc, lrlrl{ichloroGthroo, crrboa tctnchlori&,
od chlorinrtcd fluoroqftoc; dl cpcat colvcot oirlrrcc/blcodt usd h dcgrersing
cmtdning, bcforc usc, e totd of tco pcrccot o( Drr @y volure) of onc or mrl
of thc rborrc Mqcortcd solvcotr or thocc colvcotr listd h F0O2, F004, rad
F005; rod still botlon from thc rooovcry of thcsc lpcot solvcots end spcot solvcot
oixorcs.
Spco3 h.lo$old solvcatc inLluding totnc,hlorocthylcoc, mcthylcoo chlorido,
trichloroethylcao, l,l,lticblorocthmo, chlorobcoac, l,l,2tichloro-1,2,2-
tsiftrorocthmo, orthodichlorobcoac, trichlorofluoroahrnc, .Dd 1,1,2-
trichlorccthnc; dl gpcot colvcat oixficc/blcad! cotrhin3, bGforc usc, . lotrl ofta pcrccot or mrc @y volum) of oc oE Drr of 6c rbovc hdojeoetcd solvcots
or ttoeo listd h F0Ol, F004, or F005; rod still boconr fron thc reovcry of
th6c rycat solvcots ud ryat cohrcot Eirtrcs"
Spat nmh.lo$o.tcd solvatc iocludiry lylcoc, rcctooc, cthyl rcctrtc, c6yl
bozoo, c6yl erhcr, ncthyl isohtyl &Gtonc, a-lntyl dcohol, cyclohcxraonc, raddroob dl spcat solvat nixorcs/blcods cottrining, bcforc uso, ooly tho rbovc
ryot amhrlogcortcd solvcots rod e totrl of tca pcrccat or ulrt (by voluoc) of6r or mro of 6occ solvcots listG.t in F001, F092, p66t4, rad F005; rnd still
boiooc froa thc reovc(y of thcso rycot solvcots rod spcot solvcot Eirturts.
Spcot Dmhdo$orbd solvcott including crcsols ud c'rccylic .cid, rad
nitobcaao; dl spcat colvcat tnirturc/blcods contriniog, bcfuc usc, . totel of
tca pcrccot or mrc (by volno) of onc or Dro of thc rbovo mah.logcortod
golvcao or thm solvcats listd h F001, F0O2, rad F005; .Dd still bottoos fron
thc ncorrcry of thosc cpcat colvratr ud spcat solvcat mirores.
Spcot nmhelogGoiGd solvcntr iachding toluo, octhyl cthyl kaoc, crrtoo
dier16&, isohrluol, pyridioc, bcoaq 2+ttorycthnol, rod 2.oitlryrcpcao; dl
pcnt olvcat mixortdbtcodr cotririlg, bcfulu ur, r btrl of l0 pcrccot or Drl
(by voluu) of m or Drr of thc lbovc omhdqcartcd rolvcou c thocc solvcats
lirld iD F@1, FOUI, or FfiX; Ed dill bocoor fto,E thc reovGry of thccc spcotrlmtr ud rycot rolvcat Eirornr.
qns,.r tt
IDdrdry Ed
EPA llrztdoua
Wroc Nunbcr
Explocivc:
K044
1045
KO'l6
GM-3.1
Issue No. lil
2l Sqtclnber Dql
TABLE VI (cooO
IIAZARDOUS WASIE FROM SPECIFIC.SOI'RCES
40 cFR 26t.32
Ilrzrrdous Wrstc
$rroccrta latilcot shrdgcc fron thc tDraufictriog rd procccdng of crplodvcc
Spcat cuton ftrom thc trcrtmrat of nn*ernta conteining explocivce
wracuntor trcrGt dudgcs ftoo tho rDronf.chuiag, fotuuletion, rod lording oflc.d$.sd inirirf '.g coryormdr
t[$2D t9
GM-3.1
Issue No. Ul
2l Septonbor l99l
TABLE VII
CHARAC,IERISIIC HAZARDOUS }I'. ASIE
40 cFR ?st.2b?s1.24
EPA WASIE
CODE
Dmr
DW2
Doql
WASTE DESCRIPTION
Conocivc
Reacive
REGT'I.AIED
LEVEL (lnq/D
nOeolat < l4O'F
pH32 or > 12.5
Unstable, CN or S
(Undergoes violent
change)
D004
Dms
D006
Dofl
Dmt
D009
D0r0
D011
D0t2
D0l3
D014
D0l5
D0l6
D0t7
D0lt
D0l9
Arsmic 5.0
Barftm 100.0
Cadniun 1.0
Chromium 5.0
Lead 5.0
Merory 0.2
Selenium 1.0
Silver 5.0
Eodrin 0.92
Lindane 0.4
Mc$oxyc,hlor 10.0
Toxryhone 0.5
2,4-Dichloropheooxyacaic Acid @,4-D) 10.0
2,4,5-Trichloropheooxlpropionic Acid (Silvex) 1.0
Bcozcoc 0.5
Carton Tetrachloride 0.5
g!n'r.O 90
GM-3.1
Issnc No. lll
2f Scptcmb€r f99.
TABLE YII (com)
CIIARACTERISTIC HAZARDOUS WASTE
/m CIIR 261.20-261.24 :
EPA WASTE
CODE
REGT'LATED
LE1/EL (ms/ll
0.03
r00.0
6.0
200.0
200.0
200.0
200.0
7.5
0.5
0.7
0.13
0.008
0.13
0.5
3.0
200.0
2.0
100.0
5.0
0.7
0.5
4(n.0
2.0
0.2
D(n0
Dg,.r
Dgxt
DO23
Du2.4
DUls
Dfils
DUn
DUt
DU2g
D030
D03l
DU32
D033
D034
D035
D036
D037
D03t
D039
D040
DO4l
D0/,2
DO43
WASTE NFSCRTYJTON
Chlordane :
Chlorcbenzene :
Chlomform
O-cresol
M-crcol
P+resol
Crcol
1,4-Dichlorobenzene
1,2-Dic.hloroethane
I,l-Dichloroethylene
2,4-Dinitooluene
Ileptachlor (and its Hydroxides)
Hexachlorobenzene
Hexachlorobutadiene
Ilcxacilorahane
Methylethylkaone
Nitobeozene
Pentachlorophenol
Pyridine
Tenachloroethylene
Trlchloroethylme
2,4,5-Trichlotophenol
2,4,GTrichloropheool
Vinylchloride
,Darr 9t
WASTE GENERATORS:
Strategic:
CONTAMINATION RANGE:
Solvents
1,1,l-Tricblorcethane
1,l-Dichloroethane
1,2-Dichlorocthane
Trichlomethyleoe
1,2-Dic.hlorcethylene
Dlchloromethane
Trichlomnothaao
Acaone
TABLE VItr
NG WASTEWATER
M{93, M694, M-191, M-193
DDtr
GI
Solvenc
GM€.I
Issuc No. Ul
2l Septcmbcr DqZ
DDII
Methyl Ethyl Ketone
Isopropyl Alcohol
2-Btftaml
1,4-Dioxaoe
1,3-Dioxolaae
1,2-Butadieoe
Nitromethane
Butylene Oxide
Maals - EP Toxic Other Maals
Barium
Cadmiun
Chromium
Lead
Silver
0{.(n
0{.2
Characteristics
o{lt
G5.0
Gl0
7.5-t.0
500-3m0
1m-2m0
350-3m0
G2000
0-100
0-o.l
o-1fl)
O"tO
Glm0
Alumimm
Boron
Calcfum
Copper
hon
Magnesftrm
Idangance
Molybdeoum
Nickel
Potassfum
Silicon
Sodium
Strcmium
Titanium
7fuc
G20
0{.4
G200
G2.0
0-200
G20
o-1.0
G2.0
0-0.3
O-()
G200
Gr00
Gr.0
G3.0
o-20
pH
Toal Solids
Supded Solids
Dissolved Solids
Aomonfum Perchlorue
Ntffic
Nttrite
Chloride
Sulfate
NG
oil ad Greasc
9rc7.n v2
TABLE D(
HII,D( WASTEWATER
GM-3.1
Issue No. ljl
2f Scptcmbcr 1991
DDIB
o-2.0
G1000
WASTE GENERATORS:
Strategic:M-570, M-571, M-5T1, M-573, Sd)t, M-701, M4V2
CONTAMINATION RANGE:
Solvents DDtr Solvents
I, l, l -Trichloroethane
I,l-Dichloroefrane
1,2-Dichloroetbane
Trichloroethyleoe
1,2-Dichloroethylene
Dichlorome&aoe
Trichlommethane
Acetone
Metals - FP Toxic Other Maals
G20
G500
Mcthyl Ethyl Kaoae
Isopropyl Alcohol
2-Butanol
1,4-Dioxane
1,3-Dioxolano
1,2-Butadieoe
Nitrcmethane
Butylene Oxide
Buium
Cdmium
Chronium
Lerd
Silver
Caaracteristics
pll
Total Solids
Snspcoded Solids
Dissolved Solids
Anmnium Perchlorate
HMX
Oil strd Greasc
Nitrate
Nitritc
Chloride
Sulfat€
0{.01
0{.1
0{.2
0.0.4
7.5-9.0
5fi)-100,000
50-150,000
4m-1000
Gso
10G50,000
Et2%
Gl0
0-150
G3o
Aluminum
Boron
Cdcium
Copper
hon
Magnesium
Ivlaoganese
MolyMmm
Nickd
Fotassium
Sillcon
Sodium
Strontium
Titanium
Zllc,
G3.0
0-0.2
Gl50
Gl.0
G10
G50
0{.4
0-0.3
0-0.s
&.20
G20
Gl20
o-1.0
Gl.0
G2.0
rn-r.G 9?
GM-3.1
Isqr No. Il
2l Septcober 1992
WAS'IE GENERATORS:
TASLE X
MTXED CI.ASS I.T AI{D I.3 WASTEWAIER'.'
Smegis Opcrationr:M-16, M-10, It/[42, M-115, M-15, M-126, M-14t, M-504, M-519, M-
s2l, M-s?s, M-'U, M-526, M-52t, M-590, M-59t, M-593, M-595, M-
59t, Mdqi, s-501
Scicocc & Enginocring: I-lO, M-9B, M-{3, M-56,l**!iE; M{3, Mff, M-201, Ittr-?gl,M-?frg,
Mtlo, Mal4, M-21t, M-t23
Spcoc Opcntionr: M-20,M-N2,M-U,M-8,M-TI,M-52, M-:X)9, M-32)
CONTAT{INATION RANGE:
Sels@
I,l,l-Trichloroc&roo
I,l-Dic,hloroctroc
1,2-Dichloroctrno
Trichloroc&ylcoo
1,2-Dichlorocfrylcoc
Dichloroncltroc
Trichlomnaheoc
Acclonc
@
GlS(x)
G2m
G5.0
Gl(x)
().3m
o.sn
G5.0
G2m
Solvcng
Mcthyl Ethyl Kaorc
Bop,mpyl Alcohol
2-Dxrool
lr4-Dioxenc
1,3-Dioxolaoc
1,2-Butadim
Nimnaherc
htylcno Od&
DDtr
GN
G40
&6(x)
G2m
0-250
().250
o-30
G30
Mctals - EP Toxic
Brdun
Cdntum
ChronftmLd
Silvct
0{.2
0{).4
GICT)
G2.0
Olhcr Mctals
Alumirun
Bomn
Crlcftm
Coppct
Iton
tvtegecsiun
Mrngnrsc
Molybdcoun
Mc&al
Eotr$iun
Siliooa
Sodfun
Strcntftn
Tltroftm
ZtE
&25m
o-3m
o"@
G20
o-4q)
G25o
GZ)Ctencrcristica
pH
Totrl Soli&
Supcodod Soli&
DirrolvcdSoli&
Annoniun Eerchloratc
Niffio
I\titsilo
Chlori&
Sulfuo
TOC
3.9-10.5
Grc,(m
O'rc,m
G25,(x)oGa),m
().sm
Gl0
Gnx)
olSo
G35(n
G7m
&20
G7m0-lm
Gl5,m
UN
G2(x)
Gl(x)
re'?.ra 94
' GM-3.1
Issue No. Il
2f Septcmbcr 192
TABLE XI
INERT WASTEtrTATER
WASTE GENERATORS:
Stocgic Opcrations:
Spccc Opcdiol3:
E-512, E-517, M-50t, M-179, T-21, T-lL2
A-1, M-2, M-55, M.:lZ), M-305, T-1, T-9, T-U,T-gl, M-314
CONTAI{INATION RANGE:
SolYf,tr
I, l, l-Trichloroethaoc
Irl-Dichloroc&roc
lr2-Dcf,loroc6ane
Trichloroahylcoo
1,2-Dichloroahylcrc
Dichlomnc&roo
Trichlommaharc
Acaooc
Mctelg - FP Toxic
Brrftrn
Cadniun
Chroniun
Lcad
Silvct
Ohcr Maals
Ahminum
Boton
Cdciun
Coppcr
Iror
tvtryecOun
Ulo3loccc
Molytdcoun
Ni&d
Fotrduu
Silicon
DDD
Gr(m
o{()
Solvcarc
Mcthyl Ethyl Kctonc
Isopropyl Alcohol
2-Buuaol
l,&Dioxeoc
1,3-Dioxolano
1,2-htadicno
Nitomcthanc
otf,cr Maals (Cont)
Sodium
Siontium
Titrnium
Arc
Charrctcristics
PII
Totd Solids
Surpcodcd Solids
Dircolvod Solids
Aomoniun Ferchloralo
Nitntc
l{itsito
$tfrfic
Chlori&
TOC
oil rod Grt.sc
DDD
L.,
G3.O
G10.0
0{.3
Grz)
G300
()-l.0
Gl(x)
(}.lz)
G10
Gq)
G30
GZ)
G30
Gl.0
G3.0
G4.0
G50
o.g)
o-10
G2m
G200
o-50
G25o
().50
().20
o-3oo
0{.4
G2.0
G5.0
6.().9.0
9qL2O,(m
3&15,0q)
4(xI5,000
G2m
G3
G3o{)
G2(x)
G3,5(nw%
r[s7.6 95
TABLE Xtr
AP WASTEWATER
\TASf,E GENERATORII
Stmlcgic Opctalions: F'fi2, M{06, M-629. M-13
Spoo Opcrationr: M-174
ffi
CONTAIT{INATION RA}.IGE:
Solvcntg DDB
G300
G5
().80
(}.r.0
G10
Maals - EP Toxic Se-Meds
Buftn
Cadniun
Chronium
r-C,d
Silvcr
I , I , l-Trichlorocrheoc
l,l-Dic,hlorocffroo
1,2-Dichloroc&roc
Tridloroc&ylcoo
1,2-Dlchlorocrhylcoo
Dlchlomncthrno
Trichloronclhroc
Acaooo
Solvcats DDtr
GM-3.1
Issue No. 1.ll
2f Scp&mbcr DqZ
G3.0
().30
0.60
:*
Mc&yl Ethyl Kaonc
Isop,mpyl Alcohol
2-But ool
1,4-Diorerc
1,3-Diorolerc
1,2-Butrdicoc
Mtmnctharc
htylcoc Oxidc
0{.(n
0{.2
Caareccdstics
pII 6.3{.6
Totrl Soli& 6:XD-2m,(m
SrycoOoa SoU& lm{mO
Digolvod Soli& t!rO-m,(n0
Aomonfun Pcchloruc 5ff)-200,m0Nttilo G250f$Eito GlmCblod& Gs(I)Srlfito O.fl)TOC G30
Afuniaun
Bomn
Calciun
Coppcr
Imn
Ifiryncsiun
Itrfrogaocsc
Molybdcoun
I\tic&el
Fotrcsiun
Silicon
llodfun
tltmntiun
fitroiun
ztu
o-4(m
0{.5
().s(m
Gr0
G6m
GlSm
Gl0
0{.5
0.2.0ofl)
o{(x)
o-3m
Gl.0
G30
GZ)
gnOr.5 96
GM-3.1
Issue No. I!
2l Septomber 1991
Cloiel
TABLE XItr
REFORIABLE QUAITTmES.Fcdcral
BATUBg)
Uteh:
RO nbftqt
Ao@oo
AmnonftrnHydroxi&
Arbostos
Bcozcoo
tuyl Alcohol
Crfton Diculfi&
Cbronic Acid
Ethylcnc Glyool Monocthyl Ethcr
Ilydnzirc
Ilydrcchlotic Acid
Ilydmfluodc Acid
Mccury
Mcfrenol
Mcthyl Chlorcfurm
Mcttylcoc Chlori&
Mcttyl Bhyl l(aoao
Mcrhyl Ethyl l(aonc Pemxidc
Nitie Acid
Itosphoric Acid
Ptosphorus
Fotr$ium Hydroxidc
PyridiDc
Sodiun Azidc
Sodium Hydmxi&
Styrcoc
Sulfiuic Acid
Tohtcoo
Tolum OlisocyeDdo
Vlnyl Ctlori&
Xylcoc
Uolistcd Dml
Unlistcd Dm
Udistod DmB
Arlcoic Dm4
Bufin D(Xlf
Cdntun D(X)6
ChroniunDfiIT
Lc.d DCIE
Itlrrcury Dm9
Sclcoftm D0l0
Sllvct, D0ll
5,WWn
l,m/454
l/0.459
tol4.54
s,wtx|1o
t@14s.4
tot4.54
l,wl454
rn.454
S,WlXnO
t@t45.4
v0.4545,ffitun
l,m/454
1,000/454
S,mpit?,/Il0
tot4.54
l,wt454
5,om,l:Urc
llo.454
I,m/454
l,wt454
l,m0/454
1,0(p/454
l,m/454
t,000/454
l,wl454
t@t45.4
vo.4s4
1,ffi7454
t@145.4
100/45.4
t@145.4
uo.454
l,m/4!t4
tu4.54
1u4.54
rn.454
l/0.4t4
tu4.54
Ln.454
xr,/t@
zfrnoiJ
xnn@
ND,/I@
2.2nmn@
xI,it@
2,0,n@
NDII@
xNt@
22,,ilqJ
xrut@
xI,,it@
xr,/t@
xI,,/t@
xNt@
2frll@
?,,J,lt@
2,0,noo
2@,n@
2.2^
2.211
zim,/r@
?2ilt@
2,0,n@
2g,/n@
2g,,nqJ
2,,J,nUJ
?frlr@
xIJ,/t@x,,/tfi
xI,,/t@
?,tritqJ
xrulqJ
xnn@
x,yr@x,,it6
?,,J,trUJ
t,,itqJ
x,J/tqJ
lrre7.t n
TABLE XItr (cont)
REFORTABLE QUA}{ImEi.
9[oicd
Fmr
Mc6ylcoo Ctloride
Irlrl Trichlomcth.oo
Chlotinelcd Fluorocrrbonr
F(xIl
Mcthyler Chlori&l,l,l Trichlomcthaoo
Fm3
Xylcoc
Aaciono
Butyl Alcohol
Mcth.ool
Fm:t
Toluonc
Mc6yl Ethyl Kaooc
Cubm Disulfidc
Isobulond
P!/tidinc
. Onlv amlics if spilled in thc Statc of Utah.
Fdcral
RO nb)
tu4.54
l,m/454
1,0m/4li4
5,Wrmo
tot4.54
l,0q)/454
l,m0/454
to/4n.4
l,0q)/4tt4
5,Wtmo
S,WrEnO
5,00p,t22ln
t@14s.4
l,0q)/454
S,Wrnrn
tm,t45.4
5,m,t2il?O
1,m/454
GMt3.l
Issue No. lil
2f Srytea$er DqZ
t&[
RO flbftqr
xrut0/
?ir,/rqJ/
xwrqJ/
N,,/IqJ/
?,I),itm/
xtr//tm/
xIJ,itm/
?,on@
2,0,trc/J
NIJ,iI@
xIJ,it@
?,,Jn@
xrut@
xr,itop
?,f,tr@
Np,/Io,J
NI,,/I@
?frn@
t[ozr 9t
Nanc
Flennrblo Gs
Non-Flsnnrbb
Conp,rcsscd G,
Foisoaous Gar
Ftannrblo Uquld
Flennablc Solid
Sponuncously
Conbustiblc
Dragemus lVhca Wa
Oddizcc
Orgnric Pemxi&
Mcthyl Chlorofotu
Poisonous Metctial
Conosivo Metaial
All otha Hazrdous Irilatcricls
TABLE ]gV
DOT IIAZARD CI.ASS
Ne.
2.1
2.2
GM-3.1
Issuc No. lil
2l Septcmbcr Dql
I$cl
Fteonrblc &r
Non-Flsnnrblo Gas
Poisonous Ghs
Flanmablc Uquid
Fhmnablc Solid
Spontrocously Conbusiblc
Dragctous Whon Wct
Oxidizcr
Organic Fercxidc
Kccp Awey From Food
Foison
Conosivc
Clrss 9
2.3
t
4.1
4.2
4.t
5.1
5.2
6.1
6.1
E
9
,:E.7.9 9!t
GM-3.1
Isguc No. Ul
2f Scptcnbq l9tl
$.aDraOtaaatoaor!'I'lrOta
cotr.aa
ata, oaacarrroo rr rart3 uaa! E,qao,
-1 ura,rornreoourcomEcttY
I rmstErotrlcrqccocoRaEcttY
i erceEostsr,t.,,.t
ll rcraeatnuocsalrnzlD
i-'i r€tlrrccotoiluETPEnri{
! on*n
tIOrOCOirCt
aacafarloE'ln
oncgtDr€ o{ r{ow ro tBttal ri.allilrs tor 0(3to3rr Aru Four'o N n{€ GENERAT Ptoc$s ngtRrgtErC[ 1!.06tOt3^ll,€rnJCnOB80ttill5llr.rlrEil^tt. txl3 OOClJrr€xr ri[Y 8EO8?Alr.EOFIOInr€ PnrtCt,lVqJnAegA.CEll€n^tilGlLlf,BraAtEllL VALSOSCFiOlrlOlrani€ iil tlFl^rHe^fniAogAttTlngrfi.Gtog tr..as0. cctlmct 6tut6r.5na u^sfl o€tc]s^r rF you NEEo ^ootftota Har.
Crr atrari.O
roDrai{,cr!.rl
9Er.to
,r!it t.ta-r, taa
lm
FIGT'RE I . WASitE DISFOSAL NOTICE
GM-3.1
Issue No. lil
2l Septarbq 19!12
OOT Hazard Class l:bel
DOT 17E Ctos.d Top Stcol Drurn
DOTllard Clalr Ubd
rg.
DOTCIo!.dTop Poly Drun
FIGURE 2 . DfII I7E (CIPSED TO$ AryP POLY DRT'MS
rearor r0t
qM€.1
Issue No. Ul
Septanrbc 1992
Chime Oamage
Deep
Creasas
or Dents
Chimc with deeP, sharP ctoase
or bnak
Hole or gash in head, bottom,
or bodY
D*p, sharp crease3 or dentg in head,' bottom, rolling hoops, or bodY
SludEe, Uquid
or Resldue
Hole or Gash
Eulgar
Scal Broken
Top or sides contaan an ercessive amount
ol sludge, llquid,or residue (e.9., paint)
A@r.
Bulge ln head or bonom thet Flange cractc4 thnads
dlct-ott! tlrc flanEc or chlmc stripped' or6d broren
FIGT'RE 3 . DRT'M INSPECTION
,rc,.4 rg2
ll^zAnDous
WASTE
-a DOT-17t1-SPec. No.
o DFF-SYmbolol Mlr.
o 20 Gauge ol BodY
18 Gauge ol ToP
and Bottom
55 CaPaciU in Gallons
75 Ycar ot Mlr.
o STc-slngte Trlp
Container
EXPLANATION OF
iJ|ABKINGS
20 18-55-75src
DFF
DOT-I7H
GM-3;1
Issue No. Ul
21 Septcnbq 1992
Bung
Top Head
Gasket
Seal
Chine
(top)
12-Guage
Bolt Rlng
5/8-in. Bolt
Lock Nut
Vent
Folllng
Hoops
Chlnc
(bonom)(on thc@
FIGITRE 4 - DOT l7E (OPEN TOp), 55€AL DRt M
,E.ro l03
Wagte Flammablc Solvent Rags
(methyl ethyl kctono)
Solld
(clry)
Label
Flammablc Solld
(rrry)
Lebcl
Wastc Corrosive Solld
(alodine)
GM-3.1
Issuc No. Ul
Seplcmbcr Dql
Corro-
sive
Lab€l
t8.!!t
Al! Othcr
l{arardous Material
Label
Wbstc Flammablc Solvcnt R.gg tfUrctc Nonflammable Solvcnt Bags(utonc) (m.thyl chlorolorm)
FIOT'RE 5 . Dqf POLY DRT'M PREPARATION FOR WASIE NAGII
lrlaEut
WASTE
--
RAIIIMABLE SOUD
FTAMMABTE SOUD
t[or.!0.l(r
GM-3.1
Isgue No. Ul
2l Septemb€r 1992
HAZARDOUS WASTE STORAGE CONTAINER INSPECTION
lu
frrt6r r&At TTUTE
tlo
.riiaout .Aitral ot oractq,iac[t naOoJfi.'fitD
L
I
a
I
a.
.tottotv u?cJl
comrt3
t.
t
t
a
cta-a-rrit-
crurESrImru!.o,llrlat otoollllIlatS
oaat
FIGT'RE 6 . IIAZARDOUS WASIE STORAGE CONTAINER INSPECTION
6'r.E 105
rl
!
t
tttc
I
i2
;EIePt
$rE
lEt
16i
EilI
EIE 3
HEg6E ;.
ir [';
ggIfl
'.1 r,l ..1 a d
Et
fr$
lEs
iii
HUH
g
oj
dr!
6{.aal!
o
.!t
;
e
TE
6.rCIG;ieE'oud665
.,da
,L
I
-,
I
TI
d
.,
a)
r,vor,
{
3
,I
G
t{.t
+,iI
1J.rl
i-tijI-o
3i
H
=EEB?I5fir
EH$
Efi!'
qTEil
)
I
\
E-
EP
frH
$$F
EEfi
Hgq
)
)
)
d
I
#ff$
\
I
\
J
)
\
-i
FE:
$ffi
\
\
a
;trl
l'rJi J{lij
.i :.[
;ijjii
ii;
I3
$rc
rie
\
\
\
oeJ
IB
58"2loL
EI$P6EgIE
$ffi
I
I
arl
t
tIa,
.!
{r,I{
tili
:!ttat
IaaI
aI
a
t
a
ta
{,ttttt
al.JFIr!. t:fii.li{I
3ri:-I!
H
OL
grlE
=:<-
3fiau
EHFq
EFgB
F$$n
\
\
\
\
t
I
\
t
;
I
iI
oIoI
it
i
G
i
(r.
V.
a
=
2!1
6lttr6eg.:)v,
fl
r{
ttrl
al
a{
:
od
Irt
o
.L
ao
I
(J
o-afa
s.i
Grt
J
J dj
,dr!
\o,..ri
.,9:3.rF
\
I
I
I
\
\
\
\
\
\
\
\
I
.iild
HGIN.iie
E;E
EJ oa.E
t
ao(J
H
E
A2o
E
Ha
a
5o)ip
D(:,
E
!
GM-3.1
Issuc No. l.ll
21 Septcrnbcr 1992
llll
I li tl
I
I
I
II
g
t I
U
3 ll
e
I
L'Ag
ET
rii
T
U
e
U
3
rii
3
EaI
Up
t E EoIaI
E
tot
Eu
oGooll|G
oohaa
=o|ro
=t
oul
c.I(t
d!t
=ur:
=oE
=lll
ia E
5i
:T:lil.:Et;!l 3Iu i
FIGT'RE t . E}IVIROT{MENTAL SAIVIPI.E CHAIN OF CUSTODY RECORD
,D7.N'to
tac
I
i
I
II
I
tr
tr
Ti
D
t
II
tr
,T
tr
a
itt
E
diu
tI
tr
t
t
tr
i!
U
tu
I
tr
t
?
Io
I
u
I
U
I
D
I
t
t
p
?Grll
Ito
I
tI
!taaJ
tr
lr
!u
I;
tI
ttt
aIl
t
IIIt
at
E
Io
tr
!
tr
!
tr
,I
D
tI
tr
t
t
t
I
t
I
I
korllJ
TLoEo.t
Tat)
F{ 'Ncri t{
8i
t
Eo
6t
a
HltocA
H
B9'DI
3
f;
;
B0E
I
H
GM-3.1' Issoc No. Lll
21 Septcmbq 1992
ct*rcorqrEr
slf
fcr! !ro !rc
c'lrxu lro !rc
i{rrtcr lrrl !rc
trm lve Qrc
ratlCar..nlt rOrUl,EEIt
lErca.nlrt l,'HTE!l
ETCtr'
fglirglE?
tVESOnr'€l Pctctrrr I rgccxrtm[aJtat I (rarlaJr.t
rOato
FIGI'RE IO.IIAZARDOUS
t09
GM-3.1
ksnc No. 12
21 Septanber. f992
11r...labcls ArcPhd on Orums
dwoil Statlons
aaxl
To Br PLc.d O,c Slblllb lEnbrrl fUs ld Wh.n Orumll Drdarrd fult.nd PLc.d on r Ooci fr Oilt Plr[ Olapo!.|
EIGT'RE II . SAEIITIE ACCT'MT'IA'TION AREA DRT'M PREPARATION
COTTENIS lilerrrt E+yrl l(coane.
fq.rr t.rra.rf ,.c- ,Il r;vr
HANDLE WITI{ CABE!
. cofxlrs t{Az^Root B on 10xE lJu snE3
21EilERGENCY FESFOMiE
Gt IOEBOOKNO.
t
IItt
APPROPHIATE
DOT HAZAHD
CTASS LABEL
HAZABDOUS WASTE
FEOEBIL LJIW PROI{lBrTll ITPROPER OtttPGSALIF FOUNO. CS{TAfiTHE NEAREST POUCE
OR PIJBUC SAFETY AUTI{ORITY. OR 11{Eu.tt ElwtnoNr.e{ra pnorEgnor{ AGE}Gi
l,lt4t El^--Jh ll-!).- --rt^lfrt+Ll lfLl ktl.-t' l-ll-tl
fiFEflhl4r ml;1 E-lgil-
-@rr4391_GENENATON NrcRMANON?73*em,oEII"kclDrt--rE.I.rltta nrrGtoro' l,lEt, mlxtE
-rtt.aa
- loillr rrrrr oell.lT
,E-aatEN
gc5oaa
Oaao
aa
l}aaar}<ts<><ts<D-(}.>.-<D l}<)-<> ---<.> a.>--(} O
a
aa
ao
O
o
a
a
o
,[$r.llo u0
GM-3.1
Issue No. Ul
2l September 1992
gH)ay Dock Drums
Thacc Labels Are
Placad on Drums
at Work Statlons
lBatao
FIGT'RE 12. gO.DAY SIIORACE AREA DRI'M PREPARATION
APPROPRIATE
DOT HAZAHD
CI-ASS TABEL
HAZAHDOUS WASTE
FEOERAL tAW PBOHIBITS IMPBOPEH OISPOSAL
IF FOUNO. CONTACTTHE NEABEST POUCE
OR PUBUC SAFETYAUTHOFITY. ORfiE
U.S. ENVIFONMENTAL PFOTECTIOT{ AGENCY
VtJt Fl^--Jh ll-l).. --^t-lnt4-l Etl-t Ltf.-t' l-tl-tl
rrr.cr- 1 E ,t111|1. rrn ttf.ltl!atf''/l,,6
mflOr..11l nn l.}- rB- l(I!-z f,.-!, F-tt-to r- &ilrl-
GENERATOR INFORMANON
7%€wa,oE-.rrollD.IC,llU'tI-io..lHlrl$g r.!-t!l?ior€. rrurlt, mrgr?ro.-
EI'CIt rlr-
aa
Oaoo
a
qlsztn llt
GM-3.1
Issuo No. ljl
21 Septanbor 1991
IJST OF APPEI{DDGS
APPEI{DD( I I.ABEIS, MANIFES'TS, AI{D
ASBESTOS RECORDS
APPEI{DIX tr DISPOSAL OF E(CESS
EXPLOSIVE PROPERTY
APPEI{DD( M EPA PAII{T FILTER LIQT'IDS TEST
Plss
l13
l4l
ro
g[!Dll.ll2 tt2
ATFENTDT'( I
r.ABErS, MANITESTS, AI\D ASBESTOS RECORDS
TABIJ OT CONTENTS
GM-3.1
Issuc No. 12
21 Sqtcmbcr Dql
t20
Page
SeRilX I,I/rTFn$r T+€ (re 0878) tlND IN
scRAP LABEL CIC 164) Ar{D TNSTRUCTIONS . . . ..
IIAZARDOUS WASTE PROPELLANT LABEL
GC t159) AND'TNSTRUCTTONS t2t
HAZARDOUS WASTE r-ABEL CrC 718' Ar{D TNSIRUCTIONS r22
COMMON HAZARDOUS TITLES FOR COMPLETING
HAZARDOUS WASTE LABEL t24
SYNONYMS FOR COMMON MATERHL NAMES t25
UNIFORM HAZARDOUS WASTE MANIFEST AI{D INSTRUCIIIONS 126
ASBESTOS I.ABEL 133
ASBESTOS WASTE SHIPMENT RECORD AND INSTSUCTIONS t34
wAsTE I-ABEL CrC u5) AND TNSTRUCTTONS t37
EMPTY DRUM LABEL (rC 7711) Ar{D INSTRUCTTONS l3t
suMP ACCUMITLA'TrON RECORD AND TNSTRUCTTONS (ST 9062)
SATELLTTE TTAZARDOUS WASTE r-ABEL CrC 8lm)
139
AI{D INSTRUCTIONS I4O
WASTE DISFOSAL STEPS: t
1. Consult Hazardors lilaste Pr,ofile Data Sheet fiIWPD), Material Health and Saf*y Instrustiors
(MHSD and Geoeral Process Instnrctions (GM-3.1) for proper waste disposal piocedures.
2. If waste is a raw materid or a componeot, use Scrap Tag (IC 0878 or SP 0fr0 system to
seod items to M-136 for disposal.
3. If waste is a waste propellaog explosive, or pyrotechnic Eaterid, it mrst have a llazardoru
Waste Plopdlaot lebel Crc tl59) asachd to-&ch cootainer, in ddition to any other required
trgr or labels.
4. If waste is hazardors, use a Ilazardors lYaste Label OC 7lt, for offalant disposal.
5. If wastc is mohazardors, rse tlc $rase kbel CIC 815) Systeo.
6. If wastc is comminatcd sith asbcsto3 and mrst be shippcd on public roads o 6e Main Ptam
6r disposal in the asbestos treochcs at the M-336A Sanitary l5dfiIl, rse the Asbesos lVastc
Shipmeot Record CIC tl7r.
,[}rt.rD l13
GM-3.1
Issue No. Ul
2l Septembq 1992
IICSAP IIATEilAL TAG
GqlE@@
oooooo
AL
-I
I IT
ooaooo
[l3rnElil[lt
r. ri--.t-d---'-'-tlr-r.--m- il![r-rLa.rt.Cttlr-
ahtr-t-tLrb-rt'-L..'Gl}e
a fl
--i-r-aE -L-t'na . illDtcllr't-r---s--1--
--t-GGrcr
aE
----t--r-,.r-----r----
-a--...a.
tatEooil
--1l--iF-ra-r-l-b
tGl--A-a---elts,
-
-a -.-a-
-Ir'
lt
-r---------------
---
--Ol--l---'
--rr--ra-l.-\tar---ro--"-b
-----L---
taFF-rt---tEt
----a-aa'-'l-'-
-r-r-tl
lr--'ll-'--E-t-l-ral--
O
-a--
t3
ta
---cal
ta
l--rla--t
SCRAP
fubb€
o-
ff-
-
Oo
-rt
'E
caura U,t
GM€.I
Issnc No. ljl
2l Septcmbcr Dql
w
€eta*eeg78)
Ths Semp Motaid Tat b usC cer seraFp'-g mrv raterids ea plant edy' The tag eeas'se ef tre
Fd?r
a. Whitc label (original goes to ttre Mateiial Review Board).
inea
Whoe o lete ilmb€r ef €oatei-
vil eeelibe go ryfe(o) ef Cnee
lletrts
€erietoto tmtre$orc for filliig
l. TyAe of Scrap
| ff-otcid b hasudeus; ehs€hh^-erdour, illre; €enpl*e o PogofCeus Wolte L*ol;
iFeecca+
ina
N€lB
ffi
Usc numcric datc: MM-DDIT (e.g., 1-15-90)
3. finc of scro. Use nilitar!, time (e.g., l4{D)
If plad sciap, eot€r cost cente( processing 6c natecid at the time it was scrappcd.
rsll.tt l15
GM-3.1
Issno No. Ul
21 Septanbc 1991
ffi@
-TC
8Ct4.
6. Describe the iten as entered on Shop Traveler or Accept Tag.
7. Enteroart/socknumberon Shop Travelr or Acceot Tag.
aumber Gdicit numb6, e.9.,IIB520 00 01)
If Shop Trarrelq is nor ayailable, enter 'N/A.'
or Acceot Tag.
unevailable,emer "Untnowa' and provide a explanation.
l3; Fer t-Flr-C s€rap; oat{ *!U m-ber:
For plaooed scrap, enter 'N/A.'
MHSI under Plotection.a
twI5tf*cn * sctt ,c hfnffi Wcplr- Tlctlrh (il 136) wtu '
Wcrlra l}crrpi/t' en tctta n efpi* cefr' tefrlilitdflc Ciffesd b, tlt
etckry-ff+\E
14. Signaore of person initiating the scrap, tel@hone extension, b.dgr number.
15. For olaoned scrao onlv. simanrre of Foremao. date. badce number.
16. Leave bla* - organization find disposition will complete.
t Ssed whito eepy to Mrteril tevieroeord:r floe9 p'-'€adbeord €opy h'eevr"ffeig't 5 b, l0 '-: siFleek rypo beE te pret€€t fremscadren; teFe sh[t
ehel
qEu.lL u6
GM-3.1
Issuc No. 12
2l Septanbq 1992
w
etn*++s78)@
t. rrtl
CouurDlEalr,l!aroat-,t:!tr
gOr.tt t
tr!
oart
r{
Orrrmr \E orrmr
SCRAP MATEHIAL
alaa-.o acta,iralr oarE3lrEia
Oe Or Oe Oo
ma aclD
iartlEt|6
rq,66ana O
Earairatra-
irtgtB3l.r50Il
tr
,A.E E
iMtaCatrinari arl
q?
tt-ro, rcraa n
Jff.'U"O.rt IEO
NO. sP 01120
L' IJO
oilEA
rrtrtpttt
I-ro
IITO
to
\V7fub€cmtu
flce aatptg '.
nr!E'
El er,rlo
tr rftr
€rtlrttor-
, {Earaa 6aaaEE- rlotsEra-! itE Eti.|EtSor-E
nua - t E .|r.! i[lt rr|..ir t.q lrra !-f dtEa6.a. n a^rlo - lraG(nEsanrll.lEac,u}.trxlEaoE.
3. !€PECtlOll StAfat - t l1g111arbEErf arrrggt Ea;;aOaC,5. rrlE .tl.rS tara E lrrrE rgta,?lta O!SCa|PT!O..- ldrrrrlrtcrt ilrClhri i
ua, co:t artE .ntEE COI,o utrtsom. &rr,tAmtrruEEr.
tO qJ ,lrfty u^a-trEj-torll'|nrrrrrtlnt qrra.ttlEta. ac.t f!t ac ia-t at-,. a,I
la rOrtCOrrFOetlAr€ESOUAwr.fi€l to. - For uwrn rc'l, rlrs. Jilo.Esruwuqrrrolmirr;6r;;; --
r. !!!!!!!! rol trlrtrry E r ..rtrrt un. rr e,in n r tr.EIIIOEIE
t!. ltAl3O,{ FOt SCnArOt3rG3A OSadnnnDnCE - t rrlrlrn rEoEnanrraut tcIl1
lgt^omt rurcr 0.a! arEa t rtrF,,ar,au! t.. orottoatlrrsarr .G,lla" lrnAtlD !Y. An. IAOGC T0, - r- Irr llir.cr].!rrrr!.
---=:E-GraE-c-tt E-rlr llrtaot Eo ry. o^t!.r^mE ro. -Fcurryr orerlrrr!D!9. rrnro.. Scr1 tef o rrri ;-lra ;; ;;;uEtrrao *raat1 txoolrtEftiE EvauAnot ar. sorrnn oA[. or1 l^Ioor io. _ff;
t7. tla oEacmor.. s'Er|rrura. o^t:. aloBa ro. -oEErItE-rE E a!!E.an r r I 1;r1a[-:il,ItrB -.rya trE rrt- aryrlrc ErrE n.=rIlE!:Gr = qrr-_{Efar!3
CNGi.E.
tl. SEll UtOttO. -htE.,:t tirrtr 't'r d .cnl!r, railtr. It
AIorEaarfr.q ,UA.,rt ,&a
c.rrrt r.iftaoOOr
tao.-rEErrlrlarE)rlrt . €rrltgl
,Ar?.stctcr(r.o.tt]E !I}E.|Dr ,tfl3c acrEIi, fiua,lll.I oaott.tYolr(usEt co!,,ea-Proq.E cortrq.- lf,atr, aila,trIt
1..9.
,toJcct r.l*t lElr(ri tlr iraEE:UT ,EtaEr.
t.06i6ra.
ltar.lqJut.
Sorron.A iwIlO,El
A LoErqtrIlo..ottcna.\rreoaaalnarr. -
C O5urar.i..A Clrrmrror.-..t tsrr*rE..
EllJl?tn
GM-3.1
Issuc No. Il
2f Scprat$or f992
w Ecq.-SD-6Et9I@
Fe SeroP Motu'C Tat is urC for !€reFp'-g row r-terids ea plmt edy' T.e tet eonsbr ef tre
portsr
e.WLito label (oricind coca b the hecrated tocistics Suooort).
etner,
It€E
I Type of Scrap - Iaitiator rwiews qpe of scrap action tating place:
t t
or
2. Dae - Ioitioor €otem numeric due MIII/DDIW)is being complaed.
3. TiE€ - Initiaor emers militarv time (e.g.. 1430)is being complaed.
4. Hrud - Initior checks eithcr hazardous or nonhazardors block.
cotcss N/A br
6. IE Dcsctiption - Initiator etrtcr! description of the item being scrmed.
7 Pm/Stoct Numbcr - Initiator eotes part/sock aumber of Datcrial.
rDtLrrt
N/A rvhco m
lrt
GM€.I
Issuc No. Ul
2l Septcnber l99l
of measue (ea, lb).
ffi@@
mmber caonot be obtained, initiator epters 'unlnown' or provides a brief explanation.
ll: Ne-rafrrreCSqurrhNu-ber Fet uapl^--C -erap; :-'dotsr eat€rs the N€/SQ nurboi
acioo). Initiator eders N/A for planoed scrap.
landfill, or seod to hopemy Management, ac.).
I l: '-'dotC byi Ert; oadgo Nrnbc lridater sitnr (nofta eert^:- sitnohre is elau en dl
ceics) and enters telephone extension and badge number.
15; ll-paevC by; 'ltt; oodte Nunber Ferrm situ; datx; aad eatas tel€phom orteatiermC
bdge number on dl Scrp Tags for planned scrap. Initiaor ente6 N/A for unplanned ssrap.
reE'-or/er$n''Etion sigFr;
ewluaion/analysis purposes.
fegistie&€uppo*
cregea*rscropr
Mffi
@
lea@la
GlLlt9 l19
GM-3.1
Issue No. Ul
2l Septcnbq 1992
SCRAP I.ABEL
(Fom TC 1064)
A PERMAMNT INK PEN MUST BE USED WHEN EOI,TPLETI.IG THE
SCRAP LABEL; USE A BUNNI'S MIRACT E PEN, OR EQUWALENT,
STOCIC NO. 5I-5t7004. DO NOT USE PENCXL, BALL POINT, OR FELT TIP
PENS.
The Scrap l.!el it placed on the neck of the ouside linec and cross refereaced to the origiaal Scrap Tag
as an$orization
l.
2.
3.
4.
Eater 6c ftigrt 'S' Scrap Tag nrnbcr ftou the Scrap Materid Tag.
Entcr thc mmber in the series of comainers that have the same stock and lot number
(e.g., 2 of 5).
Use nuocric date as date of scrap (e.9., lGls-E7).
Siguaorc of person who initiates thc scrap.
?l.la L aaL ?o lttr.rr. ora coi?am.3i u||?t|. coi"3r?t aratrocatttD ri. accoaoarrct rttr. ?t.ta ot
SCRAP
,oa. tc ao. rc.a.aaY. Lar
tc.
c.nl rraraC!oa
taoat"roi..
EDlt.r,r20
GM-3.1
Issue No. 12
2l Septarbq 19E2
IIAZARDOI'S WASIE PROPELI"AIYT I"ABEL
(Form TC tl59)
INSTRUCIIONS: (Uso a Bunny's Miracle Peo, or equivdent, Stock No. 5l-587004 when compl*ing
this fega. Do not rse peocil, ball point, or felt tip peos.)
l. Eoter description of itern being scrapped/disposd
2. Eoter building or material origin.
3. Encr part/stockaumber of scrapped/disposed naterid/Propellant tlpe (Examplle: TP-II No.)
4. Eter quadty (mmbet of pounds, ounces, gdlons, ac.) of Propellant, Explosive, or
Ppotechnics (PEP) being scrapped/disposd and the unit of measure (pounds, grams).
5. Eilcr qu.miry (nrnb€r of pouods, ources, gallons, ac.) of coouninated waste (wipes,
spatdas, glovc, ac.) bcing scrapped/disposed and the unit of measure (pounds, etc).
6. Initialor's Due.
7. Ioitiator's bdge mrmber.
t. Cuneot date.
9. Emcr the sixdigit 'S' Scrap Tag Nunber tom the Scnp Muerid Tag if the item is a'sqp€d'ntcrial.
10. Eltct thc aumbcr in thc series of cominers tht have the same soct and tot aumber (for
cxaople, 2 of 5).
I l. Encr any pcrtineot conniner insmrtions/rcods/specific contens rags, wipes, gloves, etc.).
For cm4lc: if 6crc .rl mre trash ircos io the cooaincr or too maoy coauminarcd-mcal
objeq o list h'1. Itco Dccriptioo" Iist iD'll.' This infurmation is intded o hdp 6e
M-136 diryGal crern h thc safg ordcrly diryosal of 6c matcrid. Includc solveot EPA
srsfic mnbct3 ia 6is ara.
qrxmYl,,t ll:glrr qxxmYrlgtl
3 l.
6 "*'lf)0^rl
cilnrraro,
IO
P P
€r.l.grtro,
lrfrrccrngt
r!ot
rt{
GILIA t2l
GM-3.1
Issno No.12
2l Septemb€r DqZ
IIAZARI'OUS }YAS'IE I.ABEL
(Form TC 71t!t)
A PERMANENT INK PEN MUST BE USED WHEN COMPLETING TIIE
HAZAR,DOUS WASTE LABEL; USE A BUNITY'S ImACLE PEI.I, OR
EQUTVALENT, STOCK NO. 5l-587004. DO NOT USE PENCII, BALL
POINT, OR FELT lIP PENS.
The Hazardors Waste label (Form TC 71tS) is ued for coaainecs of dl hazardous maerials.
Excess maserial docs mt require l lrazudous Srastc Irbel uatil the material is declred a waste.
Obtain proper MHSI ad Eatesial sock number from the Accept Tag or Shop Traveler before
coryleting the Hazardous lVaste kbel.
HAZARDOUS WASTE
GENERATOR INFORMATION
Zletba @ffiltu{ruv
P.O. BOX689. HWY83gRtclrAu ctTY. uTs.ifilssgPt{ottE60r..&Gfi
MANIFEST @
DOCUi,ENTNO.
@q-EFG rlo. C I
P.e
RO
wwtrastuI
sunorrKl{St-Ds-Xsro@
EPA
ID NO.uTD0090813r7
tsrq
SIIIPPTNG NATE
H iaRoctAss
EPAWASTE
GrrJrt
Fil.rcn!ttavr{D
r/2
2
3
L
-,1
_6.
J
3
o
10.
IL
GM-3.1
Issue No. ljl
2f Septeobe 1992
IT{SIRUC'TIOT{S FIOR, FILLING OUT HAZARIDUS WASIE I IBEI S
A Hazardou Waste l$el (Form TC 71tt must be afrachd to esch hazardous waste cootainer which
is o be shippd ofralam for disposd.
It+tela6.recfa*;
Write in the fullowing information:
L Pnoger n0f Shiggins Name: Found in the EtWPrr or obtained from EIIW.
P.G. (Optional): Indicates deqree of hazard. Infurmation is found in the IIWPD or obtained
fton FIIW. Curtrntly infotlration is optiond.
Hazard Class: Numeric DOf hazard class as found in the IilVPD or obtained from EIIW.
R.O (Ogtional): EPA Federal) re9ortable Srantity. See Table XI[. HWPD. or contact EIIW.
IIN: Fnter United Nations identification number found in IIWPD or obtained from EIIW.
EPA Waste No.(s): Found in the IIWPD or obtained from EIIW.. The numbers may
dqpndins on how the waste was Droduced.
Accnrrmlation Start Date: Date the materid is first placed in the container at the oOday
smrase site.
Profile/Stock No.: Stock Number for gure M.II.& S.r. materids or IIWPD profile numbers.
Qnrator: Name of person actually filling out label.
BuildinLBuildine that is seneratine the waste/Prosrem designator (see list below)/Cost
Center
6l hoqram Desisnators
Science and Engineerins
Space Shunle
Strateqic Overhead
D-5 Trident
Pcacekeeper
Standard Missile
EEre
Caster 120
MM Mfunrteman
AP AP Recovery Process
EO Ewimnmentd Ovcrhead
Addifunnl codes nny be added by F'IIW.
Cocn Centcr is thc qmup oerforminq the work- to the lowest possible accountabilitylad.
SE
SEsut
EK
SMEE
,EDll.riD
rDI
r23
GM-3.1
Issuo No. Ul
2l Scptembcr 1991
(12\ Manifest Eloorment No: To be conglaed by Hazardous Wase oickuLcrews before shipgins.
1, UN er N/\ ---b*: UN!}077
6r rteE'dodee Sert D*sr D*c &s -eterid h firot plreC hthe €ortaher et 90 Cey
ltottgo{ltE
ffi
tu
@
*ippiEE)
rerl.ut l2l a
GM-3.1
Issue No. ljl
2l'Septcmbt 1992
COMMON HAZANDOI'S WAS'IE TTII,ES IIOR
FILLING OUT IIAZANDOUS WAS'IE IJIBEL
Corlrn Nrm/Mam PtopcDOfShimim Nrns DOT lLzrrd
Clarr/Lrbol
llN or
NA No-
EPA\f,alo No.
Irlircd lLmbb dvcrr \f,roflluttrbbliduilr- N-O.S f.t 3/Flgrrbts li+dd trN 196 Dml..
Ftrsuorblo (erceaUo*unlnoaDhff-lcr tho 5l3 propcllrrr,
coil.inim.006rt0)
lVrlc fLomrblo
liqui.lt, N.O.S. (.)3/Fhnmrblc li+rU r,rN 1993 Dmls
I,l,l Trictloroalur (DropclLil-c@mid El@-L- th.D 5f
Drooclh0
rill.o I,l,l
tricUorocthfr
6.llK4 A*ry From
F@d
IrN 2t3l F(xz
Mchyl cliloroftrn(l.l.l trhhlomcthm)
W.no I,l,l 6.llKq Arny Froo
Pood
IrN 2t3l FOl,F@
Malryl atyl &rmo G,CK)ftctrr lrylalryl
hlamc
3/FhrlDrblo liquil uN lrqt FrUt,Dmr,
DO35
Matryl doohol (matrrct)W.no rtcahyl rlcohol 3/Flrnmrblo li+ril tN 1230 Fm,Dml
Mahyldclrbri&Wcc diclrlorcrnahrac 6.1/Kc.p A*ry Fronr
P@d
t N 1593 Fml,F@
bopropyl .lcohol fVro iropropyl.l6hol 3/Flemudlc liquid t N l2l9 Dml
Tohro W.nctohro 3/Fhmnbloliquil lrN 1294 F(XI',Dml
Acaoc Wrlcramo 3/Flrmnrilo fquU I'N I(BO Fm,Dml
HGilrrD Wrlc h*rrg 3/Fhmrmblc liouirt tN 126 Dmr
Xyhoo (rybl)W.nc x/m 3/Flrmublo li+rU trN 1307 Fm,DOI
Colhrolw Wrn ctryLo. Sl!.colmcrlrvl alr 3/Flrrrnrblo lhuid t N lrTl Dml
F nrTA W.iofgvfoqlrlrdlyllsrdour $rbnrmcr,
U6dd. N.O.S. (n
9/ClE 9 I'N 3G F(Xz,
FGl,
Fml
Chromio rid Wrao chmis rcidrofrin UCouorivc t N 1755 D(Xz,D07
Ftefinblo ngr Yro lbmarbblolUr.N.O.S. (n 4.l/Ftemr,bb rlil UN I32J Dmli.
Aboriom PocCoilrnirrd tVrra Weo AlninrmPordc. um.lod 4.3/Dr4crur Whco WGa t N 1396 D(pt
Matylclrlosofrrur qr W.ioElvtffillyIlcrrdou $rborcr,.o[d. N.O.S. (n
gl0Lll9 lrN 3077 FOl,F@
AlodiodCotrcrivc njr Weo corruivotoli&. N.O.S. (n !/Conduc UN 1759 D@,Dqn
Pticflct Wogritutamny
llprrdoor l$rblroccr,
-lid. N.O.S. (n
9rcbr9 t N 9307'Fmr
/llodiD liqrdd Yo Chunio Aoid3rlrio SlCorrutrc lrN r75:,D@D07
gErLrr.t24
GM-3.1
Issuc No. Il
2l Septembc l99l
l. Th. moifGa ilmbot fc tho rborc mloddr xill bo oonplaod jua prb! to offrito rhipraclr ty eorrrrtladfuthorchicb2. Aeqmdrdol -rrt d.to i. di. thc lrrtEi.l rnr firr phccd h tho dnm". Wb urh3 rny N.O.S. dcuiptim, tho tehicd nru of I lc.f tso compoitcil. rnc pcdolftuly
codibudos !o tho herrdr of tho serc Err bo cileld in purdrdr .ncc tb N.O.S. (Chcmicd nrm
r Addllnl urmbcar rnry b.ddd byWro Mrnrgqncd eod Ervirpmsrrl Scrviccr.
No0r:
,[orLDa l24a
GM€.I
Issue No. Ul
2f S4tcmbcr f9qZ
SfNONYIIG FOR COMMON MIJIERIAL NAIIIES
Common Name/
Mdtrial
Mxd Flemmable Solvenc
I,1,1 Trichloroethane
2firtanonc
Mcthanol
Me6ylene Ctloride
Isopropyl Alcohol
Toluene
Acaone
Xyleoe
Cclhsolve
Fron TA
Chromic Acid
Synonyms
Acaone "
Tolueoe
Xylene
Bopropyl Alcohol
Methyl Ctlorofurm
Methyl
Tric
TCE
Mcthyl Ethyl Keone
MEK
Methyl Alcohol
Wood Alcohol
Methylene Dichloride
Dichloromethane
Isopropaool
IPA
2aropaool
SECaropyl Alcohol
Dimethylcarbinol
Methylbenzene
Pheoylmethane
Toluol
Dimerhyl Kaone
Methyl Ethyl Kaone
MMK
2lropaoone
N{epune
Dipropylmahane
Dlnethyl Beozene
Xylol
Trichloro Triflouroethane
Cbrcniun Trioxidc
Chromic Anhydride
Alodinc
Ethylenc Glycol Monoefiyl Ether
2lheooxyethaool
llcpune
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GM-3.1
Issno No. ljl
2l Septanbc f99l
II{STRUCTIONS IIOR, COMPT,ETION OF I'NITIORI}I
EAZARDOUS WASIE MANIIEST {on0
U.S. EPi\ Form 87fi)-22
Some states require 'S*rNffifoo' (e.g., Pennsylvania,
Teras, etc.). Conac Environmemal lV3ste Disposd, Ext
62&{, befure complcing one of theso manifests.
Tte gmerator's U.S. EPA ideotifrcatiou number must be the @Eect l2digit number assigaedp qe fac4itl sendinq tle load. Identification nrmbers for Thiokol and Auomotive Saf*y
Produsts Division (ASPD) are:
Uuh regulations require proper complaion of dl infornation ea 3 manifest. Omissions,
nisspening, false coding, or illegibility is considered a violation. All geoerators are
rcsponsible under Utah aDd Federd Law for the proper identification, labeling, marrifesting,
ad ultinde disposd of dl hazardous wastes they geoerae. The manifest system is designed
to track hardors waste from the point of generation umil its final disposd (cradle o grave).
In ordcr o accomplish this god, it is esseotial thd all items on a manifest be properly
corylaod.
Read all instructions befure conpl*ing this form.
This form has been desigued for tse on a l2aitch (elite) typewriter; a firm point pen may
dso be nsod - Press dowtr hard.
Utah and Federal regulations require generalors and transporters of hazardous waste and
ownem or opetaon of hazadotts waste treatneot, storage, and disposd facilities to use this
forn (8700-22) ail, if necessary, the continuation sheet (Form n&22L) for both inter andirasate transportation.
rnfi3@7
Thiokol
Promoaory Plant
H-7xao
z-t2
ASPD
- UID 0090El357Promonory Plant- U T D
- ulD 9t0806236x-r7- UTD 05ffi4n3
- urD 9t0808513
- UTD 981551D6
GENERATORS
It€m I Geoctaor's U.S. EPA ID Number-Manifest Documenr Number
Eucr the genetabr's U.S. EPA l2{igit idrntifiction nrmber aod the unique Sdigitmnbcr assigned to thb manifest (e.g., 0flDl) by the geoer$or.
Itcm 2 Page I of _
Eucr thc otal_number of pages rsed o corylae this manifest, i.e., thc first pagc
(EPA Form no0.22) plus thc umber of Cominration Shoas (EPA Foru tTOO-
XIA), if aay.
t[srr.r,tn
Itcm 3
IteE 4
It€m 5
IteE 6
ItGu 7
Itcm 8
Gill-3.1
Is$to No. 12
2l September 1991
INSTRUCIIOI{IS FON, COMPT,ETION OF T'NIFORI}T
IIAZAIDOITS WAS'IE MANIIEST (conO
U.S. EPA Forn t70.,22
Geoerator's Name ind Mailing Address :
Emer the oame and mailiag ddress of the generator's location that will manage the
reauaed manifest forms.
Geoemtor's Phooe Nunb€r :
Entec atdephone number where an arthorized ageot of the operalor may be reached
la the wcot of ao locrgeocy.
Transporter I Coryany Name
Emer the oompany oame of the first tramporter who will tra$port the waste.
U.S. EPA ID Number
Emer the U.S. EPA l2{igit identification number of the first transporter identified
io It€E 5.
Trusporter 2 Coryany Name
If applicable, eoter the coryany name of tho second transporter who will transport
thc waste. If more than two traosport€rs are rsed to transpon the waste, use a
Continuuion Shea(s) (EPA Form g7W22A) and list the transporters in the order
they will be traospoaing the waste.
U.S. EPA ID Nunbcs
If applicable, eots the U.S. EPA l2{igit identifrcation number of the second
tramponer ideotified in Item 7.
NOIE
If morc than two traosporters are used, eoter each additiond
transporter's coryaoy oame ad U.S. EPA l2digit
ideotificatioa numbcr in Iterns z+tl on the Continuation Shea
(EPA Form n@-22A). Each Continuation Shea has space
to reoord tuo additiood transporters. Ever!, traosporter used
barvecn the geoerator aod thc designaed facility must belistd.
Itcu 9 Dcignated Facility Namc and Site Addres3
Eotcr the conpasy oame and sitc address of the facillty designated to receive the
wrstG listed on this manifest. Tte addres must bc tf,e site ad&ess, which may
difrcr ftron thc coryany mailing address.
Iteo l0 U.S. EPA ID Nunbcr
Emcr thc U_.S. EPA l2tigit idemificatioD arrnbcr of thc dcsignated facitityiddifid in Itco 9.
9A$ll.l,tzt
GM-3.1
Issue No. Ul
2l Septanber 1991
II{STRUCTOT{S TIOR, COMPLEION OF I'NIFORIVT
IIAZARDQT S WASIE MANIFEST (con0
U.S. EPA Form t7fi)-22
Item ll U.S. DOT Description (Including Proper Shipping Name, Hazald Class and ID
Numbq - UN/NA)
Eot€r the U.S. DOT hoper Shipping Name, Hazafi Class, ad ID Number
(UN/NA) for each waste as identifrd itr 49 CFR l7bln.
NOTE
ffdditiooal space is aecded for waste descriptions, eotq these
ia ltem 2t on the Continuation Sheet (EPA Form t70G22A).
It€m 12 Conainers (No. and Type)
Eater the number of containers fur each waste and the appropriate abbreviation from
the list below for the type of conainer.
TYPES OF CONTAINERS DM = Metal dmms, barrels, kegs
DW = Wooden dnrms, barrels, kegs
DF = Fiberboard or plastic drums, barrels, kegs
TP = Taots poruble
TT = CargO tutq (taots, tructs). TC = Taok cars
DT = Dump truck
CY = Cylinders
CM = Mctal boxes, cartoos, casc (including rolloft)C[/ = Wooden boxes, qarbns, casEs
CF = Fiber or plastic boxes, qarbns, qases
BA = Burlap, cloth, paper or plastic bags
It€m 13 Total Quantity - EDtGr the totd Erantity of waste described on each line.
It€m 14 Utrit (WWol)
Emer the appropriate abbreviation from those listed bdow for the unit of measure.
UMTS OF MEASURE G = Gdlons 0iErids only) '(E.3 lb)
P = Pounds 0b)T = Toos (2,000Ib)
Y = Cubic yards r(O.tli tons)L = Litcrs 0iEri& only) .@.2Ib)
K = Kilograms (2.2lb)
M = Mctric oas (1,0fi) tg) (2,200Ib)
N = Cnbic Eetc$'C2,200Ib)r Specifrc grayity - 1.00 unless indicatd in Box I.
rell.r,t29
II{ISTRUCTIONS FON, COMPLEIION OF I'NIIIOR}T
EAZARIIOT S wASaE MANIFESI (con0
GM-3.1
Iscur No. 12
2l Sqtcmbcr 1992
ftltrsporter.
manifest by
U.S. EPA Form t7fiI,22
rrco 15 Specid Handling Instrucioos and Additional Ioformation
ItcE 16
It€D l7
Thc 24,ir emeqgeocy r€spotrsc number for Chemtrec, 1{t00) A+93Ul., should beeilctd iD ttis spac9. Also the Guide Number from the Emergency Rcponse
Guiddook needs o be ecered h this spaoe. If more than one hazardous waste is
listed on 6e manifest, additional Guide Nunb€rs mst be included with referenceo which wase thcy apply.
Gcocraon may use this space to indicate special transportation, treatmert, storage,or disposd infurmation or bill of lading infurmation. Sutes may Dot require
additiooal, nep or difrereu information h this space. For ioternationd shipments,gcosalon Eust entqr in tiis space the point of deparure (Crty aod State) for those
shipmem destitrd frt trement, storage, or disposd outside the jurisdiction of the
Unitd States.
Geoerdor's Cenification
Ilc gcoerator mst read, sigu Oy had), and date the certifrcation stateoent. If amdc othcr than highway is rsed, the word 'highway' should be lined out aod the
appmpriatc mode (rail, wdetr, or air) inseaed in the space below. If another mode
in additiog to the higbway node is rsed, enter the appropriate additional mode (e.g.,
aod tail) in the spaco bdow
NOTE
All oltlu ofuvc Wtlrotiln qccpt tlu lutt&vrfxen signonre
rcWtrcd ln ltcnt 16 noy b prqilucn.
Transporter I Aclnowledgement of Receipt of Materids
Emer the aame of the person acc€pting the waste on behdf of the firstTht person must aclnowledge accepance of the waste described on the
signing and emering the drc of receip.
Itcm lt Tramporter 2 Acknowledgemeot of Receipt of Materials
EilGr, if 4plicable, the name of the person accepting the waste on behdf of the
sccond tla$portr. Thc person mrt acknowledge accepance of the waste
dcccribcd on thc nanifest by signing aod entering the datc of receipt.
ItcD 19 Discrcpancy Indication Spacc
Thc atfiotizod represent*ive of thc desiguaed (or dtccaate) facility's owner oropcrdff lltst noto ir thb spasE atry signifrcant discrepancy bayeco thc waste
decc8ibed on the manifcst and the wastc acnrally received u hc facillty. Contac
EA, Ert 5454..
,Elt.t 130
GM€.I
Iscuc No. ljl
2l Septombcr f99l
INSTRUCTIONS FON, COMPI.ETION OF I'NIFORI}I
IIAZARDOITS WASIE MANIFEST (con0
U.S. EPA Form t70G22
Item 20 Facility Oumer or Oprator Ceaificatioo of Receip of Hazardous Materids Covered
by this manifest exc€pt as noted in Item 19.
Print or type the name of the penon accepting the waste on behdf of the owner or
opcrdfi of the facility. That person mrst actnowledge acceptance of the wastedecribd on tho Eadfest by signing and eotering the dae of receip.
Itms A-K are not reqrired by Fedcral regulations for intra or interstatc
trusporEtion. Howerrer, sates mly reErire geoerabrs and owners or operalos of
treffine.ot, sbrage, or disposd facilities to complete some or dl of items A-K as pan
of state manifest reporting requiremeos. Generators and ownec and operaors of
trctmeot, storagq or disposal facilities aro advised to conrrct state officids for
guidance on complaing 6e shded areas of the manifest.
ADDnONAL Ir{FORMATTON REQI TRED By THE STATE OF t TAH
Item B State Generator's ID
Enter State Generator's ID Numberf
Item C State Traosporter's ID
Enter State Transporter's ID Number
Item D Transporter's phone
Eoter the phone number of the first traosporter who will trauport the waste.
Item E State Transporter's ID
If applicable, eotcr tho State Transporter's number of the secoad transporter who
will transpon the waste.
IEm F Transponer's phone
If applicable, eotsr the phone number of the second tra$portes who will traosport
thc wastc.
Itco G Statc Fecility's ID
Emcr thc State Facility ID number
ItcB H Facility's phone
Eotcr thc phone oumber of the facilrty dcipated to receivo thc waste listed on thc
naoifest.
,[slt.1,l 13t
Item I
It€m,
Iten K
Item O
ItcE Q
ItGm R
ItcD S
Itco T
GM€.I
Issue No. Ul
2f Septcmbor 1991
IT{ISTRUCTIONS FIOR, COMPLEIION OF I'NIFOnIVT
IIAZARIIOUS WAS'IE MANIIEST (on0
U.S. EPA Form t7$.'22
lYastc number
Emct the 4-digit EPA hazardous wasto trumber assigned to the waste. If the waste
is a Eixurc, include all EPA huardous waste numbers fur the wastes known o be
prescot, regrdless of the quai[ity of each itrdividual waste compooeot.
Additional Descriptions for Material Listed Above Shippcd Withio thc State of Utah
If the DOT shipping dccription in Item 1l (a, b, c, d) contains NOS or other
gcoeral terms, the hazardous waste onstinreot(s) Eust be provided here for each.
Thc specific gravity is assumed to bc one (1.00) unless othenrrise indicated here.
Ilaodling Codes for l\lastes Listed Above
Eoter oae of the following threedigit handling codes for each waste listed above.
STR = Storage; TRT = Treamem; DSP = Disposd; RCY = Reclamation
The codes assigued h this item mrst be the ultinate Eaoagement code. Both the
gcoesator aod the tremeot, storage, and disposd CISD) facility should agree on the
codc assigned io this item.
NOIB
Thc following items apply if a manifest cootinuation shea is
tscd.
Transportet's Phone
Rder o Iten D
Transporter's Phone
Rcfer o Iteo F
Waste Number
Rcfer o Iteo I
Additiooal Dccriptions for lvlaterials Listed Above
Rdc( b Item,
Ilaodliag Codes for Wastcs Listd Above
Rcftr to Iten K
reu.rt t32
GM-3.1
Isue No. ljl
2l Septembq l9t2
ASBESTOS LI\BEL
(Forn TC 444t)
DANGER
CONTAINS ASBESTOS FIBERS
AVOID CREATING DUST
CANCEB ANO LUNG DISEASE HAZABD
aol tc...atIva.aal
EttlS TB
GM-3.1' Bsue No. 12
2l Septanbcr l99l
ASBESTOS WASTE SEIPMEXYT RECOru)
(Fotu TC tl7,
Ctra raroror!3 frla3r{ila3ltlaAa.t
o'ardo3 ,UIIt
;t ratrEarttrt6sa rrrarEaalS ro rf,tcr arl raclanor rBrE to.arr{r
. ulr,oraEaorrF-l.lraolEt
Got-
aUJz!r(,
! oaacrnnor,ltr.'t a oo.'riara
,'D.
, rollournn
rv"c cu. Yos
r OPETAIOBS Itrnao,oaoara orilDa curEr!]c flra co,rar9,rntart ara illy arlt &qraD,ocnoao ilEtaa,! arla n aI raa9ct3 n rog,ccrEn lara,r.o,rDy 9rsar allm,l nftE antxacF.ftict gBarl,nrraar. tr! saaao.i{,trray EUre l' oEaoS fi!'rEi. fE oo,tmtrrElraEra.
Er. 0-
olt
r8.aaa tuaoar,-t
xo gt 6ft
.ooaaa3
rtl-
.D
gloAdla
i.r O|tgl.lrc'r.lcrroarCa
I
.,f,art EIrEfl f[
ctitrc^tErc rtcctt ilA3fg|B uatEn^rsoot tito fr fl{r3 u^rrasf, Erct7rrs rllttD r,rtL 12
,or ,a t.1 AtrirtO
tir'l . ,ftttltaO,
- - tl-iaIio Itll . AlO3r.ltCCt
rtI
rrlJr ty
GM-3.1
Issue No. ljl
2l September 1991
ASBEST(XI WAS'IE SEIPMENT RECORI)
(Form TC t17t
AN It{r(PEN MUSTBE USEDWHEN COMPI#TING TI{EASBESTOS WASTE
SEIPMENT RECORD. DO NOT USE PENCIIS OR FELT TIP PENS.
PRESS HARD . YOU ARE TAKING SD( COPIESI
The Asbcos Slaste Shipment Record m$t accompatry atry regulated asbesos contaminated
naste mderids during transporution o.n ary public highway.
The 'Geoerator' of the waste fills out the form according o the instnrctions whic.h follow.
The generaor then has the'Traosporter l' fill in dl of the reErired informaion on line 10
or the furm aod then tears off the goldeorod (Generator) copy and blue (file or State) copy
and placc them in their appropriate sorage files.
The 'Transpotter l' is the person who trarsporr the waste material from X-20 or H-7 !o M-
136. 'Traosporter l' tutas the materid over to an authorized person at M-136 who then fills
in dl of 6e required information on line 1l of the form. Transporter I removes and raains
6e pint (transporter 1) copy of the form for his permanent file.
'Transporter 2' is the persoo vho receives the waste at M-136 and transpors it to the M-
336A Saniary llfflfill. This person must verify the corecoess of the Asbesos Waste
Shipmem Reord. Any discrepaocies described in the iostructions mst be indicated on line
12 d resolved with the generator over the telephone before the waste is accepted at M-136.
ASBESTOS WASTE SHIPMENT RECORD INSTRUCTIONS:
S/aste Generator Section (Items I through 9)
Item I Eater the name of the facility a which asbesos waste is generated and the ad&ess
ufrere the facility is located. In the appropriate spac6, dso enter the name of the
oyner of the facility and the owDq's phone number.
ItcD 2
Item 3
Itco 4
Itco 5
If a demolition or renovation, enter the name and address of the company and
arthorized agent reponsible for perforning the asbestos removal. In the appropriue
s[rag6, dso ents the phone numbq of the operabr.
Eoter the name, address, and physical site location of the S[Iaste Disposd Site
(WDS) that will be receiving the asbesos materids. In the appropriate spaces, dso
cmcr the phone number of the WDS. Eotetr 'on-site' if the wasrc will be disposed
of on the generator's propetty.
hovide the namo aod address of the local, State, or EPA Regional office responsiblefq rdministering the asbestos NESHAP progran.
Indicate 6c types of asbesos waste Eiltesids genemed. If from a deoolition or
rmvation, indicatc the amount of asbestos that is:
o kiable asbesos Eatffido Nonfriable asbestos ntcrid
qrcrt.lt 135
GM€.I
Issue No. ljl
21 Septonbor 1992
INSTRUCTIONS TOR, COMPLETION OF ASBESTOS
WASIE SIIIPMEhIT RECORD (con0
(Form TC tlTt
ItcD 6 Emer thc number of ontainers rsed o transpon the asbestos materials listed h item5. Also enter one of the following conainer codes rsed in transponing each type
of asbesos materid (speci$ aoy other tlpe of container rsed if Dot listed below):
DM - Metal dtums, barrels
DP - Plastic dtums, barrels
BA - 6 mil plastic bags or vrrapping
BIN - BiD Qind with double plastic)
It€m 7 Eoter the quntities of eacb tlpe of asbesos material removed in units of cubic
Dotets (orbic yards).
Item t Use ttis space to indicue specid transportation, treatmeot, storage or disposd or bill
of lding infurmation. If an dtemate waste disposd site is designated, note it here.
Emergency respoose telephone numbers or similar inforuration may be included
herc.
Item 9 The arthorized agent of the waste generator mrst read urd then sign and date this
ccrtification. The date is the date of receip by transponer.
NOTE
Tlu tttoste gcnerotor mtst retah a coyy oltilsform.
TransBlrter Section (Items lO aDd ll)
Itcms l0
aod ll Enter name, address, aod tdephonc number of each traDsponer rsed, if
applicable. Print or type the full name and title of person acceptiag
responsibility ad acknowledging receipt of materials as listed on this waste
shipment record for transport. Enter date of recetpt and signanre.
NOTE
fuch trowponer must raain a cW of tlns form.
Disposd Site Section fltems 12 ad 13)
Iteo 12 Thc authorized represeottive of the WDS mrst note in this space any
discrepancy between waste described on this rnanifest ard waste acnrally received
as well as atry iryroperly enclosed or contained waste. Any rejected materids
should be listed aod destination of those materids provided. A site 6at converts
asbestosontaining wasto Eatedal o mnasbestos material is considered a WDS.
I&m 13 Thc siguanre Oy hand) of the ar6orized WDS agcnt indicates acceptance and
e3rceneot with satements on this Asbesos Waste Shipment Record except asDtd in item t2. The date is the date of signanre and receip of shipment.
. NOTE
Thc WDS mtst raah a a nplad qy of fisfont Ih.
WDS rrrurt olso scrd a compl*l cW to tlu opcroor ltstcd
ln ltn 2 $rtin 35 doys. If fiu encrur hot no rcccivdtlu ortgbtol ($ilc) Gcneroor cayy ba*wttht t 45 doys
lrut M-136, tlu gateraor nust na{y thc trA.
9[$ll.r!6 l36
GM-3.1
Issue No. 12
21 Scptanber l99l
WAS:TE IJ\BEL
(Forn TC t15)
WASTE LABEL
[rAtERtAtCO#ONNAr.€ i
No 033452
BUTTDI}IG CONIACT O^TE
ff)Rrrc 8125
MHT SI OIJANTITYSTOCX tlo
BAmEi.ro
GT IDEUNES FOR COMPLETING FORM: (Use a Bunny's Miracle Peo, or
equivdeor, Sock No. 51-5S7004, when completing the Siraste Label. Do not use peocil,
bdl port, or felt tip pens.
1. Material common nane as found in MHSI, MSDS, or IIWPD.
2. Building of material origin.
3. Stock nrmber from MESI; learre blaok if materid has no MHSI.
4. Write in five digit MESI number if available, if not write N/A. Auach a copy of the
MSDS or call Indrstrid Hygiene o order one from the material mamfacturer.
5. agadry of maerid being disposed in largest unis (grams, ounsEs, kilognms, pounds
or cubic yards for asbestos contaniDred waste).
6. The person filling out the label or 6c building representtive designaed by
maoag€Eeot o be the Contact Persoo; this person needs o be lrcwledgeable about
the natcrid.
7, Bdge nnrnb66 of 6e pessoo identifid in No. 6 above.
8. Date 6e lVaste Label was frlled out ad the materid placed on an apptoved waste
doct
9. Spacc br thc uscr E providc specid handling reqniremeots or othcr helpfitl
inftroadon for disposd Eens. This should include the IIIVPD{cigEatd place ofdispal: Industrid ll/aste Treoch, Asbctos Trmch, or Carbon and Silica Sand
Trtoch" a thc M-336A Saoitary l:ndfill.
Rcoove or paint out produc labels fron comincr aod place lVastc kbd in a cleady
visiblc pooition. If 6c iteo is snallcr 6a thc labcl, place thc itcu irib of a sealable
plastic bag and placc labcl on 6e bag.
,Err.r,,t37
GM€.I
Issue No. 12
2l Septembq 1992
EMPIT DRT'M I.ABEL
(Foro TBnll)
A PERMANEM INK PEN MUST BE USED WHEN COMPLETING TIIE EMPTY
DRUM LABEL; USE A BUNNr'S MIRACLE PEN,"OR EQUMLEI{T, STOCK
NO. 51.5T'004. DO NOT USE PENCIL, BALL POIhN, OR FELT TIP PENS.
l. List original coments aod sock lnnb€r (f available). Get stoct nunbq from Accqt
Tag or Shop Travela.
2. Building mmber.
3. Datc removcd fron building o doct for pickup.
4. Signmre of person requming pic@.
5. Doc of pichry re$est.
I$cl should_bc ptaced on 6e uppa 6ird of thc drum body. DO NOT placc empty drun
labcl ovcr original nartings aod labd.
EMPTY DBUIJI LABEL
mrrdlEall
reUEMTTE O'EIreTE
Emtganr
,rrE,?tl
oEt
, TLtI r3t
GM-3.1
Issue No. ljl
2l Scptembq 1992
ST MP ACCUMULA-TION RECORI)
(Fom ST9062)
A PERMANENT INK PEN MUST BE USED WHEN COMPLETING THE SUMP
ACCUMUTa-TION RECORD; USE A BUN}.IY'S MIRACLE PEN, OR
EQt MLENT, STOCK NO. 5l-5t7004. DO NOT USE PENCIL, BALL pOrNT,
OR FELT TIP PENS.
Wheo surting a rcr, form, ema building number where the sump is located. SpeciS
north (N), south (S), east (E), or wqit (W) if there is more than one sunp u the sane
building.
As soon as oaerial accuurlaion bcgiDs, em€r Dirne of person filling out the record
aad 6e datc accumrlatioa began ulder 'Accumulation Start Date'.
3. Thc nr4 truc,k opermr will sigp ad dde the 'Date Pumped' seqion after the sury
has bGGo puryed.
4. Rcpcat step No. 2 ndil both sidca of the furm are fiIld. Seod corylaed form o
Eavircnnemal Wastc Disposal, Ittail Sbp 3Ol.
I
2.
'l
.2)3
MP
OAIE
I
I
ACCUMUTATION STAFT DATE
lturlE OATE
OATE PUMPED
NAME
tDrt.t r39
GM.3.I
Issuc No. D
2l Sepanber f99l
SATELLIIT IIAZANDOUS WASIE IJ\BEL
(Form TC t19O)
A PERMAMENT INK PEN MUST BE USED WHEN COMPLETING THE
SATELLE HAZARDOUS WASTE LABEL; USE A'BUNNY'S MIRACLE PEN.
oR EQt TVALENT, STOCK NO. 5l-5t7004. DO Nm USE PENCIL, BALL
POINT, OR FELT IIP PENS.
Isa4u'PRrn, Tf, r'gilq.Xr ra,e
HANDLE WITH CARE!
CONTAINS HAZARDOUS OR TOXIC WASTES
Oz+EMERGENCY RESPONSE
GUIDEBOOK NO.
CONTENTS
1. List Energency Respoose Guidc Nnmber found in the currenr Dqartmem of
Transpormion (DOD Enugeocy Respooso Guidebook.
2. l,laterid common name of dl naterids placed in the container as fouod inlflISI, MSDS, or IIWPD.
kbel must be placed on 6e uppet third of the dnrm body adjacem o the DOTHra;d Oass kbel.
,[su.to 1,()
GM-3.1
Isgue No. lj2
2l Sdptanbc 1991
DrsFosAL o, offiH* PRoPERTY
The following information is provided so that personnd will be able to differentiate
between qplolive items destroyed through the scrap system ao$ explosive items excessed and
prcccsed by Property Maoagemeot.
'Wheo xplosive items are excessed because they are no longer requirod, out of shelf tife,
or in somc insunces because the comact is complae, these items arc screened in-horse by the
Division Sores in an arempt o daermine if aoy item can rsed by another organization. If
there is no further requirement by another orgadzation for a specific items, ercess documens
are furwardd to Property Managenem
Plop€rty Management ptepares an invenory schedule listing exoess explosive iteos and
submis o the Goverament for screening with variors govemneot agencies. The government
agency rwiews the propeay for possible reutilization on other projects in the Deparment of
Ddeose. In some cases there will be a request for transfer of the propefiy to an applicable
ageocy.
If thse is not request for renrtilization, then in accordance with FAR 45.61l, the disposd
deerniaation for an explosive item is destruction. A Requisition/Shipping Doorment @D-ll49) is issued by Prcpeay Management as authority for destruction of Governmentowned
Eopefty.
Atr IMO is issued by Pr,operty Manageoreot for destnrstion of Companyowaed property.
A mcmo is urricen, with the IMO or DD-1149 asached, to the applicable Division
requesting that planning be corylaed and that items be destroyed withia 30 calendar days.
ltc Division is responsible o prepare the necessary planning and followup o accomplish
destruction. Smres personnel tnd orgenization perfurning the destruction mst follow the
applicable instructions to ensure that the exsess explosive items are properly packaged, moved,
aod desuoyod within the 3Gday pedod.
There are matry organizations involved in acconplishing the destructioa of explosive
items; therefore, such an effort requires a great deal of coordination and cooperation on the part
of all individuals in 6e various orgarfzations.
Property au6orized for desrruction by Property Management does not require a scrap tag;
howwer, if a scrap tag is prepared, it should accompany the planning and DD-1149/IMO to the
disposal organizatioD.
It is vcry imporuot the documents prepared by Pr,opemy Management arc auached to the
erplosivc itcms so the disposing organization will be able to deternine the difference between
excess itcus and itcos processed through the scrap systen. TLc exsess explosive Dat€rid
should NOT be placed otr e wastc dock for pickup, witi only a scrap tag a:tachd. Thc
dispcsl organizdion should be conuced o coordinate pickup of materids to eosute prcpcr
documcm are with 6e materid at the tine of pichrp. Thc IMO prepared by Propcrty
Managcoeu shonld be givm o the drivcr and a siguanre obained fron the &ivcr at the timc
of pichtp, with onc copy cained by thc o(laniztion shipping the explosive item and one oopy
seu b Plopcrty Disposal. Thc disposing organization should theo complee destnrction aodforv.d a signed copy of 6e DD-1149 or IMO b Propedy Managemeot.
,Eu.Ll l4l
GM€.I
Issuc No. Ul
2l Septcnbcr 1991
Af,PEIITDTX Itr
PAIT{T FITTEN, LIQI'IDS TEST
1.0 scoPE AI{D APPLICATION r
l.l This m€thod is rrsod to determine the presence of free liquids in a representative sample
of waste.
1.2 lte me&od is used to determine compliance with 40 GR 264.314 end 265.114.
2.0 SUMMARY OF MEIHOD "
2.1 A predaerniaed amurt of maerial is placed in a paim filt€r. If any portion of thc
Datsid pass6 through and drops from the filter within the 5-min test period, the
materid is deemed to costain frec liErids (Figure [-1).
3.0 II\TTERFERENCES
3.1 Filter media wcre obsened o separate from the filter cone on cxposure o dkaline
n*erids. This derrelopment causss no prcblem if the saryle is not dishrbed.
4.0 APPARATUS AI{D IvIATERIAI.S
4.1 Codcal paint filtec Mesh number 60 (fine meshed size). Available at locd paint stores
sush as Shemin-Williams and Glidden for aa apprcrimate cost of $0.07 each.
4.2 Glass ftnnel: If the paim filter, wi6 the waste, qaomt srsain ia weight on the ring
staod, thco a.flutedalass ftnnel or glass fumel with a mouth lirgo eooug[ to dlow u
least I in. of thc filter mesh to protnrde should be rsed to support the filter. The funnel
is o bc flutd or harre a large opeo mouth in order to support the paint filter ya not
interfere with the movenent, to the graduatd cylinder, of the liErid that passes through
the filter mcsh.
4.3 Ring sund and ring, or tripod.
4.4 Graduatd cylinder or beakec lm-d.
5.0 REAG:ENTS
5.1 Noae.
6.0 SAMPLE COLLECTION, PRESERVATION, AI{D HAI{DLING
6.1 All saryles mst be collected accordiag o the directions in Section 9 of this maoud.
6.2 A l0O-Dl or l0Gg represenctive sample is requircd fur the test. If it is not possible to
obtein a saryle of l(X) ml or lfi) g 6at is snfficimtly rcgrcsemtive of the waste, the
analyst Day u$ larger size sarylcs in miltiplcs of l(X) nl or lfl) 8, i.o., 200, 300, 400
nl or g. Ilowwer, wheo laryer saryles arc used, aoalysts shdl divide the saryle inolm-d or lfi)-g poaions and test each ponioa separuely. If aoy portion contains frec
liqui&, thc cmirc saryle is coasidsed to havc free liqd&.
t[su.rc ta
GM-3.1
Issue No. Ul
2l Septcmbcr Dql
AIPEDIDD( Itr
PAIITT FILIER LIQITIDS rESr (con0
7.0 PROCEDURE
7.1 Assemble test apparanrs as shown in Figure ltr-2.
7.2 Ptace saryle in the filter. A fuanel may be used to provide support for the paint filter.
7.3 Allow saryle to drain fur 5 min ino.the graduated cylhder.
7.4 If -y poaion of the test materid coll'ecs in the graduatd cylioder in the s-min period,
6eo 6o mterid is deemed o contain freo liquids for purposcs of 40 CFR 2*.ib ail
261t.314.
t.0 QUALTTY CONTROL
t.l Dlrplicate samples should be analped on a rcutiae basis.
9.0 MEIHOD PERFORMANCE
9.1 No data provided.
1O.O REFERENCES
l0.l None required.
gErLt.B t4l
GM-3.1
Issuc No. lll
21 Septcrrber 1992
Slart
7,1
Assemble Tegt
Apparatus
7.2
Samole
Filter'in
7.3 Allow
Stopin Graduated
7.4 Material is
Deened toContain Free Uquids:
See 40 CFB 264314or 265314
&at077.
Figue ltr-I. MG6od 905-PaiDt Filter Liquids Tct
,I$lt.ltL tu
GM-3.1
Issue No. Ul
21 Septembq 1992
Stand
Rlng
Paint Filter
Funnel
Graduated
Cyllndsr
Aoa.tt
Figurc m-2. P.ia Filtcr Test Apparatus
I
I
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APPENDX C
Sampling Procedures
SAMPLING PROCEDURES
1.0 INTRODUCTION
Saroples wiLl be collected using a statnless steel hand auger.
l,lhere coarse gravels 1111 not al-low collection with an auger, grab
sarnples rsilL be obtaiued rlth a stainless steel scoop. This
equipment is illustrated on Flgure C-1.
2.0 SURFACE SAITPLTNG TECENTQTIES
Iland auger conslsts of a two-inch stainless steel cylinder for the
collection of a sample, a handle to rotate the auger, aod a bit to
cut the soil. The auger is rotated, and the bit pul1s the sample
collection cylin<ier into the soi1. After ithe sanpie is collecied
from the desired soil level, the auger is1lfted froo the borehole
and the sanple reuoved. Ttre soi.l sanple rri11 be placed lu glass
bottles with a teflon seal and cooled to 4oC.
2.L Decontamination Procedures
The hand auger aad/or scoop w111 be decootaui.oated grlor to each
sample collection. Ite equipnent !r'i11 be steao cleaned wlth
Alconox detergent, rlnsed wlth tap lrater aad then fiaal rlnsed wlthdistllled (deionlzed) water.
2.2 Sanpllne Containers
Sanpling contalaers will be supplied by the analytical laboratory
contracted to perforu the sample aaalysis. Cootainers.lrlll cooslst
of ride Eouth glass bottles and a tefloo seal. A11 smples ri11 be
cooled aad stored at 4oC.
2.3 Sanole Locatlons
Sanple locatlons !ri11 be chosen uslng the Random Nuober Table
(Table 1). Instructlons for use are located at the bottm of the
tab1e.
-1
Hondlo
SCOOP
Somplc Colloctlon Cylinder
|-IAND AUGER
FIGURE C-l
SAMPLING EOUIPMENT
Augor Blt
APPENDIX D
Statistical Comparison Techniques
STATISTICAL CoI'{PARISoN TEC:$IIQUES
1.0 PARAMETERS FOR SIIYPLE RANDOI,I DESIGN
The calculatlon of the basic parameters for Ehe sinple randondesign will be calculated using the following rechnique ourlioed inPrtton of Soil S Protocol: Te s and Srrato/
The calculation of the mean and the variaDce can take two forus.0n1y one of the forus w'i11 be presented here. rn cases where thevariaoce ls corrmon beBreen tvo sauples and proportioual allocationls used, the calculatlons for the mean and the variance aresluplifled. Proportlonal allocatlon is conrnon in sol1s workbecause the variance tends to be the same over soil that is iaclose geographic proxiairy. i
(1)=nY = (EYt/n)
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(3) szp = I t,tt -",f * frr, 4.)'!: tg,+n--z)lc.t J.t '
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The meao is calculated by use of equation (l), the variance by useof (2), and rhe pooled variance by equarion (3)
lJtrere - mean of all soil saoples
- varlance of the oean
- total ouuber of obsenrattoos
= pooled variance
v(Y)
stP
2.0 AI.IAIYSIS.0F VARIANCE OF SII.IPLE RANDOI,i DESIGN
rf the analysls of varlance (ANOvA) is used ro determine thedlfference betreen che tro sets of saople data, the folloning tablecan be used to do the calculatlons for the AlrlovA. fna rerntreatEenr is a Eerm used by statlstlcians when handling differentdata secs. This should be kept in rnlnd when readlng the secrlonsthat follos. one treatmenr Ls the data frou rhe polluted area andthe second is the data froa the control area.
Y
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Table D-l Analvsls of Yarlance for Sirnole Ranciom Design
SOURCE OF VARIATIONS
DEGREE OF
FREEDOM MEAN SQUARESiI
( (5 r /u)-(c:/= n) ) /(k-l)(zy -GTr/n))/(= n-r)(E y -(c'l* n))/(: n-l)
)t' T- /n = Ehe rotal of each treatDent squared then divided by thenumber of obsenrations in the treatDent
,
G- / 2 n = Ehe square of the sum of aLl obsenrarions divlded by thetotal number of obsenratlons
)y- = the srrm of the square of each obserrratton
k . rhe nuaber of treatmeots i
To test the hypothesis that the aean for the controls is eo-ual tothe nean for the polluted soils, the withio tleattren.r Dean squarels dlvided iato the treataent meaa square to give the I. value atthe sigoificance 1eve1 wlth (k-1) ana (2 n-k) degrees of freedou.Ifheo the calculated F vaLue is less thaa the value found ia chestati.sti.cal tables, the hypothesls is uot rejected. A calculatedF value grearer thaa Fr1 leads to the conclusion chat the hypothesisls false aod rhe tlro treahtrenrs atre statlstlcalllr dlffereai. rrr"within treaEtreut 'oeaa square is st, therefore, tir" standarddeviation can be obtained by takiog the square root of this value.
Treataent
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Total
(k-l)
(I n-k)(s n-t1
3 .O LEAST SIGNITICA}TT DIFTERENCE TEST
Ihis test cao be used to dete:mine lf there 1s a dlffereoce benreeathe sanple Eeans aod background Eeans.
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, , is coopared to ihe tern on the right sidelarger, Ehe difference is significant.
l
where 7, - ueao for the backgrouud
where I, - mean for the coataoinated saruples
td. - t value from statlsrlcal tables at the ( n_h)degree of freedou and the slgnifl.cance 1evel
Ea = total number of observations
,s-_ - pooled variance which is also rhe wlthioD'' strata aean square froo table D-1.
Tte absolure, ly, - y^of che lnequalirf ; i.f.'
Appendix E
Least-Squares Analysis Documentation
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longitudinal dispersivit y
Hun,.f^mg#.gp Chen-Northern, lnc., Division
350 West 2700 South
Sall Lake City, Ulah 841 1 5
1801 ) 487-3661
Fax [phone]
Prepared for:
THIOKOL CORPORATION
STRATEGIC OPERATIONS
P.O. BOX 689
BRIGHAM CITY, UTAI{ 84302.0689
M.136 GROUND WATER MODELING STI.JDY
EVALUATION OF REMEDIAL ALIERNATWES
Prepared by:
. Chen-Northern" Inc.
350 West 27@ South
Salt I-ake City, Utah 84115
JOB NO. 5-t79-91
B'A .erbe, ol tne lEilfl grouD oi companres
ruNE 1992
TABLE OF CONTENTS
1.0 Introduction
2.0 Site Background2.1 Operational History2.2 Geologr2.3 Ground Water Hydrolory
3.0
4.0
PAGE
1
9
11
11
11
11
11
12
72
1
1
2
J
5
5
7
7
7
Summary of Previous Modeling Studies3.1 Model Description3.2 Model Application
3.2.1 Ground Water Flow Model
3.2.2 Solute Transport Model
Evaluation of Remedial Alternatives4.1 Effea on Ground Water Flow
4.1.1, Flow Model Assumptions
4.1.2 Remedial Alternative #L
4.1.3 Remedial Nternative #2
4.1,.4 Remedial Alternative #3
4.1.5 Remedial Alternative #4
4.1,.6 Remedial Alternative #5
4.2
5.0
6.0
7.0
Effect on Solute Transport
4.2.7 Solute Transport Model Assumptions
4.2.2 Remedial Alternative #1
4.2.3 Remedial Alternative #2
4.2.4 Remedial Alternative #3
4.2.5 Remedial Alternative #4
4.2.6 Remedial Alternative #5
Baseline Risk Assessment
Summary and Conclusions6.1, Ground Water Flow6.2 Solute Transport
13
13
13
1,4
1,4
15
t6
t6
t7
18
18
19References
Figure 2 -
Figure 3 -
Figure 4 -
Figure 5 -
Figure 6 -
Figure 7 -
Figure 8 -
Figure 9 -
Figure 10 -
Figure 11 -
Figure 12 -
Figure 13 -
Table 1-
Table 2 -
Table 3 -
Table 4 -
Table 5 -
Figure 1 -
Figure 14 -
Figure 15 -
Figure 16 -
Figure 17 -
Figure 18 -
Figure 19 -
Figure 20 -
Figure 21 -
Figare 22 -
Figure 23 -
Figure 24 -
Tables
Summary of Aquifer Properties
Summary of Solute Sources
Summary of Retardation Coeffi cient Calculations
Summary of Site Boundary Concentrations
Summary of Baseline Risk Assessment
Figures
Topographic Site Map and Piezometric Surface of Perched and Regional
Aquifers (map pocket inside back cover)
Estimated Piezometric Head Distribution
MODFLOW - Finite Difference Grid Hydraulic Conductivity Distribution
MODFLOW - Finite Difference Grid Boundary Conditions
MODFLOW - Simulated Piezometric Head Distribution
Measured Trichloroethylene (TCE) Concentration Distribution ( 199 1 )RAIID3D - Simulated Trichloroethylene Concentration Distribution ( 1 99 1 )
Measured 1.,1,1-Trichloroethane (TCA) Concentration Disribution (1991)
RANiD3D - Simulated Trichloroethylene Concentration Distribution (1991)
Measured Acetone Concentration Distribution (1991)
RAIID3D - Simulated Acetone Distribution (1991)
Recovery Well Locations for Remedial Alternative #2
MODFLOW - Simulated Piezometric Head Distribution for Remedial
Altertative #2
Recovery Well Locations for Remedial Alternative #3
MODFLOW - Simulated Piezometric Head Distribution for Remedial
Alternative #3
MODFLOW - Simulated Piezometric Head Distribution for Remedial
Alternative #4
Recovery Well Iocations for Remedial Alternative #5
MODFLOW - Simulated Piezometric Head Distribution for Remedial
Alternative #5'
RAIID3D - Simulated TCE Concenuation Distribution for Remedial
Alternative #7 QA\RAl.iD3D - Simulated TCE Concentration Distribution for Remedial
Alternative #1, (2051)
RAIID3D - Simulated TCA Concentration Disribution for Remedial
Alternative #l (2021)
RANID3D - Simulated TCA Concentration Distribution for Remedial
Alternative #7 (2051)
RAI'{D3D - Simulated TCE Concentration Distribution for Remedial
Alternative #2 (2021)
RAI.iD3D - Simulated TCE Concentration Distribution for Remedial
Alternative #2 (2051)
Figure 25 -
Figure 26 -
Figure 27 -
Figure 28 -
Figure 29 -
Figure 30 -
Figure 31 -
Figure 32 -
Figure 33 -
Figure 34 -
Figure 35 -
Figure 36 -
Figure 37 -
Figure 38 -
RAND3D - Simulated TCA Concentration Distribution for Remedial
Alternative #2 (2021)
RAI.ID3D - Simulated TCA Concentration Distribution for Remedial
Alternative #2 (2051)
Cumulative Percent Total Removal of TCE/TCA - Remedial Alternative #2TcE/TcA concentrations in Recovery well Discharge - Remedial
Alternative #2
RAI,ID3D - Simulated TCE Concentration Distribution for Remedial
Alternative # QAI)
RAND3D - Simulated TCE Concentration Distribution for Remedial
Alternative #3 (2051)
RAI.ID3D - Simulated TCA Concentration Distribution for Remedial
Alternative # QA\
RAND3D - Simulated TCA Concentration Disribution for Remedial
Alternative #3 (2051)
Cumulative Percent Total Removal of TCE/TCA - Remedial Alternative #3TcE/TcA concentrations in Recovery well Discharge - Remedial
Alternative #3
RAND3D - Simulated TCE Concentration Distribution for Remedial
Alternative #a Q021)RAIID3D - Simulated TCE Concentration Distribution for Remedial
Altenrative #a Q05l)
RANID3D - Simulated TCA Concentration Distribution for Remedial
Alternative #a Q021)RAliD3D - Simulated TCA Concentration Distribution for Remedial
Alternative #4 (2051)
Cumulative Percent Total Removal of TCE/TCA - Remedial Alternative #4
TCE Concentrations in Recovery Well Discharge - Remedial Alternative #4
TCA Concentrations in Recovery Well Discharge - Remedial Alternative #4
RAI.ID3D - Simulated TCE Concentration Disuibution for Remedial
Alternative #5 (2021)
RAIID3D - Simulated TCE Concentration Distribution for Remedial
Alternative #5 (2051)
RAI{D3D - Simulated TCA Concentration Distribution for Remedial
Alternative #5 (2021)
RAIID3D - Simulated TCA Concentration Distribution for Remedial
Alternative #5 (2051)
Cumulative Percent Total Removal of TCE/TCA - Remedial Alternative #5TCE/TCA concentrations in Recovery well Discharge - Remedial
Alternative #5
Figure 39 -
Figure 40 -
Figure 41 -
Figure 42 -
Figure 43 -
Figure 44 -
Figure 45 -
Figure 46 -
Figure 47 -
Appendix A -
Appendix B -
Appendices
Usting of Projected TCE Concentrations for Monitor Wells 88,
B6/El, E3, and E4.
Listing of Projected TCA Concentrations for Monitor Wells 88,
B6/E7, E3, and E4.
Appendix C - Baseline Risk Assessment by Industrial Health, Inc. (IHI)
M-136 Ground Watcr Modcline Studv
Eraluation of Rcmcdial Altcrnativcs
Thiokol Corporation
Brigham City, Utah
CNI Projcct No.5-1891
1O TNIROpUCTTON
This report presents a portion of the results of a ground water modeling study at the M-136
Burn Grounds Area at Thiokol Corporation's Strategic Operations Facility, located about
20 miles west of Brigham City, Utah. This report has been prepared by Chen-Northern, Inc.
(CM) for Thiokol Corporation (Thiokol) in accordance with Thiokol Contract Number
1GH096. This modeling study is one phase in a series of ground water investigations
involving monitoring well installation, aquifer testing, ground water sampling, and ground
water modeling. In agreement with Thiokol Contract Number 1GH096 and Field Change
Order #OC/,, this report includes the comparison and evaluation of four remedial
alternatives. A separate report outlining the data review aud the physical and numerical
model set-up and calibration was previously issued (CM, 1992). A topographical site map
showing the area included in this study and the location of the monitoring wells and site
structures is presented in Figure 1.
2.0 SIIE BACKGROTJND
The site background has been detailed in numerous previous reports. A summary of the
site history is presented below.
2J Operational History
Thiokol owns and operates a facility identified as M-136 for the open burning of wastes
generated during the manufacnre of solid rocket motors and propellent. Disposal of wastes
at the M-136 facility began approximately in l9A, and continued through the mid-1980's.
Previous geological, hydrological, and monitoring well installation reports made available
by Thiokol include:
o Underground Resource Management, 1985;
. Engneering Science, 1987:'
. Sergent, Hauskins, and Bechrrith (SIB), 1988;
o Christensen Engineering, 1989; and
o Chen-Northern, Inc. (CNI), 1991 and CM, 7992.
1
M-136 Groun<t Warcr Modclioe Studv
Evaluation of Rcmcdial Altcraativcs
Thiokol Corporation
Brigham Ciry, Utah
CNI Plojcct No. 1179-91
A total of 46 monitoring wells have been installed at the facility in the course of the five
previous investigations and are accordingly designated as the A B, C, D, and E series wells.
This information, along with water level elevation measurements and ground water sampling
results provided by Thiokol, were used in the preparation of this report.
22 Geolosv
The site geolory has been discussed in detail in previous reports (SI{8, 1988; CNI, 1991,
1992). The Oquirrh Formation (Pennsylvanian limestone with occasional fine-grained
calcareous sandstone) is the principal formation exposed within the Blue Springs Hills
directly east of the M-136 and Manufacturing Facilities. The regional ground water beneath
the site is largely contained within this formation.
The Salt [ake Group (Tertiary tuffaceous sandstone and siltstone) does not outcrop within
the study area, but has been encountered within wells drilled beneath the center of the M-
136 Facility including monitoring wells A-7,D4, and D-5. Sandstone which may belong to
the Salt lake Group has also been encountered in wells D-3, D-1 (also beneath the M-136
Facility) and west of the Administration Building in well E-7. These deposits are located
above the Oquirrh Formation at or below the regional water table surface.
Unconsolidated and unnamed Quaternary deposits exist across most of the Blue Creek
valley floor and side canyons. Predominately coarser grained colluvium and alluvial fan
deposits exist within the numerous side canyons emanating from the Blue Springs Hills.
These higher elevation deposis are generally nnsanrrated although numerous perched zones
exist within these deposits along the fringes of the Blue Creek valley. Unconsolidated
sedimentary deposits tourards the center of the valley consist of alluvial and lacusrine
sediments, the latter derived from ancestral Lake Bonneville which covered the lower
elevations at the site during the last ice age (about n,W to 11,000 years ago). These
deposits consist primarily of silty sands and gravels with occasional interbeds of clay and silt
througbout most of the study area. Finer grained deposits of sandy silts and clays
predominate within the vadose zone sediments northwest of the Administration Building
(wells E-1,E-2, and B-8), and south of the nuuror rs of Blue Creek Canyon.
The strucnrre of the study area consists of localized and irregular folding and numerous
faults. The Blue Spring Hills reportedly has three sequences of faulting listed below in
chronological order (from oldest to youngest):
a reverse fault dippitrg westward under the site and exposed to the northeast of the
study area;
2
M-136 Ground Water Modcline Study
Evaluarion of Rcmcdial Altcrnatives
Thiolol Corporation
Briglan City, Utah
CNI Projco No.5-179-91
a series of parallel east-west trending faults;
a series of parallel north-south trending nonnal faults.
The location of these faults is generally concealed by surficial deposits and other
unidentified faults may exist. These faults are important, however, since they create
preferred locations for subsurface flow and development of solution channels within the
limestone. Inferred and identified fault locations have been presented in previous reports
(sHB, 1988).
D. Ground Water Hydrologr
A piezometric contour map of the study area, based on water level measurements made by
Thiokol personnel on November 27, 1990 is presented in Figure 1. The wells used to
construct this piezometric contour map are screened at or near the water table surface. This
contour map shows that the regional direction of ground water flow is primarily from north
to south.
Within the northern portion of the study area (M-136 Facility) the ground water flow
patteru is irregular and complex. Flow within this area appears to be dominated by nvo
major features:
The first feature is a ground water mound in the vicinity of well D4. Wastewater was
reportedly discharged in this vicinity at an average rate of approximately 250 thousand
gallons per montl from the mid-1970's until November, 1988. Despite the fact that no
wastewater has been discharged to this area for the last 2.5 years, the ground water mound
has not diminished appreciably. This may result from slow rates of ground water movement
and/or continued drainage of stored water from the vadose zone. The mound may also
originate from natural sources. The ground water mound appears to dominate the flow
directions within the saturated alluvium of the adjacent Blue Creek valley, with ground
water flowing radially away from the mound. The ground water gradient within the alluvium
is relatively flat ranging from a high of 0.008 ftlft near the center of the mound to a low of
about 0.0005 ftlft near the edges of the mound (CM, 992).
The second major feaare is a ground water trough which extends from the M-136 facilities
are4 in the vicinity of wells C-Z arrd possibly 44, towards the downgradient manufacmring
facilities are4 paralleling the base of the Blue Spring Hills. An extension of this trough also
appears to extend southeastrvard toward the vicinity of well E-10. This gound water trough
probably corresponds to fracture zones andlor solution channels developed within the
3
M-136 Ground Warcr Modcline Studv
Eyaluation of Rcmcdial Altcmativcs
Thiokol Corpomrion
Brig[am City, Urah
CNI Projcct No. 5-l?9-91
Iimestone bedrock of this area which may correlate with a north-south trending fault within
tlis area. The regional flow from the northern portion of the study area (M-136 facility)
towards the southern portion of the study area (manufacturing facility) appears to be largely
through this ground water trough which acts as a high conductivity drain or "pipeline". The
action of this trough may be enhanced by the existence of an upfaulted limestone ridge,
which nrns northeast to southwest across the Blue Creek Valley and separates the northern
and southem portions of the study area. This ridge apparently acts as a low conductivity
barrier or ground water dam (CNI,1992).
Within the southern portion of the study area (manufacruring facitities) the direction of
ground water flow is more uniform from north to south. The gradient is steepest, about 0.01
ftf ft, near the upgradient edge where the regional ground water flow enters the area from
the ground water trough described above. The gradient flattens near the downgradient
boundaries of the facility to about 0.001 ft/ft. The change in hydraulic gradient is believed
to result from: 1) the large volumetric inflrrr over a small cross-sectional area of flow near
the upgradient edge; and 2) lower relative hydraulic conductivity of the unconsolidated
sediments within the upgradient areas compared with the fracnued limestone along the
downgradient areas. Solution channels *ithin the limestone were encountered within the
doumgradient wells E-3 and E-7 (CM, 1991).
Ground water inflow into the area is probably derived from subsurface flow from the upper
reaches of Blue Creek Valley and infiltrating snowmelt and subsurface flow from the Blue
Spring Hitls. Several perched and confined aquifer zones are reported to exist within
fractured and brecciated zones of the limestone and quanzite strata within the Blue Spring
Hills directly east of the M-136 Facility. These zones have piezometric heads some 200 to
250 feet higher than the neigbboring regional aquifer and are probably recharged by
infiltrating precipitation within the Blue Spring Hills. Ground water within one of the more
continuous perched zones within the eastern portion of the M-136 Facility flows towards the
ezut at a gradient of about 0.003 ft/ft (CM,1991).
The hydraulic and transport properties of the formations beneath the study area are
surnmarized in Table 1. The hydraulic conductivities and porosities are based on the well
test analyses presented in the CNI 1991 report. Porosities are also based on published data
for the general rock and soil types present at the site (Fetter, 1980; Davis and DeWiest,
1966; Tod4 1959).
Florv through fractured limestone or within open solution channels in limestone is similar
to flow through a network of pipes. While such a network differs from traditional porous
medi4 specifically in the size and scale of individual flow conduits, porous media
4
M-136 Ground Watcr Modclins Studv
Eraluation of Rcmcdial Altcrnati\rcs
Thiokol Corporation
Brigham City, Utah
CNI Projcct No.5-1D91
equivalency is commonly assumed when simulating flow through fractured rock. This
approach implicitly assures a representative elementary volume (REV) exists such that
volumes of the flow media greater than the REV do not exhibit scale dependent properties.
The REV for fractured media is larger than that for porous media. Hence for regional
numerical flow simulations where the individual model elements are expected to be larger
than the REV for the fracnrred media, assuming porous media equivalency usually produces
satisfactory results. For aquifer tests which are dominated by a relatively small flow regime
close to the well, assuming porous media equivalency is usually not appropriate. Specifically
individual aquifer tests are determined by the major hydraulic conduits intersected by the
well bore yielding relatively high conductivities where the well bore intersects major flow
conduits and relatively low conductivities (more indicative of the intact or unfractered rock)
where the well bore does not intersect major flow conduits.
u sLtMrr4ARy oF pREvrous MoDELTNG STUDIES
A nro-dimensional steady-state ground water flow and solute transport model for the M-136
Burn Grounds Area of Thiokol Corporation's Strategic Operations.Facility has been
developed and calibrated. Details of the model assumptions, application and calibration
were presented in a previous report (CNI, 1992).
!.l Model Description
Ground water flow modeling was simulated using the United States Geological Sunrey
Modular Finite-Difference Ground Water Flow Model or MODFLOW (McDonald and
Harbaugb, 1988). MODFLOW is a quasi-three-dimensional (layered trvo-rlimensional)
finite-difference ground water flow model. In applying the finite difference method the area
of interest is divided into blocks by superimposing a rectangular grld over the modeled area
in plan view. Each block is then assigned aquifer parameters corresponding to the acnral
or estimated aquifer parameters ursociated with that block. For steady state simulations
aquifer transmissiviry (or conductivity for unconfined conditions) is the only aquifer
parameter required. Transmissivities are altered for changes in water table elevation
(saturated aquifer thickness) under unconfined aquifer conditions. For transient flow
simulations, aquifer storativity (or storage coefficient) is also required.
MODFLOW computes the quantity of ground water flow benveen adjoining blocls based
on Darcy's I-aw for incompressible isothermal fluid movement in a porous mediun, and
mass balance assuming changes in storage are a function of only aquifer compressibility (or
water table fluctuation under unconfined water table conditions).
5
M-136 Ground Watcr Modcline Studr
Evaluation of Rcmcdial Altcrnativcs
Thiokol Corporation
Brigham City, Utah
CNI Projcct No. 5-179-91
For three dimensional models, multiple horizontal layers, each with identical rectangular
grids but different aquifer properties, are defined. Venical cross flow between layers is
simulated by defining a vertical conductance (hydraulic conductivity divided by flow path
lengrh) benveen layers. Where aquitard layers are present the vertical conductance is
defined by the venical aquitard conductivity and thickness. Where no aquitard layer is
present, the vertical conductance is defined by the vertical aquifer distance benveen
adjoioing layer nodes aDd the vertical.aquifer conductivity.
Solute transport was simulated using RAIID3D, a tlree-dimensional solute transport model
which uses the random-walk algorithm and the MODFLOW Model oulput (Koch, Mattejat,
and Prickett, 1989). RAI.ID3D is a three dimensional version of the random-walk algorithm
originally developed as a method for solving one-dimensional ground water solute transport
problems. The random-walk technique is based on t}re concept that dispersion in porous
media is a normally distributed random process which can be simulated by tracking the
motion of numerous individual panicles. This statistical solution method eliminates the
numerical dispersion and stability problems associated with finite-element/finite-difference
solutions of the diffusion equation. Each particle is expressed as a fixed mass of given
solute. In the model, the motion of individual particles follows nvo paths through an aquifer
flow system. The convective motion is along the mean flow path (streamline), and the
dispersive motion is a normally distributed random motion governed by the convective flow
path length and the longitudinal and transverse dispersivities. Venical mixing for
multilayered systems is controlled by the vertical dispersivity benneen model layers.
Due to the random (statistical) nature of the model, a suffrcient number of particles must
be utrlized in the model to provide definition of the concentration distribution of the
chemical evaluated. Concentrations are calculated from panicle distributions by summing
the particle mass (number of particles times individual particle mass) within a specified
aquifer volume 6d diyirling by the corresponding ground water mass within the aquifer
volume.
RA]{D3D was designed to function using the output of MODFLOW as input. A
preprocessor (PREMOD3D) allows the final head data output from MODFLOW to be
converted to ground water flures (apparent velocities) between adjacent model blocks which
are then input to RA}.ID3D. Solute tra$port is then interactively simulated by introducing
contaminant "particles" at specific locations (source areas) within the model boundaries.
The particles are moved through a series of user defined time steps. During each time step
the particle is first moved coilrectively using the apparent velocity vectors calorlated by
PREMOD3D. Each panicle is subsequently moved a random distance parallel and
perpendiorlar to the particle streamline. The magnitude of these components of random
6
M-136 Ground Watcr Modcline Srudv
Baluation of Rcmcdial Alrcmativcs
Thiokol Corpontion
Brigbam City, Utatr
CNI Projcct No. 5-179-91
dispersive movement is defined by a normal density distribution with a mean of zero and
a standard deviation proportional to the square root of the dispersivity (longitudinal or
transverse) and the convective path lengt}.
32 Model Aoolication
32.1 Ground Water Flow Model
The Thiokol M-136 area was modeled using a single layer, 43 column by 19 row grid aligned
approximately parallel to the primary direction of ground water flow (nonh to south). Each
block within the grid is square in plan view and measures 400 feet on a side. Unconfined
aquifer conditions were utilized in the model. This single-layer model was used in
formulating and calibrating the ground water flow model.
A tno-layer model was subsequently developed solely to accommodate the solute trarxport
model requirements. Identical geometry and hydraulic conductivities were incorporated in
both horizontal layers, and the vertical conductance was chosen so as to effectively simulate
x singls aquifer layer and perform a npo-dimensional simulation The upper layer was
modeled as an unconfined aquifer and the lower layer as a confined aquifer. Results of the
two layer model simulation were verified by comparison with the original singls layer model.
No significant differences were observed between the avo simulations.
The piezometric head distribution based on measured water elevations and extrapolation
of these mernurements (Figure 2) was closely simulated by MODFLOW using the hydraulic
conductivity distribution shown in Figure 3. This conductitity distribution is based upon
material qpe and inferred fault or fracnrre (high conductivity) zone locations. Boundary
conditions for the numerical model, shown in Figure 4, were estimated by extrapolating
piezometric contour data from existing well measuremeDts. A singls fixed head node was
utilized to simulate the ground water mounding beneath the M-136 facility. The model was
calibrated by trial and error to obtain a close approximation of the measured piezometric
surface. Comparison of hydraulic conductivities utilized in the calibrated model with those
obtained from aquifer tests (Table 1) show close agreement. The piezometric head
disribution obtained with the final calibrated model is presented in Figure 5.
322 Solute Ttansport Model
The initial solute transport model calibration was performed using gound water sarrple
results for trichloroethylene (TCE) collected by Thiokol personnel in November/December
1990 and March 1991 (Figure 6). TCE was chosen to initially calibrate the solute transport
7
M-136 Gmunr! Watcr Modclinq Study
Erraluation of Rcmedial Altcrnati\Gs
Thiotol Corponrion
Brighan City, Utah
CI.II Projcct No. 5-179-91
par:rmeters due to the it's longer history of usage at the site and more widespread
observance across the site. As not all wells were sampled during any single sampling round,
results from nvo consecutive sampling events were used to provide more complete areal
information on the $ound water plume. The other solutes used during model simulations
were L,L,1-trichloroethane (TCA), and acetone.
In order to simulate TCE transport, TCE particles were introduced to and tracked within
the model from time zero (1962), continuously through a time period of 12 years (until
1974). This time period corresponds to the approximate time period when TCE was used
and disposed on site. In order to compare the model results with the most recent sampling
data (November/December 1990 and March 1991; Figure 6), the particle movement was
tracked for an additional 17 years and the oulput compared to the sampling data. The
source areas, or locations where TCE particles were'input, were chosen based upon
information provided by and discussed with Thiokol as well as characteristics of the
measured ground water plumes. The five source areas used are listed in Table 2. The time
of solute transport through, and the lateral movement and attenuation within the vadose
zone were not simulated in the model.
The source strength is dependant upon both the number of particles input to the model and
the mass of each particle. Both the particle number and mass were varied during initial
model calibration to obtain a close match to observed solute concentrations ne.u the source
area. This approach was used as solute concentrations near the source areas are relatively
independent of the solute transport parameters (dispersivity and retardation coeffrcient) and
the amount of TCE disposed on site is uot acorrately known. The number of particles and
the particle mass used in the final calibrated model are listed in Table 2. The computed
TCE concentrations at the end of 29 years from the start of the simulation are presented
in Figure 7.
Both TCE and TCA were thought to have emanated from the same general source areas.
Therefore the five source areas listed in Table 2 were used for both solute transport
simulations. Time zero is approximately 1974 for TCA and corresponds to the time at
which TCE use was discontinued and TCA use was initiated. TCA panicles were
introduced to and uacked within the model from time zero (1974) continuously through a
time period of l?years (until 1986), which corresponds to the approximate time period TCA
was disposed on site. In order to compare the model results with the November-December
1990/March 1991 sampling data for TCA (Figure 8), the particle movementwas tracked for
an additional5 years and the output compared to the sampling data- The particle number
and mass were determined in exactly the same manner as described for the TCE
simulations. The number of particles and the particle mass used in the final calibrated
8
M-136 Ground Watcr Modcline Studv
Evaluation of Rcmcdial Altcrrativcs
Thiokol Corporarion
Brigham City, Utah
CNI Projcct No. 5-179-91
model are listed in Table 2. The computed TCA concentrations at the end of 17 years from
the start of the simulation iue presented in Figure 9.
Based on the observed gound water plume and site history, acetone is thought to have
emanated from only three of the five source areas used for the TCE and TCA simulations.
These source areas are lisrcd in Table 2. In orber to simulate acetone transport, acetone
particles were introduced into and tracked within the model from time zero (1974)
continuously through a time period of 72 years (until 1986), which corresponds to the
approximate time period acetone was disposed on site. In order to compare the model
results with the most recent and complete May 1990 sampling data (Figure 10), the particle
movement was tracked for an additional 4 years and the output compared to the sampling
data. The particle number and mass were determined in exactly the same manner as
described for the TCE and TCA simulations. The number of panicles and the particle mass
used in the final calibrated model are listed in Table 2. The computed acetone
concentrations at the end of 16 years from the stan of the simulation are presented in
Figure 11.
Model calibration involved varying the input parameters to the RAIID3D model, executing
the model over a specific time interval, and comparing the model results at the end of the
interval to the actual ground water sampling results for late 7990/eaiy 1997. Model
sensitivity analysis involved changing one of the input parameters while keeping the
remaining parameters constant. Further details of the solute traDsport model calibration
were presented in a previous report (CNI, 1992).
Ground water traosport of the dissolved chemical constituents trichloroethylene, 1.,L,1-
trichloroethane, and acetone were simulated using the calibrated ground water flow model,
calculated estimates of solute retardation coeffrcients, and calibrated values of porosity and
dispersivity. The transport parrrneters utilized in the calibrated traosport model are
summarized in Table 1. The solute retardation coefficient calculatiors are summarized in
Table 3. Both the retardation coeffrcients, which are different for all three compounds, and
the porosity values used in the model appear to fall in the midpoint of values estimated
from published data. The same dispersivity values were found to result in accurate solute
transport simulations for all three modeled compounds, despite differences in the time of
solute release and transport, and retardation coefficients.
{ EVALUATION OF REMEDLAL ALTERNATTT/ES
The previously developed and calibrated ground water flow and solute transport model was
used to evaluate remedial alternatives involving recovery wells to remove and treat ground
9
M-136 Ground Watcr Modelins Studv
Evaluation of Rcmcdial Altcrnativcs
Thiokol Corporation
Briglam City, Utah
CNI Projcct No. 5-179-91
water containing TCE and TCA. Considerationwas glven to five separate remedial optiorrs:
1) Remedial Alternative #1. 'no action;
2) Remedial Alternative #2 - four recovery wells in the southern portion of site;
3) Remedial Alternative #3 - three recovery wells in the northern portion of
site;
4)Remedial Alternative #4 - four recovery wells in the southern ponion/three
recovery wells in the northern portion of site;
s)Remedial Alternative #5 - six existing monitoring wells in the southern
portion of the site.
The no action alternative provides a basis for comparison of the effectiveness of the other
four remedial alternatives. Separate consideration of wells within the northern and southern
areas of the site results from the existence of separate groupings of source areas within tlese
two areas. All five alternatives were evaluated over a sixty-year period (1991 to 2051)
assuming steady-state ground water flou, conditions. Each recovery well used in remedial
alternatives 2,3, and 4 was assumed to have a sustainable yield of 100 gallons per minute
(gpm), avalue whichwas believed to be re$onable given the average aquiferproperties and
proper well constnrction. Existing monitoring wells used as recovery wells in remedial
alternative 5 were assigrred pumping rates estimated by Thiokol from aquifer tests. The
effectiveness of each alternative was evaluated on the alteration of steady-state ground water
flow patterns and their predicted effect on TCE and TCA migration.
Although acetone was utilized in the model calibration, acetone was not included in the
evaluation of remedial alternatives because:
acetone was not encountered as frequently as TCE and TCA;
measured concentrations of acetone were considerably lower than for TCE
and TCA;
a
a
acetone is considerably less toxic than TCE and TCA;
where acetone is found, TCE and TCA are also found, indicating that removal
of TCE and TCA should also remove acetone.
a
a
10
M-15 Ground Watcr Modelins Studv
Eyaluation of Rcmedial Alrcrnatlves
Thiokol Corporarion
Brigbam City, Utah
Ct{I ftojcct No.5-1891
il Effect on Ground lVater Flow
4.1.1 Flow Model Assumptions
The simulation of ground water flow conditions at the project site using MODFLOW
includes several assumptions:
Ground water flow is horizontal throughout the study area;
Water bearing sediments in each different hydraulic conductivity area are
homogeneous and isotropic;
The overall mass balance of the ground water system remains constant
throughout the sixty year period of our modeling scenario.
4,12 Remedial Alternative #1
Under remedial alternative #1 (no action) no recovery wells were emplaced and glound
water flow was assumed to remain constant in accordance with the piezometric head
distribution presented previously in Figure 5.
4.13 Remedial Alternative #2
For remedial alternative #2, a total of four recovery wells (RW-l through RW-4) were
placed within the southern ponion of the site to preveDt off site migration of TCE and TCA.
The well locations are shown in Figure 12. The resultant piezometric surface with the
inclusion of these four wells is shown in Figure 13. Under steady-state conditions, the wells
created a ground water depression to intercept ground water flow within the southwestern
portion of the model. Drawdown within the individual wells was 5 to 12 feet, with the
greatest drawdown occurring near the centennost wells (RW-2 and RW-3). The wells also
influence ground water flow within the northern portion of the site, effecting the existing
radial flow pattern surrounding the ground water mound in the northern alluvial basin.
4.1.4 Remedial Alternative #3
For remedial alternative #3, a total of three recovery weUs (RW-5 through RW-7) were
placed in the northern portion of the site in an effort to contain TCE and TCA migration.
The well locations are shown in Figure 14. The resultant steady-state piezometric surface
is shown in Figure 15. Wells RW-5 and RW-6 were placed within a high conductivity (250
o
a
11
M-136 Ground Watcr Modclinq Studv
Evaluation of Rcmcdial Altcmatirrrs
Thiokol Corporation
Brigian City, Uah
C[.{I Projcct No. 5-1891
ft/day) zone in the north central portion of the study area. Althougb these wells created
4 to 6 feet of drawdown within this zone and flattened the hydraulic gradient throughout the
zone, they did not create a ground water depression sufEcient to reverse the flow gradient
and completely contain solute migration from the northern source areas. This could be
because the high conductivity appears to act as a collector for $ound water inflow within
the northern portion of the model. Hence to create a ground water depression sufficient
to entrap all solute migration from the northern source areas, the pumping volumes would
need to be very higb and the corresponding solute concentration within the pumped water
would presumably be very low due to dilution. Both factors would increase recovery and
treatment costs. Well RW-7 was placed in the alluvial sediments directly south of the high
conductivity zone. The drawdown in well RW-7 is about 20 feet, of which approximately
15 feet is directly associated with this individual well. Although this well creates a small
localized ground water depressiorl the radius of influence of well RW-7 is limited to about
500 feet, suggesting that many such wells may be required to impact the entire oorthern
plume. Hence containment of the northern source areas is not as effectively implemented
zN containment of the southern source areas.
4.1.5 Remedial Alternative #4
Remedial alternative #4 involves the simultaneous pumpage of both the northern and
souttrern source areas. The desired result of pumping both areas i5 1s 6iaimize migration
from the northern source areas and hasten the entire remedial process. The well locations
and capacities for this combined placement of seven recovery wells is identical to that used
for the previous two recovery well scenarios. The resultant piezometric surface is shown in
Figure 16. This combined pumpage has little additional effect on the observed ground water
depression within the southern portion of the site except to increase the total magnitude of
the drawdown. The flattening of the gradient within the nonhern portion of the site within
the higb conductivity zone is decreased and so the degree of containment offered by
pumping the northern portion of the site is slightly diminished.
4.1.6 Remedial Alternative #5
The final alternative considered is the use of six existing ground water monitoring wells as
recovery wells. The wells used and the pumping rates assigned are:
E4 5 gpmE-5 15 pmB-6 80 gpm
E-1
E-2
E-3
g)m
g)m
g)m
15
t2
80
t2
M-136 Ground Watcr Modcline Studv
Erraluadon of Rcmcdial AJtcrnatirrcs
Thiokol Corporation
Brigbam City, Utah
CM Projet No. tl79-91
The well locations are shown in Figure 17. The resultant steady-state piezometric surface
is shown in Figure 18. These wells created drawdowns of betureen approximately one and
three feet. A itight overall decrease in ground water elevation can be seen in the southern
portion of the site. This could be due to the fact that these wells are located in relatively
high permeability sedimens and are pumped at lower rates then the recovery wells in
remedial alternatives 2,3, and 4, creating a cumulative effect of a slightly decreased water
table. The wells also influence ground water flow within the nofthern portion of the site.
42 Effect on Solute Migration
The effectiveness of the proposed remedial alternatives on solute removal and off-site
migration were evaluated for both TCE and TCA The final (1991) particle distributions
obtained from the calibrated solute transport model (Figures 7 allld 9) were used as the
initial particle distributions for the model prediction of future TCE and TCA migration. No
additional solute particles were introduced into the model. Simulations were conducted over
a 60 year period (1991 to 2051) and results output for each ten year period. Model results
included concentration distributions, number of particles removed from each recovery well,
and concentration of solute in water removed from each recovery well. The concentration
distributions were obtained as the average concentration over square segments of the model
measuring 1000 feet on a side.
42.1 Solute llansport Model Assumptions
Execution of the RAIID3D model assumes the following:
The concentration of contaminants is equally distributed throughout the
entire thickness of the modeled aquifer;
Solute traosport parzrmeters are constant throughout the modeled domain
(i.e. porosity, dispersion, retardation).
a
a
422 Remedid Altemative #1
The solute concentration distributions for the years 2V2l aad 2051 under remedial
alternative #1 (no action) are presented in Figures 19 and 20 for TCE and Figures 27 and
22 for TCA As evident from these figures, TCE and TCA continue to migrate southward
through the model increasing in concentration near the southern and southwestern
boundaries of the model. The highest concentrations of TCE and TCA near the
ig
M-136 Ground Watcr Modclins Study
Elaluatioo of Rcmcdial Altcrnatilrcs
Thiokol C.orporation
BrigDam City, Utah
Ci.{I Projco No. 5-179-91
northernmost source areas do not decrease significantly by the year 2051, and migration of
TCE and TCA towards the southern portion of the site continues. Conversely, the highest
concentmdons within the southemmost source areas have significantly decreased and are
displaced sout}ward by the year 2051. Because particles can not leave the south end of the
model, panicles accumulate within the model blocks bordering the southern end of the
model by the year 2051. This accumulation is due to finite dimensions of the model and is
ignored in the concentration distributions presented.
423 Remedial Alternative #2
The solute concentration distributions for the years 2021. and 2051 under remedial
alternative #2 (fow recovery wells within the southern portion of the site) are presented in
Figures ?3 and 24 for TCE and Figures 25 and 26 for TCA Placement of recovery wells
in the southern portion of the site appears to prevent the southward off-site migration of
both TCE and TCA Concentrations within the northernmost portion of site decrease
sligbtly, showing minor improvement over the no action alternative. Maximum
concentrations within the southemmost ponion of the site decrease significantly, although
concentrations upgradient of the recovery wells increase due to migration of TCE and TCA
from the northern portion of the site.
Cumulative percentage removal of the total mass of TCE and TCA present within the
ground water via the recovery wells is presented in Figure 27. Both TCE and TCA are
removed at similar rates when compared on a total percentage basis. Mass removal is
relatively efficient during the first 20 yean of operation (about 20 to 22 percert total
TCE/TCA removal) but decreases gradually during latter years resulting in only about 25
to 30 percent total TCE/TCA removal after 60 years of operation. The declining efficiency
of the recovery well removal could be a result of declining concentrations in the vicinity of
the recovery wells. As the recovery wells locally reverse the direction of ground water flow
near the southern limit of the TCE/TCA plume, the recovery wells begn to define the
soutlern limit of the plume and uncontaminated ground water begins to mix with
cootaminxled ground water at the well. The average predicted TCE/TCA concentrations
of the recovery well discharge are presented in Figure 28. Both TCE aod TCA
concentrations within the recovery well discharge decrease during the fint 30 years of
operation but remain relatively constant over the final 30 years of simulated operation.
42,4 Remedial Alternative #3
The solute concentration distributions for the years 2021 afi 2051 under remedial
alternative #3 (three recovery wells within the northern portion of the site) are presented
t4
M-135 Ground Water Modclinq Studv
Eraluation of Rcmedial Altcrnalivcs
Thiokol Corporation
Briglam City, Utah
Cl.{I Projcct No. 5-179-91
in Figures 29 atd 30 for TCE and Figures 31 and 32 for TCA. Placement of recovery wells
in the northernmost portion of the site appears to limit migration from the northern source
areas to a greater extent than expected from hydraulic considerations alone. This effectively
reduces the increase in concentrations in the southwestern portion of the site. The average
concentrations within the northemmost portion of the site also dectease, although the
ma,rimum concentrations do not decrease in a similar manner. Southward migration of TCE
and TCA from the southemmost source areas continues in a similar manner to, but at a
slightly slower rate than, that observed for the no action alternative.
Cumulative percentage removal of the total mass of TCE and TCA in ground water is
presented in Figure 33. Mass removal is slightly more efficient than for remedial alternative
#2 resulting in between 30 and 40 percent total TCE /TCA removal after 60 years of
operation. This increased efficiency is at least partialy attributable to the higher Proportion
of particles and higher ground water concentrations of TCE and TCA within the northern
portion of the site. Removal efficiency of TCA on a percentage basis is higher than for
TCE presumably since TCA has migrated less distance from the source area (because of a
more recent history of usage) than TCE. Average predicted concentrations of TCE and
TCA in the recovery well discharge are presented in Figure 34. Discharge concentrations
of both TCE and TCA generally decrease during the first 30 years of operation but aPpear
to stabilize during the subsequent 30 years. TCE concentrations decline about 30 percent
over the entire 60 year period of simulated operation.
42.5 Remedial Alternative #4
The solute concentration distributions for the years 2021. and 2051 under remedial
alternative #4 (recovery wells in both the northern and southern portions of the site) are
presented in Figures 35 and 36 for TCE and Figures 37 and 38 for TCA Placement of
recovery wells at both ends of the site appears to prevent off-site migration along the
southern and southwestem site boundaries. Ma:cimum concentrations within both the
northern and southern ponions of the site are similar to those observed under remedial
alternative #Z,however the areal extent of high concentrations is limited at both locations.
By the year 2051, the southern extent of the TCE plume has retreated and the southern
recovery wells are pumping water with relatively low TCE concentrations.
Cumulative percentage removal of the total mass of TCE and TCA Present within the site
ground water is presented in Figure 39. As solute is being removed at both locations, the
iate of recovery is comparable to the combined rate of both options considered separately.
After 60 years of operation, about 50 to 60 percent of the total mass of TCE/TCA has been
removed. Removal efEciency declines with time as discussed in Sections 4.2.2 and 4.2.3.
is
M-136 Ground Watcr Modclinq Studv
Erraluation of Rcmcdial Altcmatiws
Thiokol Corporation
Brig[am City, Utah
CM Projcct No.5-179-91
Predicted concentrations of TCE within the northern and southern recovery wells are
presented in Figure 40. TCE concentrations within tle northern wells are only slightly lower
and TCE concentrations within the southern wells are only slightly higher than for the
separate recovery well dternatives previously presented. Average predicted concentrations
of TCA within the northern and southern recovery wells are presented in Figure 41. TCA
concentrations within the northern wells decline more rapidly initially before leveling off to
the same concentrations observed for the northern recovery wells operating alone. TCA
concentrations within the southern wells is higher during the first 40 years of operation, but
lower thereafter when compared to the southern recovery wells operating alone.
42.6 Remedial Alternative #5
The solute concentration distributions for the years 2021 and 2051 under remedial
alternative #5 (six existing monitoring wells used for ground water recovery) are presented
in Figures 42 and 43 for TCE and Figure 44 arrd 45 for TCA Due to the close proximity
of wells E-3 and E4, and the scale at which RAIID3D was examined, wells E-3 and E4
appear as a single recovery well on these figures. Maximum concentrations within both the
northern and southern portions of the model are similar to those observed in remedial
alternative #1, although migration of TCE and TCA solute plumes does not appear to be
as extensive. Cumulative percentage removal of the total mass of TCE and TCA in ground
water is presented in Figure 46. Mass removal is the least efEcient of any of the four
recovery well scenarios, resultingin 4 to 7 percent total TCE/TCA removal after 60 years
of operation. This removal efEciency is at least partly attributable to well placement and
pumping rate. Average predicted concentrations of TCE and TCA in recovery well
disc[arge are presented in figure 47. Discharge concentrations of TCE and TCA begin to
increase after 20 years of recovery, indicating that the recovery wells are not greatly
impacted by solutes until the year 2011. Concentrations begin to increase at this time and
seem to level off after 50 years of recovery for TCE. Concentrations of TCA increase at
a slower rate, and do not appear to level off in this 60 year model scenario.
il BASELINE RrSK ASSESSMENT
A baseline risk assessment wils performed to evaluate human health risks resulting from
hlpothetical human exposure to ground water containing TCE and TCA The baseline risk
assessment analysis wzts conducted by Industrial Health Incorporated (IHI) under the
direction of Dr. Bobby Craft, a certified industrial hygienist. This analysis is included as
Appendix C of this reporl
16
M-15 Ground Watcr Modclinc Studv
Evaluation of Rcmcdial Altcmatives
Thiokol Corporation
Brigham Gty. Utah
CNI Projcct No. 5-179-91
For the pulposes of this risk assessment, ground water concentrations of TCE and TCA
along the downgradient boundary of the facility were determined using the solute transport
model. TCE and TCA concentrations were determined for remedial alternatives 1, 2,3 and
4 at monitor well locations B8,B6|E7, E-3, and E-4 for the 60 year period 1991 to 2051,.
Remedial alternative #5 was conducted after the initid risk assessment wru complete.
These data are presented in Appendices A and B. The maximum concentrations of TCE
and/or TCA and their locations are presented for the four remedial alternatives in Table
4. It is evident from this comparison that both remedial alternatives #2 arnd #4, both of
which involve the pumping of the southern recovery wells create reductions in maximum
concentrations along the site boundary, while pumping of the northern recovery wells alone
causes little change.
The risk assessment utilized the highest predicted ground water concentration (of the four
monitor well locations 88/ B6lE7, E-3, and E-4) at the site boundary. E:rposure levels were
based on the average concentration over a thirty year period (L991-2020 or 2021-2050,
whichever was higher). Exposure pathways considered in the study included human
exposure resulting from domestic use of ground water by ingestion (drinking water
consumption) and vapor inhalation during showering. It is important to note that this
exposure pathway is hlpothetical and it is believed that no complete exposure pathways for
human receptors extist in the immediate vicinity of the site.
The evaluation of risk to human receptors for this hypothetical exposure pathway is
summarized in Table 5 for both carcinogenic and non-carcinogenic health risk. The
associated cancer risk ranges from 1 in 1000 for remedial alternatives 1 and 3, to between
2 and 3 in 100,000 for remedial alternatives 2 atd4. For the non-carcinogenic health risks,
if the hazafi quotient exceeds one, there is generally a concern for non-carcinogenic health
effects. As seen from Table 5 the hazard quotient exceeds one only for remedial
alternatives 1 and 3. In summary, placement of recovery wells within the southern portion
of the site provides plume ssaleinmsnt to effectively eliminate non-carcinogenic health risks
and reduce carcinogenic health risks to less than 3 in 100,000 for this 'Vorst case"
hlpothetical exposure route.
6.0 ST]MII{ARY AI{D CONCLUSIONS
A npo-dimensional ground water flow and transport model for the M-136 Burn Grounds
Area of Thiokol Corporation's Strategic Operations Faciliry has been developed and
calibrated to existing data- Ground water flow modsling wzls simulated using the
MODFLOW finite-difference model. Solute transport was simulated using the RA}.ID3D
random-walk model.
t7
M-136 Groun<t Watcr Modcline Studv
Eraluation of Rcmcdial Alteroarwcs
Thiokol C.orporation
Brigbam Oty, Utah
Ct'U Projc.t No. 5-179-91
6,1 Gnound Water Flow Model
The piezometric head distribution was simulated by the numerical model using hydraulic
conductivity distributions based on material t)?e and inferred fault or fracture zone
locations. Boundary conditions iue approximate and were estimated by extrapolating
piezometric contour data from existing well measurements. The hydraulic conductivity
values utilized in the model agree with estimates of hydraulic conductivity from aquifer tests.
Steady-state ground water flow simulations were conducted using four different recovery well
placement alternatives. The alternative of providing no recovery wells was also evaluated
as a baseline or no action alternative.
62 Solute Thansoort Model
Ground water transport of the dissolved chemical constitueDts trichloroethylene, 1.,1,1-
trichloroethane, and acetone were simulated using the calibrated ground water.flow model,
calculated estimates of solute retardation coefEcients, and calibrated values of porosity and
dispersivity. Both the retardation coefficients, which are different for all three compounds,
and the porosity values used in the model appear to fall in the midpoint of values estimated
from published data. The same porosity and dispersivity values were found to result in
accurate solute transport simulations for all three compounds modeled, despite differences
in the time of solute release and transpo4 and retardation coefficients.
For the five remedial alternatives considere( solute transport modelingwas conducted using
the solute concentration distributions obtained with the calibrated model for the year 1991,
and predicting solute transport over a 60 period until the year 2051. These simulations show
that if unabated, TCE and TCA may migrate off site near tle southern and soutlwestern
boundaries of the study area. Off site migration may be decreased or eliminated by
placement of recovery wells within the southwestern portion of the study area Placement
of recovery wells within the northern portion of the snrdy area were of limited effectiveness
in preventing further migration of TCE and TCA but appear to be effective in accelerating
the rate of site remediation. Recovery of TCE and TCA from the ground water beneath
the site is expected to be gradual under the remedial alternatives examined. After 60 years
of operation (1991 to 2051), 25 to 60 percent of the total mass of TCE and TCA present
in the ground water would be recovered. The most rapid recovery rates were obtained by
pumping both the northern and southern portions of the study area.
i8
\-.
M-136 Ground Watcr Modclinq Studv
Eraluation of Rcmcdial Allcrtativcs
Thiolol Corporation
Brigham City, Utah
CNI Projcct No. 5.l79.9l
ru. REFERENCES
Chen-Northern, Inc., 1.991, "Report of Monitoring Well Installation and Hydrologic
Investigation, Wasatch Operations Facility", Unpublished Report to Thiokol Corporation.
Chen-Northern, Inc., 1992,"M-136 Ground Water Modeling Snrdy'', Unpublished Report to
Thiokol Corporation.
Christensen Environmental Engineering (1990), "Report of Monitoring Well Installation at
M-146, Thiokol Corporation", Unpublished Report to Thiokol Corporation.
Davis, S.N., and DeWiest, R.J.M., 1966. H),drogeology. John Wiley & Sons, New York, New
York.
Engineering Science (1986), "Preliminary Geohydrologic Evaluation of M-146 Burning
Grounds", Unpublished Report to Morton Thiokol, Inc.
Engineering Science (1987), "Characterizatton of Hydrogeologic Setting Beneath the M-146
Burning Ground Ponds", Unpublished Report to Morton Thiokol, [nc.
Fetter, C.W., 1980. Applied H)drogeologv. Charles E. Merrill Publishing Co., Columbus,
Ohio.
Freeze, RA, and Cherry, JA Ground water. Englewood Clift, New Jersey: Prentice-Hall
ltc., 1974,604 p.
Koch, D., Mattejat, P., and Prickett, T., 1989. Three Dimensional Solute Transport Using
the Random-Walk Algorithm and MODFLOW (RAND3D). Fnginesring Technologies
Associates, Irc., 102 p.
McDonald, M.G, and Harbaugh, AW., 1984. A Modular Three-Dimensional Finite-
Difference Ground Water Flow Model, USGS Open File Report 8+875.
Montgomery, J.H., and Welkom, L.M., 1990. Ground water Chemicals Desk Reference.
I-ewis Publishers, Chelseq Michigan, 6a0 p.
t9
M-136 Grcund Watcr Modcline Studv
Evaluation of Rcmcdial Altcmalivcs
Thiokol Corporation
Brigham City, Utsh
CNI Projcct No. 5-179-91
Sergent, Hauskins, and Bechvith (1988), "Report for Geohydrologic Investigation M-146
Facilities Area Morton Thiokol, Inc., Box Elder Counry, IJtah", Unpublished Report to
Morton Thiokol, Inc.
Todd, D.K, 1959. Ground Water Hydrolo$r. John Wiley & Sons, New Yorlg New York.
Yin, S.C.L, ild Chiu, S-y., no date. "Modeling Ground Water Transport of Dissolved
Gasoline and Using the Results to Evaluate Aquifer Restoration Processes", Energy and
Environmental Systems Division, Argonne National I-aboratory, Argonne, Illinois.
20
TABLES
Table r - SLTMMARY OF AQUIFER PROPERTIES
Material Type Hydraulic
conductivity
(ftlday)
Effective
porosity
(Vo)
Hydraulic
gradient (ftlfO
Longitudinal
dispersivity (ft)
Transverse
dispersivity
(f0
Site Model Estimated Model Measured Model Model
Unconsolid.
sediments
ltol0 3to15 20 to 35 20 0.0005 to 0.008 150 l5
Unfractured
limestone
0.1 to I 0.5 to I ltol0 20 0.0005 to 0.008 150 15
Fractured
limestone
lfi) to
lm0
75 to
250
I to 100 20 0.0005 to 0.008 150 l5
TABLE 2: SIJMMARY OF SOLUTE SOITRCES
Source Area Name TCE Particles lrlrl-TcA Particles Acetone Particles
Number Mass (lbs)Number Mass (lbs)Number Mass (lbs)
Liquid Thermal Treatment Areas #15,
16, 17, l8
1500 50 1500 25 lm0 20
Liquid Thermal Treatment Area #8 729 50 729 25 2500 20
Flammable Solvent Pit,fr208 729 50 729 25 2500 20
Empty Drum Storage Area #551 1200 50 1200 25 rt :1.
Old Minuteman Missile Area fM-l6A 400 50 400 25 rl.*
rs areas
TABLE 3: SIJMMARY OF RETARDATION COEFTICIENT CALCI.JLATIONS
Compound Name Trichloroethene 1, 1, l-Trichloroethane Acetone
log K*l.8l to 2.10 2.U2 to2.l8 -0.43
f* (% by weight)0.04 to 0.09 0.04 to 0.09 0.04 to 0.09
IQ (cm3/gm)0.026 to 0.1I 0.O4 to 0.14 0.00015 to 0.00033
Butk Density (gm/cm3)
Limestone
Gravel
2.69
1.80
2.69
1.80
2.69
1.80
Retardation Coeff.
Limestone
Gravel
1.3 to 2.5
1.2 ro 2.0
1.4 to 2.9
1.5 to 2.3
I 0
0I
Model Values 1.9 1.9 1.0
TABLE 4: SIJMMARY OF SITE BOITNDARY CONDITIONS
Remedial Altemative
Well With Highest
Concentration
Highest
30-Year Exposune
Period
Maximum Predicted
TCE Concentration
(ppm)
Maximum Predicted
TCA Concentration
(ppm)
#l E-3 2021-2050 2296 1l0l
n B-6lB-7 t99t-2020 60 0
#3 E-4 2U2t-2050 2216 778
#4 B-6lE-7 t99t-2020 48 t2
Note: Data used for Risk Assessment
TABLE 5: SI.JMMARY OF BASELINB RISK ASSESSMENT
Remedial
Alternative
TCE/TCA Ingestion TCE/TCA Inhalation Total Exposure
Hazard
Quotient
Cancer
Risk
Hazard
Quotient
Cancer
Risk
Hazard
Quotient
Cancer
Risk
#t 8.5 7xlOra 10.9 lxlO3 t9.4 lxl0-t
n 0.1 9x106 0.2 2xl0-5 0.3 3xl0'5
#3 6.7 6xl0a 8.6 lxlO3 15.3 lxl0-3
#4 0.1 6xl0{0.1 lxl05 o.2 2xlOt
Note: Please refer to Appendix C for a complete description of the baseline Risk Assessment
,
,
FTGURES
GRID (columns)
7600
6800
5800
oo
-J8oo
! 2 I I 3 ! ' ! ! lO tt t2 t5 tt t! i! 17 t! ra 20 2l 222t2a ?nJzt 2, D 2e $ st !a llt !a !c !! !? J!!t ao at a2 {r
600 t600 2600 3600 4600 5600 6600 7600 8600 9600 10,600 1r,600 12,600't3,600 1a.600 15,600 16,600
DISTANCE (feet)
t
2
t
1
c
c
7A4aoocfef
ro{i
Ito
t2E
'ota
r!
tc
t7
tc
te
2800
r800
800
lrJ()z
Fao
0
\z ,)cRouND WATER EQUTPOTENIAL L|NE (ft)
1
MI ilt pr a (rc n€o LT rl'1,,S
I !!-I -I !r -
/I
/I
I t-
,,I I I I
'6t l
SIGr \\I 7 I I I \\
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1q-/,/\/I 7t/\-/a /
I \I //\
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It )I \\
0t \\\r-
a.(t D ()
I &I ],
III
MODFLOW
ESNMATED PIEZOMETRIC. HEAD DISTRIBUTION(Bosed on meosured Ei,' extropoloted doto)
Thiokol M-136 Modeling Study
ChenQNorthern,Ine.
Drown DMZ 6Dotc I{ Nerth
Revlsed 9 1 Job No.5-179-9 Figure /
l2 J a l l7l I lO tt t2 tl t,a !5 la t7 t! lt ,O I A D Za 6 A Z, D 2t D llt lP !l ta !g !Ct, ! lr rto at at! rtit
GRID (columns)
600 1600 2600 3600 4600 5600 6600 7600 8600 9600 10.600 1r.600 12,600 15,600 14,600 15,60016,600
DISTANCE (feet)
7600
6800
5800
?480ooo
-sBoohJoz< 2800FU'6 r800
800
I
2
t
4
t
c
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ffi $ ft/doy
tX 75 ft/doy
I roo ft/doy
ffi rzs ft/doy
/ zso n/doy
X x
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MODFLOW
Flnlte Dlfference Grld
Hydroullc Conductlvlty Dlstrlbutlon
Thiokol M-136 Modeling Study
ChenQNorthern,Ine.
Dotc I 1Drown DMZ Figure 3<+l€rth
Revised 9 4 1 Job No.5-179-
N 3 ft/doy
GRID (columns)
7600
l2 t 't 5 C 7 6 o lo tt t2 t3 t.r l5 tG t7 la 19 20 2t u2 2, 21 2a 2A 27 2C 2a !O 3i t2 3:' !a t6 !C t7 !t 59 ao n a2 a":,
600 1600 2600 5600 ,l5oo s600 6600 7600 8600 9600 10.600 11,600 12.600 13.600 t/t,000 .15,600 .16,600
DISTANCE (feet)
% []..:1hh"i[,noo,,y1
X Fixed Heod (Colculoted Heod) Cell
I
2
t
4
t
c
,
cQe!
to->
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ta
t!
tc
l7
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2800
1800
800
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MODFLOW
Flnlte Dlfference Grld
Boundory Condltlong
Thiokol M-l36 Modeling Study
ChenQNorthern,fne.
Drown DMZ<+[er+h
Revlsed 9/4/91 Job No.5-179-9 Figu re 4Dotc E
Active Cell
,,/ I
7406
6600
6A00
63/00
420/6^
3406
260/0
lAOO
1006
200
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lrJc)z
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E
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E
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DISTANCE (fcet)
GROUNDWATER EQUTPOTENIAL L|NE (FT.)
90
CDG'
MODFLOW
Slmulotcd Plczomctrlc
Hcod Dl*rlbutlon
Thlokol M-t 36 Modcllng Study
ChenONorthern,Ine,
Drown DMZ Dotc l0 3r+I€r+h
Rcvlccd 9 4 1 Figure 5
\
GRID (columns)
t t l a l a, ! t to ll !2 t! t4 !c l! t7 t! rt 20 zt ?z B za 2a a 27 n 2e !o !t lll !s !a J! !t 9, !! !a ao llt a2 /l!
64aoo
7600
6800
5800
800
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el
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t!,
rc
l,
tt
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600 1600 2600 5600 ,[phone] 8600 9600 10,600 11,600 12,600 15,600 t,t 600 15,600 16,600
DISTANCE (feet)
SAMPTES COLLECTED BY IHIOKOL PERSONNEL IN
No\EMBER/DECEMBER 1990 AND MARCH 1991
o E-I MONITORING II€LL LOCATION
(590) DISSoL\ED SOLUTE coNcENIRAIIoN (vg/T)
(BDL) BELOW DEIECTABLE LE\ELS
MI tlt pr t r(rc 1€o LI rh,)S
aI---,I a I a r
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I I'.rrt 79(D)-((
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Meosured Trlchloroethylene (TCE)
Concentrotlon Dlstrlbutlon (1991)
Thiokol M-136 Modeling Study
ChenQNorthern,Ine.
Dotc I 6Drown DMZ Figure 6<+[e+t+
Revlsed 9 1 Job No.5-179-
,oo ISOCONCENIRAION une (ugA)
GRID (columns)
7600
6800
5800
0
I t t a t a T l e rc t! !2 tt ta !3 tt t, tt It to a 22 Lt aa E D zr 6 2t J0 Jt !a !lJa5!a g7 !l !a tlo a! t2 (!
600 1600 2600 3600 4600 56q, 6600 7600 8600 9600 to,e00 11,600 12,600 11600 14,600 15,600 16,000
DISTANCE (feet)
S|MULATON CORRESPONDS TO NO\EMBER/DECEMBER
I99O AND MARCH 199I SAMPLE RESULE
t
2
t
1
t
t
,
t tn
5800
2E00
1800
800
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trJ()z
Ftno
cf,
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tlo
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'!otl
r5
tc
t
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460
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SOURCE AREA
DISSOL\ED SOLUIE coNcENTRAnON (rglu)
//1
\aI
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\r.I i \\
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Slmuloted Trlchloroethylene (TCE)
Concentrotlon Dlstrlbutlon
ln 1991
Thiokol M- 1 36 Modeling Study
ChenONorthern,Inc.
Drown DMZ FigJob No.5-179-9 7Dotc 8 1
Revlsed I /4/91
<+[erth
ISOCONCENIRAIION LINE (ugrlL)
\
I
GRID (columns)
7600
6800
5800
l2l4 3 a r l I lo ll 12 t3 !r 15 tt 17 r! 19 20 2t 22 tt 2a at 2a n n t !0!t 12 lit !a Jo Ja !t !t !0 ao 4t 42 ('
600 1600 2600 3600 4600 5600 6600 7600 8600 9600 10,600 t1,600 12,600 15,600 14,600 15,600 16,600
DISTANCE (feet)
SAMPLES COLLECIED BY IHIOKOL PERSONNEL
rN NO\EMBER/DECEMBER 1990 AND MARCH 1991
. C-T MONITORING WELL LOCATION
(460) DISSOLIED SOLUTE coNcENTRATIoN (ug/L)
(BDL) BELOW DETECTABLE LEVELS
-rrr{coNcENTRATroN
LINE (uelL)
I
2
J
1
c
t
7
cQet
roti
tto
t2G.
rsO
ta
It
It
l,
tt
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3800
800
0
800
800
2
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Meosured 1,1,1-Trlchloroethone (TCA)
Concentrotlon Dlstrlbutlon (1991)
Thiokol M- 1 36 Modeling Study
ChenQNorthern,Ine.
Drown DMZ Dote 8/26/91 Figure I<+[erth
Revised 9 /4/91 Job No.5-179-91
\
GRID (columns)
l2 t 't 5 t 7 E 9 lO lt t2 13 tl t5 lC t7 lE tg 20 21 22 23 21 25 2C 2t 2C 29 tO Sl !2 31, tt 33 SC t7 tt J9 40 4t 42 4J
5800
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t
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tc
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600 1600 2600 3600 4600 5600 6600 7600 8600 9600 10,600 11,600 12,600 15,600 t,t 600 15,6@ 16,600
DISTANCE (feet)
SIMULAIION CORRESPONDS TO NO\EMBER,/DECEMBER I99O
AND MARCH 1991 SAMPLE RESULTS
\ 460 DISSoL\ED SoLUIE CONCENTRATIoN (ugA)
\ IOO-lg.ocoNcENTRAnoN LINE (uglL)
\'(rl3 o,t\
)\
I 23 -2 r49 )t4t \\\/./ot-r\lOr /2C \//rot \'/,
I /.F u(\\
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RANDSD
foted 1,1,1 -TrlchloroethoneConcentrotlon Dlstrlbutlon (
Thiokol M- 1 36 Modeling Study
1991 )
ChenCNorthern,Ine.
Drown DMZ Dotc I 6{ Nerth
Revlsed 9 1 Job No.5-t79-Fig I
)F SOURCE AREA
GRID (columns)
t 2l a ! t ? t r ro ll 12 rI ll tt l7 !! !t,o 2l 2.2s2a6 D ill !0 !t la 3t !a t3 ta Jr:t4 3, rto {r at t3
7600
6800
5800
rE00
t
z
t
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c
t
7
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oo
UJoz
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tc
l7
rt
te
800
0
600 1600 2600 3600 4600 5600 6600 7600 E000 9600 10,6@ 11,600 12,600 15,60014,600 15,60016,600
DISTANCE (feet)
SAMPLES COLLECTED BY THIOKOL PERSONNEL
IN MAY, 1990
O C-l MONITORING WELL LOCATION
(460) DISSoI-\ED SoLUTE coNcENIRATtoN ("g/L)
(BDL) BELOW DETECTABLE LE\ELS
4 EocoNcENTRATIoN LINE (ugA)
\\
MI ilt Pr a -c,rc 'l€o LI r[l )c!
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Concentrotlon Dletrlbutlon (1991)
Thiokol M- 1 36 Modeling Study
Meosured Acetonc
ChenCNorthern Ine.
Drown DMZ Dotc I 1 Figurel 0<+Ier+h
Rcvlscd 9 1 Job No.5-179-
It
GRID (columns)
I 2 ! a l a 7l O to li tl l! 14 19 t! t7 l! ll 20 n ',22t2aA,l,,,!, !O !l !a!!!{lCM!aX/loill a2 a:l
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ttJoz tlo
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rro
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rt
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rt
ro
i-ao 1800
800
o
600 1600 2600 5600 4600 5600 6600 7600 8600 9600 10,600 t1,600 12,600 13,600 14,60015,600 10,600
DISTANCE (feet)
Simulotion corresponds to Moy 1990 somple results
---1 lsoconcentrotion Line (ug/L)
236 Dissolved Solute Concnetrote (ug/L)o
l-\
- lt/t1l \
lzl//a 7 \\\
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RANDSD
Slmuloted Acetone
Concentrotlon Dtetrtbutlon (1991)
Thiokol M-136 Modeling Study
ChenCNorthern,Ine.
Drown DMZ Dote I 1
Revlsed 9 1 Job No.5-179-Fig 11€ Nerth
4
TIIIIT IIIIIIITIIIIIrIrIIIIIIIIIIIIIIITIIIIIIIIII ITII
II II
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II IIIIITI
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* Source Areo
\
7600
6800
5800
GRID (columns)
l2 t a 3 t, ! t to lt !2 l! la rt rt t7 tl tr 20 2l u zt 21 zaz,2t 82! !o lt lit !i, l. r0!. Jt !t !t lo tt a2 rlt
600 1600 2600 3600 4600 5600 6600 7600 8600 9600 10,600 11,600'12,600 13,600 t4,60015,600 16,600
DISTANCE (feet)
A RECOVERY WELL LOCANON
t
2
t
I
5
c
,
5800
2800
1800
800
+tq)o
LrJ()z
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Recovery Well Locotlonsfor Remedlol Alternotlve #2
Thiokol M-136 Modeling Study
ChenQNorthern,fne.
Drown DMZ Dote 10 3<-Dter+h
Revlsed 9 4 I Job No.5-179-9 Figu re12
7400
66a/0
SAOO
E,o,e,a
42a/0
340/0
260/0
lAOO
1?/0/0
2e/0
+aoor|-
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l-a6
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DISTANOE (fcct)
\ GROUNDWATER EQUTPOTENTTAL L|NE (FT.)
$
9g t
},ODFLOW
Slmulotcd Plczomctrlc
Hcod Dlrtrlbutlonfor Rcmcdlol Altcrnotlvc #2
Thlokol M-l36 Modcllng Study
ChenONorthern,Ine.
Dronn D zr+I€'r+,h
Fig 13E@@M
/1
GRID (columns)
7600
6800
5800
-JEoo
C4Eoo
I I J a 5 3 7 ! 9 rO rt 12 15 ta t6 t! t7 r! tt 20 zl zr 2taa,ltalt D 2t ! !t !t !1, !a !lt J, !a !t ao 4t tt €
600 1600 2600 3600 ,t6oo 5600 5600 7600 8600 9600 10,600 11,600 12,60013,600 l/+,600 t5,6O0 16,600
DISTANCE (feet)
A RECO\ERY WELL LOCATION
t
2
t
1
I
t
7
coo
td()z
F
@o
ute!
rotz
2800
1800
800
llo
t2:E
trO
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l3
tt
t7
It
rc0
A R\A RI l_c
I Rt
Recovery Well Locotlongfor Remedlol Alternotlve #3
Thiokol M-136 Modeling Study
ChenONorthern,Ine.
DMZ Dotc 10 1<+[erth
9 1 Job No.5-179-Fig 14
+aoo
lrJC'z
Fa
cr
7400
6600
SAOO
EOOO
420/0
340/6^
260/0
lAOO
100/0
2o,0 RE$EH$R$Fg&$$EE
DISTANCt (feet)
\ GRoUNDWATER EQUtpoTENnAL LINE (FT.)
$
6
Dl
MODFLOW
Slmulotcd Plczomctrlc
Hcod Dlrtrlbutlonfor Rcmcdlol Altornotlvc ilJ
Thlokol M-l36 Modcllng Study
ChenONorthern,Ine.
Drown DMZ<-Dterth
Rcvlccd 9 4 1 Job No.5-179-9 Fig 15looic r6lJlgt I
+,oor|-
lrJ
C)z
Fa
cr
7400
660A
SBOO
E,o,o/o
42o,0
3400
26e/0
leoo
10a,0
200 $!$BB$R$F$Ng$fip
DISTANGE (fect)
\ GRoUNDWATER EQUTPoTENIAL UNE (Fr.)
C'-r---
?o
I
1(){,
o
o
MODFLOW
Slmulotcd Plczometrlc
Hcod DhtrlbutlonAltcrnotlvc 14
Thlokol M-l30 Modcllng Study
ChenCNorthern,Ine.
Drorn DMZ Dotc 10<+ter+h I 4 ,lob No.5-179-9 Fig 16
)
Recovery Well Locotlonsfor Remediol Alternotlve #5
Thiokol M-136 Modeling Study
ChenCNorthern,Inc.
Dote 1O/3/91Drown DMZ
Job No.5-179-9'l Fig 17<-$t-erth
Rcvlscd 6 /9 /92
GRID (columns)
t 2 !,t 5 a 7 a l lotl 12 l!tal!t!t7 l!te20nntt2aUAZTZl Zt !O lt l? lil !l l5 lta J, !l !..lo /n /t2 all
7600
6800
I
2
J
a
t
c
7
5800
?4aooool{.
-JBootdOz< 2800Flno1800
cfe!
ro5
It
t2
ll
t4
lc
tt
l7
tt
t,
o
v.(,
800
0
600 ,t600 2600 35oo 4600 5600 6600 7600 8600 9600 10,600 11,600 12,600 1J,600 14,600 15,60016,600
DISTANCE (feet)
r-I A EXISTING WELL LOCATION
:-l A

E .J A
6E-t A E -2 A A B-
MODFLOW
Slmuloted Plezometric
Heod Dlstrlbutionfor Remedlol Alternotlve #5
Thiokol M-1JO Modeling Study
ChenCNorthern,In c,
DMZ Dotc 10 1<rN€'r+h
Revlsed 6 2 Job No.5-179-91 Fis 18
6600.oo
[e-mail]
o)oq-
bJL)z
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340/0.oo
lgoo.oo
20/0/oo
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E
E
d
$
E
B
E
$
E
B
E
n
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Elr
=
E E
$t
E
$
DISTANCE (feet)
GRoUNDWATER EeurporENTrAL L|NE (FT.)
E-4.
-3o
&ot
E
B
.B-6
E-l O EXISNNG WELL (NTCOVTNY WELL) LOCATION
GRID (columns)
7600
6800
5800
t 2l a 3 ! 7 ! e !On lz t! la tc t! !? r! tl 20,I-z2,ttaa,!?lzr,! 2t D !t lE x, !.!r s! !7 !! !l. ao at rl2 ru
600 1600 2600 5600 /1600 5600 6600 7600 8800 9600 10,600 11,600 12,600 13,600 14,60015,60016,600
DISTANCE (feet)
100 .-- ISOCONCENTRAIION LINE (ugrll)
zro o DISSOLVED SOLUTE CONCENTRATION (ue/)
I
2
5
4
I
t
7
!
5600
2E00
1800
800
oo
trJ
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F(n6
U'el
to->
tlo
t2:tr
rsO
t'l
t5
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t7
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I/
\h o4lr,I l-21
\i
c =\.1
=t
./I \\tt0 !t \\+t /I ,1 r l
-t o^\OC \\/a /-^/I
\'t az'o1 j2 zr!ol ll t2ll t\a 7'\o 0 (a a \/o!,40 o //2I\ll I\\\\\\\\/a
\9l a -l \\4t4 \a \\1 t!\2 7C /t 7l t
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/\\\\)F'
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\\I -
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RANDSD
Slmulotcd TCE Concentrotlon
Dlgtrlbutlon for
Remedlol AitCrnotPe jt (zozt)
Thiokol M-136 Modeling Study
ChenONorthern,Ine.
Drown DMZ Fie 19i Nerth
Job No.5-,l79-9Wffi
GRID (columns)
I 2l a 5 C ' ! t lorl12rlra19rctTr!t3202t2a2;tztut?ozt?' 20 !o !t !2 It llt tc !a r, !! Jt ao tt a2 /Nt
7600
6800
5800
t
2
t
a
5
c
7
oo
td()z
FIo
?48o0
800
o
cfe!
toli
1
llo
I?E
rrO
la
t5
rc
t7
It
ro
800
600 1600 2600 3600 4600 5600 6600 7600 8600 9600 10,600 11,60012,600 1r,600 14,600 15,600 t6,600
DISTANCE (feet)
100 .-- tsocoNcENTRAnoN LINE (ugrlt)
579 o DISSOL\ED SOLUTE coNcENTRATIoN (ug/I)
;11 rO
/\
\I a \\o 't \/'/O
q(.|<,to \7
\tlG rl t 173 tt c7,
Itt!,4 l!rt ,,\2l /t o /t )c 0 159
\-\7 /,0c )r {J
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t,J9:\t )71 7{l /
:\\\At $
o\a\a \o .a a a \
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\54r ,71 /2 ,/7
U!///
/
RANDSD
Slmuloted TCE Concentrotlon
Dlstrlbutlon for
Remedlol Alternotlve #1 (2051)
Thiokol M-136 Modeling Study
ChenQNorthern,Ine.
Drown DMZ Dotc I O<+Ier+h
Revlsed 9 4 1 Job No.5-179-Fig 20
GRID (columns)
7600
6800
5800
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600 '1600 2600 3600 4600 5600 6600 7600 8600 9600 10,600 11,600 12,600 t3,600 14,600 15,600 t6,600
DISTANCE (feet)
tOo.-= lsocoNcENTRAnoN L|NE (ugl)
ZIO o DISSOL\ED SOLUIE CONCENTRATION (ue/I)
t
2
t
I
3
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7
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llo
t2E
,9
t4
t5
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t7
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2800
1800
800
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-/./\
I I
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\
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I
RANDSD
Slmuloted TCA Concentrotlon
Dlstrlbutlon for
Remedlol Alternotlvc #1 (2021)
Thiokol M- 1 36 Modeling Study
ChenONorthern,Ine.
Drown DMZ Dots 1O I<+[erth
o 4 Job No.5-179-9 21Fig
GRID (columns)
7600
6800
5800
?4800o
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-JBoo
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600 1600 2600 3600 /t600 5600 6600 7600 E600 9600 10,600 11,600 12,60013,600 I /1,600 15,600 16.600
DISTANCE (feet)
lo0 .-- lsocoNcENTRATloN uHe (ugrlt)
ZIO o DISSoL\ED SoLU]E coNcENTRAnoN ("g/I)
OIT PARTICLE ACCUMULANON AT MODEL BOUNDARY
NOT REPRESENTATI\E CONCENTRATION
t
2
t
4
3
t
7
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rc->
tlo
t2E
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t{
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2800
1800
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RANDSD
Slmuloted TCA Concentrotlon
Dlstrlbutlon for
Remedlo[ Aiternotke ll1 (2051)
Thiokol M- 1 36 Modeling Study
ChenONorthern,fne.
Drown DMZ Dotc 10/3/91 Fig 22Revlsed 9/4/91 Job No.5-179-91
+Ner+h
GRID (columns)
I I I t l a r l I lo !l t2 rl r't t!, r! 17 ta tt 20 a n 2t 21 ,!2an?, ,lt to !r t2 f, !a Jt Jt II, lt !t ao a! az rNt
I
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t
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5
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7afcl
tolz
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t2E
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t{
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1800
800
7600
5800
o
600 t600 2600 3600 4600 5600 6600 7600 8600 9600 10,600 11,600 12,600 15,600 14,600 15,600 16,600
DISTANCE (feet)
A RECO\ERY WELL LOCATION
IOO _- ISoCoNCENTRATIoN LINE (ug,ZI)
ZIO o DISSoL\ED SoLUTE coNCENTRATIoN (ug/I)
/v 30(t o \(a +l
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IIIIIIITIIII II
III
I
RANDSD
Slmuloted TCE Concentrotlon
Dlstrlbutlon for
Remedlol Atternotlve tZ (ZOZI)
Thiokol M-136 Modeling Study
ChenQNorthern,fne.
Drown DMZ Dote 10/3/91
Revlsed I /4/91 Job No.5-179-91 Fis 23^r I\T^-ll---={ .l'.Ll
\
GRID (columns)
7600
6800
5800
Q)
-JBoo
6:4aooq)
t 2 t a 9 c 7 ! ! to ll t2 tl tt !c !t t7 t! !r 20 /t 22 rt 2a ra 2a rr 2a zt J, !r J2 Jg !l 3!] !a J, ra !c ao ar a2 a:r
600 1600 2600 3600 4600 5600 6600 7600 8600 9600 10,600 11,600 t2,6001J,600l,t 600 1t,60016,600
DISTANCE (feet)
A RECO\ERY WELL LOCANON
100 -- tsocoNcENTRATtoN L|NE (u9/)
59I O PI$$OL\ED SOLUTE CONCENTRATION (,g/)
I
2
5
.l
3
c
7
t
I
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=oto:>
2
UJ()Z
t-go
800
800
Ito
t2E,o
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t7
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1
800
o
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II
RANDsD
Slmuloted TCE Concentrotlon
Dlstrlbutlon for
Remedlo[ A]ternotlve ll2 (2051)
Thiokol M- 1 36 Modeling Study
ChenCNorthern,fne.
Drown DM Dotc 1O 1
1 Job No.5-179-Fig 24{ Nerth
Revlsed 9
\
GRID (columns)
7600
6800
5800
0)q)
-JBoo
6:48oo
t 2 J a l l7l e lo !l tz tl tl !5 !! t7 !! t! 10 2t,:2:tz1 EfrzrD it !o !! t2 5! 9] !a tl. y, ! !c rto at ru2 a!
600 1600 2600 3600 ,1600 5600 6600 7600 8600 9600 10,600 t1,6OO 12,600 15,600 t+6O0 15,600 16,600
DISTANCE (feet)
A RECO\ERY WELL LOCANON
100 --- ISOCONCENTRATION LINE (ugrll)
IS . DISSoL\ED SoLUTE coNCENTRAIIoN (ug/I)
I
2
t
a
t
c
,cf
o3-oroti
tto
ve.
tsO
t4
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tc
17
It
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1800
800
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IIIIIIII
IIIII
I
II
rI!tsIIIT
I
II rI
IIIIIIIIIIIIIIIIIIII
RANDSD
Slmuloted TCA Concentrotlon
Dlstrlbutlon for
Remedlol Alternotlro #2 (2021)
Thiokol M- 1 36 Modeling Study
ChenONorthern,Ine.
Drown DMZ Dotc 1O 1
Rcvlsed 9 1 Job No.5-179-Fig 25--N€tr+h
\
GRID (columns)
| 2 9 4 5 C 7 C 9 t0ll12151415lc17tt19202l222321232C212C2t' tO5tt2ltt4to5ct75!59aOat 42 .tS
C48oo
7600
6800
5600
-JBoo
800
t
2
t
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c
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cQe!
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'ot4
t3
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t,
tt
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8001
o
600 1600 2600 3600 /1600 5600 6600 7600 8600 9600 10,600 11,600 12,600 13,600 14,600 t5,600 t6,600
DISTANCE (feet)
A RECO\ERY WELL LOCANON
t00 -.-- TSOCONCENTRATTON L|NE (ugl)
c04 o DISSoLVED soLUTE coNcENTRATtoN ("g/t)
/\
I 5 \
/\
,a 1r :.o !72 /a 10 ,tl \
I It \\
3:l I 9(,,9t \/lt]27 \\r to o c \
\a\aail \\\\IItt17,/o ,96 \a ,c .l{E a itt6 \'17 I o lt
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\It tg ,/7 /
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I
RANDSD
Slmuloted TCA Concentrotlon
Dlstrlbutlon for
Remedlol Alternotlve #2 (2051)
Thiokol M-136 Modeling Study
ChenONorthern,Ine.
Drown DM Dote 1O I<+[erth
Revlsed 9 I Job No.5-179-Fig 26
o/o25
SOYo
5o/o
Oo/o
TCE
TCA
2Oo/o
o/o15
Oo/o
H
o
frltr
EU
L{
Hq
Nq
1
1990 2000 2010 2020 2030
YXAR
2040 2050 2060
RANDsD
Cumulotlve Percent Totol Removolof TCEr/TCA
Remedlol Alternotlve #2
Thiokol M- 1 36 Modeling Study
ChenQNorthern,f ne.
Drown DMZ Dote 10/3/91
Revrsed 9/4/91 Job No. 5-179-91 Fis 27
100
EtrA
zoH
E{
MHz
T{UzoU
F]Utfrl
1 200
800
600
400
200
TCE
TCA
2000 2010 2020 2030
\TAR
2040 2050 2060
RANDsD
TCEr/TCA Concentrotlons lnRecovery Well Dlschoroe
Remedltil AltemoUve #Z
Thiokol M- 1 36 Modeling Study
ChenONorthern,Ine.
Drown DMZ Dote 10/3/91
Revlsed 9/4/91 Job No.5-179-91 28Fig
GRID (columns)
| 2 J a 5 t 7 ! I tO !t t2 tJ ta ,t5 t! t7 t! !t 20 d 2 a 21 a u n L , $ st !c t! l{ s x J7 ! t .o a! a2 rN
I
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128
'oI't
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t,
tt
t9
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FIo
7600
6800
5800
800
o
600 1600 2600 3600 4600 5600 6600 7600 8600 9600 10.600 11,600 12,600 13,600 14,600 15,600 16,600
DISTANCE (feet)
A RECO\ERY WELL LOCATION
l0o -- tsocoNcENTRAnoN LINE (ugrlt)
2TO o DISSoL\ED SoLUIE coNcENTRATIoN (ugl)
/'to ,r
a
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ta \
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7.J\a ,o o o ara a
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I IIIIII rIIIIT IIIIIIrrr
I
II rITIIIIIII
IIIIIIIIIIII III
RANDSD
Slmuloted TCE Concentrotlon
Dlgtrlbutlon for
Remedlol Alternottw #f (2021)
Thiokol M-136 Modeling Study
ChenONorthern,Ine.
Drown DMZ 1Dotc 10 Fig 29I Nerth
Rcvlsed 9 4 I Job No.5-179-
\
cRlD (cotumns)
I I J a t a r l t to tt 12 rt tt ,tt t! t7 t! tt 20 a 2 t 2a,!t,.nL $ lt lt !i, !l. *, x J7 5 9l .o {t az aS
I
2
t
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3
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7
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lo->-JBooLrJ()z< 2800
9,o
1800
800
llo
t2E
rsO
ta
tt
tc
t7
It
teo
600 t60O 2600 3600 4600 5600 6600 7600 8600 9600 10,600 11,600 12,600 15,600 l,t,60o 15,600 16,600
DISTANCE (feet)
A RECOVERY WELL LOCANON
100 -- TSOCONCENTRAIION L|NE (ugl)
2IO o DISSoL\ED SoLUTE coNcENTRATIoN (ug/I)
./I
/!\
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\a
2
l.
. RANDSD
Slmuloted TCE Concentrotlon
Dlstrlbutlon for
Remedlol Altarnottve frI (2051)
Thiokol M- 1 36 Modeling Study
ChenONorthern,Ine.
Drown DMZ Dotc 1O 1 Fig 30<-Nerth
9 4 I Job No.5-179-
\
GRID (columns)
7600
6800
5800
-JBoo
l2 t a t ! 7l t to lt t2 lJ ll t3 tc t7 t! t, 20 z'l 2z2t2a2a2an a 2t !o Jt lta !i, $ Jtt J! J7 !! !t, {O a! t2 .lt
600 t6oo 2600 3600 4600 5600 6600 7600 8600 9600 .10,600 11,600 12,60015,60014,600 | 5,600 t6,600
DISTANCE (feet)
A RECOVERY WELL LOCATION
100 -- TSOCONCENTRAflON L|NE (u97zt)
ISS o pI$$oL\ED SoLUTE coNcENTRATIoN (ug/I)
I
2
5
1
t
t
,af
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rc5
llo
t2E
,9
t4
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rt
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to
800
800
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RANDsD
Slmuloted TCA Concentrotlon
Dlstrlbutlon for
Remedlol Alternotlve #3 (2021)
Thiokol M-136 Modeling Study
ChenCNorthern,fne.
Drown DMZ Dote 10 I<+[er+,h
Revlsed 9 4 I Job No.5-179-Fig 31
\
cRlD (columns)
! I J 4 5 C 7 ! I lO ll t2 tJ la t!, l! 17 ta t9 20 A2!l 2t 21 AfrZr Zt !O lt la !1, lrt $l !! l? S r aO t! all att
7600
6800
5800
t
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7
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-JBooUJoz< 2800F(n6 1800
800
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,9
ta
t3
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t,
ta
teo
600 1600 2600 5600 4600 5600 6600 7600 8600 9600 10,600 11,600 12,60015,600 14,60015,600 16,600
DISTANCE (feet)
A RECOVERY WELL LOCATION
loo .-- ISOCONCENTRAilON LINE (ugrzl)
ZTO o DISSoL\ED SoLUIE cONcENTRATIoN (ug/I)
PARTICLE ACCUMULATION AT MODEL BOUNDARY
NOT REPRESENTAN\E CONCENTRATION
5 1
\\
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^Q /a
\\26 48 il It \6t tt |27 /1,8o -2
)-//rt/\7li //
\\/
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RANDSD
Slmuloted TCA Concentrotlon
Dlstrlbutlon for
Remedlol Alternotlve #3 (2051)
Thiokol M- 1 36 Modeling Study
ChenCNorthern,Ine.
3Drown DMZ Dotc 10
Revlsed 9 4 I Job No.5-179-Fig 32{ Nerth
\
55.
4Ooto
35o/o
3
25
2O"/o
1
Oa/o
o/o
o/o15
Oo/o
Fl
so
H
EO
Etr
NE
5o/o
Oo/o1990 2000 2010 2020 2030
YXAR
2040 2050 2060
TCE
TCA
RANDSD
Cumulotlve Percent Totol Removolof TcE/TcA
Remedlol Alternotlve #I
Thiokol M- 1 36 Modeling Study
ChenONorthern,Inc.
wn DMZ Dote 1O I
Revlscd 9 4 1 Job No. 5-179-9 Fis 33
RANDSD
TCEr/TCA Concentrotlons ln
Recovery Well Dlschoroe
Remeddl Alternotlve #J
Thiokol M-136 Modeling Study
ChenQNorthern,Ine.
Drown DMZ Dote 10/S/gt
Revtsed 9/4/91
tr
P{A
zo
H
fr
F{z
E]UzoU
F]Ut
r4
1 400
1 200
1 000
800
600
400
TCE
TCA
2001990 2000 2010 2020 2030
YTAR
2040 2050 2060
Job No.5-179-91 Fig 34
GRID (columns)
t 2 t 4 S l r l o ro tl r2 tJ ta tt t! t7 l! rt 20 2t 22 2:t 2a *t za zr 6 2t !o 9! !2 rit !{ }, !c J, !! ltt ao a!,t2 rN
7600
6800
5800
I
2
t
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5
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tlo
E()
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bJ()z
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2800
1800
800
t2
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600 i600 2600 3600 4600 5600 6600 7600 8600 9600 10,600 11,600 12,6001J,600 t4,600 t5,600 t6,6oo
DISTANCE (feet)
A RECOVERY WELL LOCATION
,lsocoNcENTRAroN LINE (ug/t)
I /r
ln.
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RANDSD
Slmuloted TCE ConcentrotlonDlstributlon for
Remedlol Alternotlve #4 (2021)
Thiokol M-136 Modeling Study
ChenQNorthern,Inc.
Drown DM Dote 1O I<+[or+h
Revlsed 9 4 1 Job No.5-179-9 Fig 35
289 o DISSOL\ED SOLUTE CONCENTRATION (us/t)
GRID (columns)
7600
6800
5800
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600 1600 2600 5600 4600 5500 6600 7600 8600 9600 10,600 11,600 12,600 1 3,600 t 4,600 1 5.600 '16,600
DISTANCE (feet)
A RECO\ERY V'/ELL LOCATION
rlsocoNcENTRAroN LINE (ugl)
327 c DISSOLVED SOLUTE CONCENTRATIoN (rgl)
t
2
s
1
c
c
7cfel
ro5
llo
ne.t.o
ta
tg
tc
l7
r8
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2800
1800
800
L.J
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t-Io
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\I 2 .|6 \a 22 \\
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RANDSD
Slmuloted TCE Concentrotlon
Dlstrlbutlon for
Remedlol Aiternotiw #4 (2051)
Thiokol M-136 Modeling Study
ChenQNorthern,Inc.
Dote 10/3/91Drown DMZ rie 36<JIe+th
Revrsed 9/4/91 Job No.5-179-91
GRID (columns)
I 2l a t a 7 ! e torl t2 rJ ta ll ll l, ll tl 20 at 2.2t2a?5?' 27 21 2t !o !t *! l3 Ja !qs 57 J!l. llo al a2 alt
7600
6800
5800
-J8oo
t
2
I
4
5
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lo->
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"Ot4
r5
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2800
1800
800
Q)
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trJ()z
ao
o
600 1600 2600 3600 it5o0 5600 6600 7600 8600 9600 10.600 11,600 t2.6OO 15,600 l,t 600 t5,6oo 16,600
DISTANOE (feet)
A RECO\ERY WELL LOCATION
/ \socoNcENTRATroN LINE ("e/t)
/5 \
/)
I r 5r a 3
/,o 16
1 a \155,\5 \/\
oa,\)l \/j7 \\
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t6 5 7l \IJ \u .16 I \
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rIIIr.
RANDSD
Slmuloted TCA ConcentrotlonDlstrlbutlon for
Remediol Altemotive #4 (2021)
Thiokol M-136 Modeling Study
ChenQNorthern,Inc.
Drown DMZ Dotc 1O 1-+l€++h Revised 9 1 Job No.5-179-9 ris 37
2E9 o DISSOL\ED SOLUTE CONCENTRATION (ugl)
GRID (columns)
7600
6800
5800
6{8ooq)
Q)
-J8oo
r 2 J a s c, ! ! ror rz rJ ra rs tl t7 r! le 20 21 22212a6anB 2e to !t !a lll!a tc !a t7 !! x:lo {r aa alt
600 1600 2600 3600 4500 5600 6600 7600 8600 9600 10,600 11,600 12,600 t5,6O0 l,t.60o 15,600 15,600
DISTANCE (feet)
A RECO\ERY WELL LOCATION
I
2
t
rl
3
c
7
E aef,
!0.->
tlo
ne.
tso
t4
t3
rc
t
tt
te
2800
1800
800
UJOz
FIo
o
,\socoNcENTRATtoN L|NE (us/t)
a/5 t,
/
\l1 a ,) 1l a \\ZZ \
/l63i '/(n (+)\
5 to -a-
06
,10r )-\\\/\
\c 90 A r65 \o \I io t6 I a \\
^/\\EOI I
\2t 2'\O.l t:I Itt tl 70t /
I ,ts
I uo I\
\5 a t a /(tt o /r/I
\/
\6 t2 4t
^..//
III
ITIIIII
RANDSD
Slmuloted TCA ConcentrotlonDlstrlbutlon for
Remedlot Alternotive #4 (2051)
Thiokol M-136 Modeling Study
ChenQNorthern,Ine.
Dote 10/3/91Drown DMZ ris 38<+l€r+h
Revised 9/4/91 Job No.5-179-91
289 o DISSOLVED SOLUTE CONCENTRATION (rgl)
600/o
5Oo/o
4Oo/o
3Oo/o
TCE
TCA
Fl
t'o
trlfr
frl
F.lUH
F-rtr
A
NR
2Oo/o
1Oo/"
Oo/o1990 2000 2010 2020 2030
YTAR
zop}O 2050 2060
RANDSD
Cumulotlve Percent Totol Removolof ToEr/TCA
Remedlol Altdrnotlve #4
Thiokol M-136 Modeling Study
ChenQNorthern,Inc.
Drown DMZ Dotc 10 3
1Revised 9 4 Job No. 5-179-Fis 39
RANDSD
TCE Concentrotlons ln
Recovery Well Dlschoroe
Remedidl Alternoilve l+
Thiokol M- 136 Modeling Study
ChenQNorthern,Ine.
Drown DMZ Dotc l0 3 1
tr
P.tr
zo
H
g
HzrlUzoO
F1U
E{
F]U
tr
H
1 400
200
000
800
1 SOUTH END RW'S
NORTH END RW'S1
600
400
200
2000 2010 2020 2030 2040 2050 2060
YXAR
Revlsed 9 4 1 Job No.5-179-9 Fis 40
RANDsD
TCA Concentrotlons ln
Recovery Well Dlschoroe
Remedldt Atternoilve I+
Thiokol M- 1 36 Modeling Study
ChenCNorthern ,fne.
Drown DMZ Dote 10/3/gt
E
F.
P{
zo
F{
frHz
t=]UzoU
U
E{
E]U
tr
B
900
800
700
600
500
SOUTH END RW'S
NORTH END RW'S
400
300
200
100
1990 2000 2010 2020 2030 2040 2050 2060
YEAR
Revrsed 9/4/et Job No.5-179-91 ris 41
GRID (columns)
7600
6800
5800
-JEooIJ
C)z< 2800Ftn
cf 1800
t , r a l l 7l 9 ro r! 12 rJ ta tll rt 17 r! !l io a a a 2a 4 u t a t!0 ll5i !i, ta !5 lI r, !a !c 40 /n uu.*t
600 1600 2600 5600 4600 5600 6600 7600 86fi' 9600 10,600 11,600 12,600 1J,6O014600 15,600 16,600
DISTANCE (feet)
I
2
!
I
t
t
7
t6:4aoo aooq-ef
rc-y
tto
t2E
rso
t{
tc
It
l7
It
t,
800
o
\ E-t A EXISTING WELL (RECOVERY WELL) LOCATTON
\,oo
- rsocoNCENTRATroN LINE (ug/t)
958 O DISSOLVED SOLUIE CONCENTRATION (ug/I)
I
a.I //o \a \
ao t\,,t
\ou)\
t6i \78 t8 t9r 5 12 lo'\t1 l2 l2 24\I 201/
\,o E o I
\-o-t o I 7 t \/a o\/\
I\I lO-\\\\/
\\\t/I
i72lo-\10 I 991 \I j2 J2 55 \E0t E ltl 29 t7)-T /
)\\.10 I
a a\,/,/\\a !/\A
E-3U.o t \I
lt r9 l5 -1 tt I
I
RANDSD
Slmuloted TCE Concentrotion
Dlstrlbutlon for
Remedlol Alternotive #5 (2021)
Thiokol M-136 Modeling Study
ChenQNorthern,Ine.
Drourn DMZ Dote 'lO/3/91<+terth
Rcvrscd 6 /1O /92 Job No.5-179-91 Fig 42
RANDSD
Slmuloted TCE Concentrotion
Distrlbutlon for
Remedioi att*notlve #5 (2051)
Thiokol M-136 Modeling Study
ChenCNorthern,Inc.
Drown DMZ Dote 1O/3/91 Fis 43<+Ierth
Rcvtecd 6 /10 /92 Job No.5-179-91
GRID (columns)
7600
6800
5800
?4eoooora-
-JBooIJ
C)z< 2800Ftno
1800
800
r 2 ! | l a T l r ro l! 12 rl l,l rl ra r7 rr t' 20 a x, 2, 2a a 4 g 2a ltI0)rvt!t !a !!, !l 17 !! ta zx, /tl ae {t
5OO 1600 2600 3600 4600 5600 6600 7600 E6OO 9600 10,600 11,600 12,6001J,600 14600 .l5,600',16.60o
DISTANCE (feet)
I
2
5
,f
5
c
I
t aeI
lo{i
llo
t2E.
tso
tl
tt
tc
l7
tt
ID
o
. E-l A EXTSTNG WELL (RECOVERY WELL) LOCA'nON
\ 1oo --rsocoNcENTRATroN LrNE (ugl)
938 O DISSOLVED SOLUTE CONCENTRATION ("9/I)
I
-il4E I l2
I
///a 21 a \./
l I ln,\I
ll Tl \7:1 \
t\22 t/l7 f6 t3:5 I lEz t2 (llt 2l I
'aaI/'ai'al o t6t a \'t0 oI t I o \/I
t9!
nntIIt0t'/I )!r/7 /
2t \1 B7 ,/rtI\tll
20 \I 17 i8 1!I 4 ,0 t4 i8 I-t -1 7
\\d /
,10 .JUa /\a /\I to,tu 1^ta.//\
la oal
3:t 1 d7 r0B /
+z 0 35 EO
I
RANDsD
Slmuloted TCA Concentrotion
Dlstrlbutlon for
Remediol Alternotive #5 (2021)
Thiokol M-136 Modeling Study
ChenCNorthern,Ine,
Drovm DMZ Dotc 1O/3/91<-$Ier+J*
Rcvrscd 6/1O/92 Job No.5-179-91 Fig 44
cRlD (columns)
I 2 r a l t 7l I l0 i! 12 rtr ra 15 r! !, tl li 20 d z, E 2t 2, a n E 2! Jo !r !t lit Jt !! I rr !a tt zto at:u:1lr7600
6800
5800
oo
-JBoo
800
2800
l-lJ
C)z
F-ao
;:4aoo
00I1
o
t
2
t
t
t
t
7afe!
tolT
tto
ne.
|So
t4
tc
tt
l7
tt
t,
.. E-I A EXISTING WELL (NTCOIENY WELL) LOCAIION
\ 1oo --rsocoNcENrRAnoN LINE (uglr)
938 o DISSOLVED SOLUIE CONCENTRAIION (ug/.)
600 1600 2500 5600 ,t800 5600 6600 7800 86fi) 9600 10,600 11,600 la6OO lJ,6O0 14,800 15,600 16,600
DISTANCE (feet)
/t-
-ll n_
Eo!I /r t a
It a ,\
,ar \tr
R5tt€,7 t5t 3\lo \14r t 0aII \
o oOIo7 yr a \a /rl
,oo )\
\\98 -I ,oo /
:t6t\r'41 J a1 I 1 1\5 711 ,10r E :-1
\/
o o /\\t /\I /t0 /,/
2 00,
1t B
-t.
RANDSD
Slmuloted TCA Concentrotlon
Dlstrlbutlon for
Remediol Alternotive #5 (2051)
Thiokol M-136 Modeling Study
ChenCNorthern,Ine.
Drown DMZ Dotc 1O/3/91 Fig 45Rcvrscd 6 /1O/92 Job No.5-179-91
<+Ier+h
GRID (columns)
?4aoo
7600
6800
5800
0
! , l a l t r l I t0 tt It tl t/t t! ta t7 ta tt ,0 6 t 2rrart',ta,l rt lo ll 12 lit L lg !a s:t !a !a:o /tl ar.*t
600 l600 2600 3600 4600 5600 6600 7600 88OO 9600 l0,600 11,600 !2,600 15,6001't,600 t5,600 16,600
DISTANCE (feet)
I
2
S
a
t
t
7
t
e
o
=olo->
tto
t2E
rso
ra
lc
tt
oo
-JBooIJ(JZ< 2800t--tJ)o 1800
800
l7
tl
t9
\ E-r a ExtsnNc WELL (nucovunY WELL) LocATloN
\ roo.- rsocoNcENTRATroN LINE (uel)
938 ' DISSOLVED SOLUTE CONCENTRANON ("e/I)
/5
\tl1'1:orr a \I I \\\!
I ((\\I
I 25I3rJ6/6t 5 rB 54,1t 5 n I 2l l2 )B B 30 3
I \I
\l2i o O /I a a a \/\/\o
\I I\
.tl 00 ^l
I3,0 I ).31 ,J I t^r(
6AJU\\10..o,5 ,8 t9 l-/tE l 2 t9 E1 I I t 1E.{)Tt -1 I
I \//
a a /\a /\I 09r a a /
/.tut
10 I 15 -ll 0-5!'lzllr6
RANDSD
Cumulotive Percent Toto! Removolof TCEITCA
Remedlol Altbrnotlve #5
Thiokol M-136 Modeling Study
ChenCNorthern,Ine.
Drown DMZ Dola 10/3/91
Rcvreed 6 /12/92 Job No.5-179-91 Fig 46
7o/o
60/o TCE
TCAFl
t< 5o/oo
H 4o/o
frl
F.l
P 3o/,
EA 2o/o
Nq
1 o/o
Oo/o1990 2000 2010 2020 2030
YXAR
2040 2050 2060
TCE/TCA Concentrotions in
Recoverv Well Dlschoroe
Remedidt Atternotive #S
Thiokol M-136 Modeling Study
RANDSD
ChenCNorthern,Ine.
DMZ Dota 10 1
Rcvlsed 6 12 Fig 472Job No.5-17
5
tr
P.
F{
zo
E{
g,
Hz
F]UzoU
E]U
tr
B
4
3
3
2
TCE
TCA
1
1
50
2000 2010 2020 2030
YTAR
2040 2050 2060
APPENDICES
Appendix A
Listing of Projected TCE Concentrations for Monitor Wells B8,B6|E7, E3, and E4
_-6f6-'9t 1a:se rr-Pl!,lr anrcsria'
ggfOBOti tDEE[Gi - U-tr36 EURI GoUltDg
CEE[-IIORE@![ NO. 5-L79-9L
,...' 4.. _.,.a.\....P,3/5u
SCETIBIO 1rca - xo REGDIAISIOI
BAIIDODi IfAIA IilFOntEtEION FOR AqE (roB I,EB rnE &Itft ASSE SIEIIE)
lDis rIFGadsIBet tal@q tE6 output_tro! Ifal(lou nalts at lour specitLed
f.""d&a aaa giv€s tUe corresBondJ.uE coBceotpiirEloDs.
IEIED tlrll (60 lElRlt)
lets cmGllERilrroN (I,I,b)r4iL Ircemor
BB B-8 ET6/Z-7 E-3 H
1991I992
1993
L99r*rgis
1996
L997
Utr'8
1999
?ooo
eoo]'
2oi02
7e03
?;0,01
.3005
2006
?oa7
a008
?ooe
2010
20112otz
2013
20.Ll
201.5
2q16
20.L7
2018
20l,9
2020
202L
2022
20?3
202r
3025
L2t2
23.58
35
LL7
82
140
140
93
105
1t00
199
1{0
152
140
L75LAtjl7
ur2
117
L87t5u9
93
1J7
93
7:29
93
93
E2
105
105
82
93
35
59
tL8
16sut3
?23
353
3?6
4004r[
494
611
600
7t7
705
8XL
894
1035Ito5
IJ64
ul58
1329
1411
rir64
143a
1S7S
L527
L446
1481,376
L458
\470
ut99
L43t
1434
o
o
o
12L2
12ut
L22l
35
a7
83
xL8
L7A
?1s
?;37
?60
272za(
442
509
6r,!t
722
876
876
876
9941rt3
123:.
1278
1456ltio3
1645
1693
1615
0
o
0
0
0
o
o
0
o
o
o
o
0
o
o
o
0
0
o
o
o
o
0
0
0
0
0
o
0
0
0
o
0xt
IL
,aiirl.
t
ar
E[n.tbb:rbrb P.4/S,
?.026
2027
2028
2A29
aog0
2031
2032
2033
zo34
209!,
2036
20.37
20138
2039
3O{O.aot,,,.
L423
1431
1458
1481
1540t528
L134
L362
1'293
LL76
L223
LL99
TLOS
1082
964
89{
T'6
799
882
882
?9e
752
658
62?
658
729
6?,3
1882
t9?7
L9?7
2000teg4
188e
1988
2000
,L7A
20E3
2r.54
224e
2249
2,296
2L7s
226L- -?26L
22Al
2225
2225
2223
2273
222^5
2119
2L3L
20?L
1965
2(Az
eq43
TLTtIr
11
11
11
11
11
11
23
0
o
0
11
113.
23t5t8
L5
45
91
91
LILTL2'Ll1
LILT
L29
105
82
7a
93
105
].L7
105
93
82
93
70
70
105
82
70
58
58
58
58
47
23
23
23
1.2
23
L2
2(I44.3o{5
Bo46
204?
2Q48
?i049.
20EO
2051
265.2
, .t
r:.
ii
ti
ti
ll
ii
i:
?,
I
i
l'
THTOKOL MODELING - M-136 BT'RN GROT'IIDS
CIIEN-NORTIIERN NO. 5-L79-9I SCENARIO 2
ICE.4RW'SESOUITIIEND
RANDOIT! WALK INFORUATION FOR TCE (FOR USE WIEE RTSK ASSESSMENT)
This spreadsheet takes ttre output from Rand,om Walk at four specifiedlocations and gives the corresponding concentrations.
FIRST RrrN ( 60 YEARS )TcE coNcENTRATIoN (ppb)
WELT, IPCAIION
YEAR B-8
1991
L992
1993
L994
1995
t996
L997
L998
1999
2000
200L
2002
2003
2004
2005
2006
2007
2008
2009
20LO
20LL
20L2
20L3
20L4
20L5
20L6
20]-7
20L8
20L9
2020
202L
2022
2023
2024
2025
2026
2027
L2
P
u
M
PI
N
ts
w
E
Lt
L
o
c
A
TI
o
N
8-6/E-7
23
0
24
24
24
48
L2
L2
24
36
36
48
36
24
35
24
24
36
60
36
24
24
24
24
36
36
36
24
35
36
L2
0
L2
0
L2
L2
0
E-3
35
0
24
L2
24
24
0
0
0
0
L2
L2
L2
L2t2
L2
24
L2
L2t2
L2t2t2
L2
L2
L2
L2
L2
0
L2
0
0
0
0
0
0
0
E-4
0
0
0
0
L2
L2
L2
L2t2
L2
L2
L2
L2
L2
L2
L2
L2
L2
L2
L2
L2
L2t2
L2
L2
0
L2
L2
L2
L2
L2
L2t2
L2
0
L2
2028
2029
2030
203L
2032
2033
2034
2035
2036
2037
2038
2039
2040
204L
2042
2043
2044
2045
2046
2047
2048
2049
2050
2051
2052
2053
2054
L2
0
0
0
0
L2
L2
L2
L2t2
L2
L2
L2
L2
L2t2
L2
t2
24
L2
L2
L2
L2
L2
L2
L2
24
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
L2t2
L2
L2
0
0
0
0
L2
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
SHTOKOL MODETTNG - M-136 BI'RN GROUIIDS
C.qEN-NORSIIERN NO . 5-L79-9L SCENARIO 3TCg-3RW'SONORTHEND
RANDOI{ WAlfi TNFORMATTON FOR TCE (FOR USE lfrtE RrSK ASSESS!{ENT)
this spreadsheet takes th,e output from Rand,oa walk at for:r specified.rocations and gives tbe coresponding concentrations.
FIRS? RI,N (60 YEARS)IcE coNcElllIRAIIoN (ppb)
!|ET,L LOCATION
YEAR B-8 B-6/E-7 E-3 E-4
1991
L992
1993
1994
1995
L996
t997
1998
L999
2000
200L
2002
2003
2004
2005
2006
2007
2008
2009
201 0
20LL
201,2
20L3
2014
2015
20L6
20l.7
2018
20L9
2020
202r.
2022
2023
2024
2025
2026
2027
23
23
L2
L2
35
47
35
82
59
94
94
70
94
L64
141
153
L64
L29
223
L64
L76
223
2352tt
zt]-
258
235
L76
L99
2AL
246
258
293
293
235
199
235
35
47
94
82
141
105
118
L77
L65
189
189
247
306
377
483
554
636
73L
707
813
860
954
978
1060
L037
1143
1131
L249
L273
L4A2
1355
L426
1355
L426
1390
1414
L567
0
0
0
L2
24
24
24
24
24
36
35
36
59
47
95
118
L07
107
118
L42
225
284
308
355
427
438
415
581
58L
628
735
7LL
794
794
984
1066
1055
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
204L
2042
2043
2044
2045
2046
2047
2048
2049
2050
205L
2052
2053
2054
0
0
0
0
0
0
0
0
0
0
0
11
ztl2],t
188
223
188
246
L99
].29
Lt7
141
Lt7
106
106
LL7
106
105
Lt7g2
106
70
70
94
LL7
82
70
70
82
L496
L520
L597
1638
L697
L697
L709
L732
L697
L673
15E5
L767
1591
L673
1561
15e5
1585
1561
1503
1603
L579
1603
],,532
L4L4
L402
L320
L332
1161
1185
L244
t434
L5L7
1559
L67L
1813
L730
L754
L7L8
1801
1884
1908
L979
2133
20a6
2097
22t6
2L57
2097
2L2t
2].o9
2AL4
2062
2038
2026
0
0
0
0
11
0
1L
11
0
0
0
0
0
0
0
IIIOKOL }IODELING - !{-136 BI'RN GROI'IIDS
CITEN-NORTEERN NO. 5-I79-9L SCENARIO 4
ICE - 4 RW'S E SOU:TE END &3 RW'S G NORIE END
RANDOU WALK INFORIIAIION FOR TCE (FOR rrSE WITE RrSK ASSESSMENT)
this spreadsheet takes the output frou Random Walk at for:r specifiedlocati.ons and gives the corresponding concentrations.
YE"AR B-8
FrRST RrrN (60 EARS)
TcE coNcEMIRATIoN (ppb)
I{EI.L LOCATTON
B-6/E-7 E-3 E-4
1991
L992
1993
L994
1995
1996
L997
1998
L999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
20L0
201,1
20L2
20L3
20L4
20L5
20L6
20L7
2018
20L9
2020
202L
2022
2023
2024
2025
24
24
24
24
35
24
L2
L2
L2
24
36
48
48
24
24
L2
0
24
24
24
L2
L2
L2
0
L2t2
0
L2
L2
L2
L2
L2
24
24
L2
36
24
35
48
L2
L2
L2
L2
L2
L2
L2
0
L2
12
0
0
0
0
0
0
24
24t2
L2
L2
L2
L2
L2
0
L2
L2
L2
0
L2
0
P
u
u
PI
N
It
!,
F
L
L
t
o
c
A
TI
o
N
0
0
0
0
L2
L2
L2
L2
L2
L2
L2
L2
0
0
0
0
L2
L2
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
2026
2027
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
2041
2042
2043
2044
2045
2046
2047
2048
2049
2050
205L
L2
L2
L2
L2
L2
t2
L2
L2
L2
L2
0
L2
0
0
0
0
0
0
0
0
0
0
0
0
0
0
l2
L2
L2
0
0
0
0
0
0
0
0
0
0
0
0
0
o
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
o
Appendix B
Listing of Projeaed TCE Concentrations for Monitor Wells B,8,B6lE7, E3, and E4
TIIIOKOL.UODEI.I}IG - U-136 BT'RN GROT'IIDS
CEEXS-NORSEERN NO. 5-L79-9L
SCS}IARTO 2
TCA - NO REUEDILTION
(using correct particleinput tiues; L974-86;tben to 1991)
RAIiIDOU !9AIiK INFORI{ATION FOR ICA (FOR USE IrITE RISK ASSESS}TENT)
This spreadsheet talces tbe output from Ranrdou Walk at four specified
locations and gives tbe corresPonding concentrations.
FrRST RIIN ( 60 SEARS )tcA coNcEt{TRATToN (PPb)
WEI.I IOCAEION
YEJAR B-8 B-6/E-7 E-3 E-4
1991
L992
1993
],,994
Lee6
1996
L997
1998
1,999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
20LO
2011
20L2
20L3.20L4
2015
20L6
20L7
201.8
20L9
2020
202L
2022
2023
2024
0
0
0
o
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
6
0
6
6
6
6
L2
18
5
L2
29
35
23
29
35
47
70
53
58
53
88
88
93
111
L23
IL1
L23
0
0
0
0
0
6
6
6
L2
29
24
4L
53
65
59
94Ll2
L23
165
159
188
206
24L
276
288
335
335
382
364
388
488
488
564
570
o
o
0
0
0
0
0
0
0
0
0
0
o
0
0
0
0
0
0
0
18
36
4L
36
53
77
LO7
L24
154
L72
183
254
272
331
2025
2026
2027
202A
2029
2030
203L
2032
2033
2034
2035
2036
2037
2038
2039
2040
204L
2042
2043
2044
2045
2046
2047
2048
2049
2050
2051
2052
0
0
0
0
0
0
0
0
0
0
0
0
o
0
0
0
11
L7
L7
23
23
23
28
28
34
34
34
40
105
99
93
88
99
L29
L29
70
76
76
99
88
82
64
53
82
70
70
70
58
64
76
82
82
70
70
47
47
588
576
676
74L
676
705
729
653
688
682
694
664
676
682
7tL
705
64L
700
664
64L
505
564
564
570
500
453
447
464
337
397
438
462
509
473
568
568
657
663
698
722
805
864
923
911
929
953
894
947
929
1030
1048
1089
1036
LOTL
LOTL
1101
A\IERAGES:
A\IIERAGES:
AITERAGES:
YEARS 1991 IERU 2O2t ( 30 gEjARS )
0.0 29.7 L48.2 33.4
Y:EARS 2022 TERr' 2Os2 (30 Y:EARS)
10 . 4 86.5 642.7 765
EIIEIRE 6]. TT;AR UODEL RI'N
5 .1 57 .O 388 .7 392.6
TEIOKOL UODELING - U-136 BI'RN GROI'IIDS
CEEN-NOR:TEERN NO. 5-L79-9L
SCENARTO 2
TCA - SOTITE E}tD REMEDIATION(usi.ng correct particleinput times; L974-86itben to 1991)
RATIDOU WAI;K IIIFORUATTON FOR TCA (FOR I,SE I{ISE RISK ASSESSI.IEI{T)
Tbis spreadsbeet talces tbe output froru Ramdom Walk at four specifiedlocations and gives the coresPonding concentrations.
FrRST RI,N (60 Y:EARS)tcA coNcENIRATXoN (PPb)
WEI.L I'CATION
YEAR B-8 B-6/E-7 E-3 E-4
1991
L992
1993
L994
1995
1996
L997
1998
L999
2000
200L
2002
2003
2004
2005
2006
2007
2008
2009
2010
20LL
201,2
20L3
20L4
20L5
20L6
20L7
20L8
20L9
2020
202L
2022
2023
2024
0
0
o
0
0
0
0
o
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
o
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
Pg
Dt
PI
N
t
w
E
Lt
L
o
c
A
Tr
o
II
2025
2026
2027
2029
2029
2030
203L
2032
2033
2034
2035
2036
2037
2038
2039
2040
204L
2042
2043
2044
2045
2046
2047
2048
2049
2050
2051.
2052
0
o
o
o
0
0
0
0
o
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
o
0
0
0
0
0
0
o
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
o
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
AI,IERAGBS:
AIIERAGES:
A\IERAGES:
YEARS 1991 IERL 2O2l (30 SEARS)
0.0 0.0 0.0 0.0
YEjARS 2022 TER[' 2052 (30 Y:E;ARS)
0000
EIITIRE 61 E;AR UODEL RIIN
0.0 0.0 0.0 0.0
TETOKOL !{ODELTNG - U-136 BI'RN GROI'NDS
CIGN-NOR:EEERII NO. 5-L79-9L
SCENARIO 3
TCA - NOREE E}ID REUEDISTION(using correct pa::ticleinput tiues; L974-86;then to 1991)
RANDOU WAI;K INFORIIATION POR ECA (rOR USE IIIIE RrSK ASSESSUEI{IT)
This spreadsheet tal<es the output frou Ranrdon Walk at four specified
locations and gives tbe corresponding concentrations.
FIRST RI,N (60 rEARS)
TcA coNcENfRAlIoN (PPb)
I{EI.L IPCAIION
YEAR B-8 B-6/E-7 E-3 E-4
1991
Leg2
L993
L994
1995
L996
L997
L998
L999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
2010
20LL
20L2
20L3
20L4
20L5
20L6
20L7
2018
20L9
2020
202L
2022
2023
2024
0
0
0
0
0
0
0
0
0
0
0
0
6
6
6
6
6
6
5
6
6
L8
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
23
23
4L
41
4L
47
53
47
65
70
70
65
0
0
0
0
0
0
0
0
0
0
0
0
L2
18
24
53
53
35
7L
77
88
94
LL2
130
165
183
183
2L2
253
242
230
283
283
295
0
0
0
0
0
o
0
0
o
0
0
0
0
0
0
0
0
0
0
0
6
6
0
0
0
6
6
18
6
30
o
53
53
47
2025
2026
2027
2024
2029
2030
203L
2032
2033
2034
2035
2036
2037
2038
2039
2040
204L
2042
2043
2044
2045
2046
2047
2048
2049
2050
205L
2052
59
23
53
23
4L
59
59
59
105
L23
106
94
88
111
100
LL7
tL7
82
100
94
LL7
100
94
L23
106
106
94
111
318
330
324
37L
377
407
483
483
460
48347t
530
542
548
613
519
6L9
630
707
678
760
778
713
748
725
742
70L
7L3
4L
47
59
83
118
150
L66
L66
L78
2L3
249
26L
273
314
332
391
403
385
391
480
533
628
675
747
693
747
800
776
0
o
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
A\IERAGES:
A\IERAGES:
A\IERAGES:
YE;ARS 1991 EmU 2O2L (30 YEARS)
0.0 15.1 74.5 2.6
YEjARS 2022 IERL 2052 (30 YEiARS)
0 89 557.8 348.7
ENTIRE 51 ITJAR UODEL RI'N
0 .0 5L.2 311.0 L72.9
SETOKOL I,IODELING - U-135 BT'RN GROTIIIDS SCE}IARIO 4
CEEN-NORTEERN NO. :5-L7g-gL TCA - SOTIIts A}ID NORTE
END REIIEDIAIION(r:sing cotrect Pa::ticleinput tiuesi L974-86itben to 1991)
RANDOT.! ![AIK MFOR!{ATION FOR TCA (FOR gSE WISE RISK ASSESSUET{T)
tghis spreadsheet taJ,ces tbe output _frorn Randou WaIk at f,our specified
iocati6ns and gives tbe corresponding concentrations.
FIRST RtN (60 YEARS)
TCA coNcEIf,tRATIoN (PPb)
TIEI,L I'GITION
YEAR B-8 B-6/E-7 E-3 E-4
1991
L992
1993
].,994
L995
1995
L997
1998
L999
2000
2001
2002
2003
2004
2005
2006
2007
2008
2009
20LO
2011
20L2
20L3
20L4
20L5
20L6
20L7
2018
20L9
2020
202L
2022
2023
2024
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
2
6
1
P
uu
Pr
N
G
w
Et
L
L
o
c
A
TI
o
N
0
0
0
o
o
o
0
0
0
0
0
0
0
0
o
0
o
0
0
0
0
0
0
0
0
0
0
0
0
0
o
0
0
0
2025
2026
2027
2028
2029
2030
2031
2032
2033
2034
2035
2036
2037
2038
2039
2040
204L
2042
2043
2044
2045
2046
2047
2048
2049
2050
2051
2052
A\IERiLGES:
A\IERAGES:
A\IERAGES:
6
6
6
6
6
0
6
6
0
6
o
6
6
6
6
6
6
0
6
6
0
0
0
o
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
Y:EjARS 1991. gERU 2O2l (30 rE.aRs)
o.o o.o 0.0 0-0
YEARS 2022 SERU 2052 ( 30 tTiaRs )
0400
E}TTIRE 61 Y:E]AR UODEL Rt'N
o.o 2.O 0-0 0-0
Appendix C
Baseline Risk Assessment by IHI
BASEIJNE RISK ASSESSMENT
1.0 INTRODUCTION
1.0.1 A baseline risk assessment for trichloroethylene CICE) and 1,1,1-trichloroethane
(TC$ingroundwaterispresentedinthissection DatafromprecedingsectioruwiUbeusedto
estimate and evaluate potential human health risks associated with o(posure to TCE and TCA
in ground water. Fotr different rcmedial alternatives will be used for predicting TCE and TCA
concentrations, exposure doses and associaed heal8t risks. The following human heatth
evaluation has been modeled after the risk assessrnent commonly used in the Remedial
Investigation/Feasibility Study GI/f$ phase of CERCT-A site evaluations.
7.O.2 Obiective
1.0.2.1 The objective of this baseline risk assessment is to present analyses of the potential
human health risks associaH with selected ground water contaminants and remediation
scenarios at the Thiokol M-136 Burn Grounds site.
1.03 Scope of Assessment
1.0.3.1 This risk assessment utilizes the ground waEr modeling proje$iors of TCE and TCA
concenEations to deternrine poEntial ocposre doses and associated health risks. The ground
water computer modeling is basd on nonibring well data recently colleced throughout the
Thiokol site.
1.0.4 Organization
1.0.4.1 In response b EPA guidance (EPA, 19E9), the following risk assersment contairs four
comtnon elements: 1) indicator &emical selection;2) an exposure assessrnmg 3) a bxicity
assessmeng and 4) a characterization of risk associated with the actud or potential chemical
o9osurc.
1.0.5 GuidanceDmmmts
1.0.5.1 Ttre primary guidance doorments used for this assessmmt are the Risk r{ssessner,
Guiilance for Supfand, Hwrun Halth Eoalutbn Manul (US. EPA, 1989'), thc
Eruironmantal Eoalwtion Manual (U.S. EPA, 1989a), and the Guiilance for Conilucting
Rnteilial Inoetigations anil Frcibility Stuilia unilcr CERCI/ (U.S. EPA, 1988). Other
references used include the Sryafund Erosurc ,4ssrssrrtmt Manwl (U.S. EPA, 1988b) and the
Integrated Risk Information System (IRI$ Database.
1.1 SELECTIONOFINDICATORCHEI,IICAIS
1.1.1 Chemicals Identilied in Shdlow Gmrurd l{ater Aquifer
1.1.1.1 For the purpos€s of this risk assessment, a preliminary selection of indicator chemicals
was conducted, basd on analpical results for seleccd monitoring wells in the M-136 Burn
Grounds. Indicator chemicals are those which are viewed to'dominate" the health risks at a
partiorlar site, based on their frequency of detectiory persistence, mobility, toxicity and other
chemical-and site-specifi c considerations.
Monitoring well data used for this selection process was ggnerated from Well Nos.86, B8, E3,
E4 and W (i.e, all wells for which computer modeling proiections were generated) and induded
analytical data from sampling conducted in November and December, 1990 and March, 1991.
Chernical contaminants identified in this ground water sampling inctuded TCE, TCA,
chloroform, l,ldicNoroethene and tetracNoroethme.
1L.2 TridrloroetheneOCE)
1.121 Trichloroethene (TCE) was selected as an indicator dremical at the M-136 Burn
Grounds. The rationale for this selection is as followsi
1)TCE is present with the greatest frequmcy and in the highest concentsations in ground
water samples collected to date on the Thiokol site (November/December, 1990; March
191; See Table 1.1.1);
2l TCE has been idmtified as a Probable Human C-arcinogen (Oass 82) by the
Environmental Protection Agency;
3) TCE ismobile and persistmtinground water.
TABLELlJ
CHEMICAIS DETECTED IN SI{AIIOW GROI,'ND WATER
M.135 BI'RN GROI,'NDS
Monitoring Wdls: B6,Bt,83, Bl & E
Sarrpling Rounds: 1;1.ngDl0, U2|U$O, gltglgl & 3DU9l
Frequcncyof
Detection
Highest Detected Average Detected
Chemical
Trichloroethme (TCE)
1,1,1-Trichloroethane (TCA)
Chloroform
1,1-Dichloroethene
TetracNoroethene
7N%
56%
67Vo
56%
22Vo
3300
270
29
110
15
ConcenEation ConcenEation
7W6
752
22
702
74
1.1.3 | il,,l{tidrloroethane (rCA)
1.1.3.1 1,1,1-trichloroethane (TCA) was selected as the second indicator for this risk
assessment, based on theaveragedetected concentration, which ranked second behind TCE
(Table 1.1.1).
T2 EEOSI,'REASSESSMENT
l.Ll Intsoduction
I,z.lJ The puqpose of this section is two-fold: 1) to identify potential current and future
o(posure pathways throrgh which ground water contaminanB may migrate to an orposure
poin$ and 2) b estimate the tyrye and magnitude of o<posrre(s) that a rcceptor population
might receive at the o(posurc point(s).
1.2.72 Erposure is defined as the gqjeqt of a human rceptor with a chemical or physical
agent.l This cpntact occurs via an Epesle.pathtygy, which is defined by four components: 1) a
source of drernical release inb the mvironmenq 2) an environmmtal medium for transport of
the chemical; O a point of poentid human o(posure; and 4) a route of exposure at the receptor.
A compleE, and therefore significant, er<posure pathway is one which is comprised of all four
of the above elements
12.13 Once a complete o(posure pathway has been idmtified, the amount or dose of chemical
intake for the receptor is catctilated, usinB standardized assumptions, eguations, and site
specific data (which may indude computer rodeling predictions of conaminant
concmtratioru). This estimatd dose, combined with chemicat+pecific bxicity information, is
then used to draracterize the actual or potential health risks associated with the chemical
contamination of the site.
l.L1..4 For the purposes of this assessnrnt, estimated fuhrre TCE and rcA concentrations in
ground waten will be guerated from computer modeling. This modeling has been calibrated
using monibriry well data recently colleced at the Thiokol site. In Novenrber and December of
lRisk Assessnent Guidance 6r Superfund, Volume I, Human Health Erraluation Manud (Part
A) US. EPA/Wl|€9lfiZ, Decsnber 19E9.
1990 and March 1991, unfiltered monitoring well samples were collected and analyzed for a
variety of constituents, induding the contaminants of PoEntial concern.
1,2.2 ReceptorDdinition
1^2.Ll Due to the renrote location of the M-136 Bum Grounds, no ctrrent hurnan r€aeptor
populatiors ocist in the immediate vicinity of the site. Therefure, for the purposes of this risk
assessmmt, a hypothetical human receptor population will be used O deErmine potential
health risks associated with TCE/TCA-contamination of the shallow ground water aquifer.
The following assumptions have been made for this hlpothetical receptor population:
1)The hypothetical human receptor population is located at the property boundary of the
Thiokol site;
2l The hypothetical human receptor population is located hydrogeologcally downgradient
of the M-136 Burn Grounds, and, thereforc, would be subject to any ground water
contamination plumes originating from this source and/or estimated by computer modelinp
3) The hlpothetical human recepbr population uses the shallow ground waEr aquifer for
domestic purposes, induding drinking, wastring and showerinp
4) TCE/rcA concentrations in this shallow aqpifer have been deterrnined by computer
modeling prof'ctions for eadr remedial scenario;
5) Worst case monitoring well proiectioru have been directly o<trapolated to this
hypothetical domestic water supply (i.e., a 4CI ppm modelling proiection is eqgirnlent to a
400 ppm concentration in thedonrestic water supply).
l.L4 CurrmtPotentidExposurePathways
7.2-4.1 An examination of orrent potential sposure pathways at the Thiokol site indicates
that no complete el<posurr pathways for human receptors ouren0y qist. The rationale for this
finding is as follows
1. Althouglr TCE/TCA<ontamination of the strallow ground water aguifer has been
documened at the Thiokol site, otis aquifer is not ctrrmtly used for drinking water
purposes. fherefore, no poinB of potentiat human oposure odst in relation to this oposure
medium, thereby resulting in an incompleE exposure pathway.
2. Access to the M-136 Burn Grounds is arrently severcly restsicEd, therefore mluding the
possibility of ornent human ogosure to contaminated soils or surhce water.
3. No potentid human rec€ptor populatioru for this pathway are located in the immediate
vicinity of the M-136 Burn Gtounds
12.5 Future Potential Exposure Pathways
12.5.1 Due to the renrote location of the Thiokol site, it is unlikely that future land use
patterns will significantty differ from curent land use. Additiornlly, it is unlikely that the
shallow ground water aqgifer in the vicinity of the Thiokol site will be developed as a source
of domestic waEr. Actess to the M-136 Bum Gounds will continue to be severely restricted in
the future.
12.6 Hypotheticd Exposure Pathway
t2-6J In light of these corsideratioru, a hlpothetical cxposure pathway has been created in
order to estimate and evaluate the potential health risks associatd with this pathway. This
hypothetical c\posurc pathrvay involves the use of the shallow ground water aquifer for
donrstic purposes. In order to crcate a'complete" pathway for this scenario, the following
assumptions are made:
1) The release sourte to the *rallow ground water aquifer is the M-136 Burn Grourds;
2l The route of TCE/TCA migntion to the ogosure point is via the shallow EFound water
aquifer qntem;
3) The point(s) of ogosure b TCE<ontaminated gronndwater are the domestic water-use
activities of drinking and showering.
4l Contaminant conctntsations at these ogosrre poinB are cpruidered eqgivalent to the worst
case monitoring well proiectiors for eadr renredial scenario.
5) The routes of ocposre at the human rcctpbr are ingestion, inhalation of rrolatilized
TCE/TCA during showeringactivitie and dermal absorption of TCE/TCA<ontaminated
water.
l.L7 QuantificationofExposurcPathwrys
l.L7.l The purpose of this section is b quantibte the ogosure (Dncentrations of TCE/TCA in
the hlpothetical ground water pathway. An o<ponrre concentration is coruidered the average
@nentsation contactd at an oqo$rrc point over the ogoced period of tirne. Exposurc
calculations seek to establish the reasonable maximum o(Posut13 (RME), a conservative
estimate of the maximum o(Posune that a single rccePtor is likely t9 encounter-
tZ.7Z Exposrre concentrations were cdoilated using TCE and TCA conctntrations estimated by
the ground water modeling. For eadr renredial scenario, the worst case monibrint well
proiections were selected for use in the o<posure equatiors. Within these monitoring well
projertioru, either a first (1991-2020D or second (2021-2050) thirty-year exPosure period was
selected, based on the highest averate concentration for each period. fhe results of this
strategy forTCE and TCA are presented inTables 12.1arrd'122.
1.L73 Exposure concenEations are calorlated as chronic dail)r intakes. or the dose received
over a selected o(posure perid. For carcinoguric health risks, the chronic daily intake or CDI,
is averaged over an o(posure period of seventy O0) years to accommodate conversion with the
cancrr slope factors used to predict carcirogutic risks. For non<arcinogenic health risks, the
e"xposurc period is estimated at thirty (30) years, the 95th percentile average for residency in
onehousehold.2
12.7.4 The potentid o<posure pathway of concern associated with the Thiokol site is the
development and use of the shallow ground water aquifer. Domestic use of this aquifu from a
hypothetical well would create the following Potmtial erPosure pathways:
lngestion of TCE and TCAin drinkingwa@
Inhalation of volatilized TCE and TCA during showering
Dernral absorption of TCE and TCA during showering.
1)
2l
3)
Although eadr of these exposure pathwap is considered separately for the purposes of the
o(postrrc assessnent, crrsrulative carcinogenic and non<arcinogenic health risks are estimated
from the sums of these pathways.
lr.t IngestionofDrlnkingWater
1i"E.1 Chronic daily intales rcceived from ingestion of water from a hlpothetical future well
wereestimatedusingEquation.&linAppadix.{. StandardqposrrreparametersfrmlEPA
(191) were used in this equation (Appendix A). Chronic daily intakes for both 3&yea" and 7&
tbidl
TABLE 1.2.1
REMEDIATION SCENARIOS AND CONCENTRATIONS
rOR TCE IN GROI,JND WATER
Rcurcdlal Alternetlvc
Worst Case
Downgradlent Well
30-Year
ErposurePerlod
IvladuumTCE
Concentratlon (pgll.)
AverageTCE
Concen trati on (;rgtT.)
#l -Noremedlatlon E-3
v6/E-7
E-l
8-6/E-7
2027-zWO
1991-2020
2296 2039
il2 - Four reovely wells ln southern
portlon of slte
il3 -Three re(overy wells ln northern
portlon of site
il4 -Four reoovery wells in southern
portlon/three recovery wells in
northern pordon of site
60 30
2021-2050 2,16 1587
1997-2V20 48 19
TABLE 1.2.2
REMEDIATION SCENARIOS AI{D CONCENTRATIONS
FOR TCAIN GROI.'ND WATER
Bcmadlal Alternatlve
Worgt Case
Downgradtent WelF
30-Year
ExposurePerlod
MaximunTCA
Concenbatlon (pg[.)
AverageTCA
Concentratlon (pglt)
ill -No remediatlon
#2 - Four recovery wells in southern
portlon of site
#3 - Three reaovery wells in northern
portlon of site
' il4 -Four recovery wells ln southern
portlon/three recovety wells in
northern Portlon of site
E-4
N/AA
9-6/E-7
2021-2050
2021-2050
2027-2050
l10l 699
00
n8
72
0
E€518
4
a TCA contamlnation does not appear at the designated monitoring points ln this remedial scenario.
year o(posure periods were calorlated from average conctntrations of TCE and TCA and are
presented in Tables 1.2.3 and72.4.
12.9 Showering - Inhdation
1,2.9.1 During showering and dressing activities, volatile organic chemicals OOG) such as
TCE and TCA can volatilize from the water into air and be inhald. Chmnic daily intakes
received from inhalation of volatilized TCE and TCA were estimated using the equatiors in A-2
of Appendix A. Shower water contaminant onctntrations wetE assumd to be present in the
sarne concentrations as the drinking water ogosure pathway. Chronic daily intakes for both
3&year and Z).year ogosure periods were calodated from average concentrations of TCE and
TCA and are presented in Tables 7.23 and 12.4.
t.2.l0 Showering - Derural Absorption
l.L1:0.l Dernal absorption of waEr-borne contaminanB during showering or bathing can
mate an o(posure pathway. To estimate cluonic daily intakes from this pathway, Equation
A-3anditsassumptions(AppendixA)wereused. Showerandbathingwatercontaminantswere
assumd to be present in the same com€ntratioru as the drinking water sposurc pathway.
Chronic daily intakes for both 3eyear and Z}year o<poilre p€riods were calctrlated from
average concenEations of TCE and TCA and are presented in Tables 123 and 12.4.
t.Lll Uncertainty Andysis
l.Ll1.l lhis section describes the uncertainties associated with the erposurE calorlations
presented in the peceding sectioru. The purpose of the urrcertainty analpis is to detail the
sotrcts of uncertainty associatd with ocposue estimates, and therefore quahfy the degree of
confidence on whether the ogosure estimates are the maximum sposues that can be
reasonably o<peced to ocrur.
1^2'11.2 Potentiel Expooure Pathwaln
The first rnalr uncertainty associad with dl three potmtid qposrre pathways (ingsstion
of drinking water, inhalation and dermal abeorption thmugh showerinp is the likelihood of
the shallow ttrourd water aqpifu being developed for dorrstic use in Or vicinity of the M-136
TABLE 1.2.3
ESTMATED POTENTIAL D(POSI.IRE DOSES
TO TCE IN GROI.'ND WATER
Rcmcdlel Altcrnatlve
Chronic Daily Intake (CDI)'
Ingeetlonb
(mg/kg-day)
Chronic Daily Intake (CDI)
Inhalatlon (Showcdc
(mg/kg-dey)
Chronlc Daily Intake (CDl)
Derurel Abaorptlon (Shower)d
(mg/kg-day)
MeanTCB
ConcenEatlon
(ng/L)
, tt - No reuredlatlon
12 - Four reovery wells ln
southern portlon of site
il3 - Thrce recovery wells ln
northern portlon of slte
' 14 - Four rcovery wells ln
Bouthern portion/three
reoovery wells ln northern
portlon of site
289
30
t*7
6E-02
9E -04
sE -02
5E -04
8E-02
rE-03
6E-02
7B-04
IE. 04
2E-(r
9E-05
lE-06r9
a Chronlc Dally Inhke (CDI) estlmated for T0-yeat carcinogenlc exPosure perlod.
b EquaHon A-1, Appendlx A.c Eguatlon A-2, Appendlx A.d Equatlon A-3,AppendlxA.
a
TABLE1.2.4
ESTIMATE:D POTENTIAL E)(POSI,RE DOSES
TOTCA IN GROI.JND WATER
Rcurcdlel Alternetlvc
tl -No resredtatlon
il2 - Four reoverY wells ln
gouthern Portlon of slte
t3 - Three recoverY wells in
northern Portion of slte
t4 - Four recovery wells ln
southern Portion/three
reooverY wells ln northern
portlon of site
Chrcnlc Dally lntekc (CDl)'
lngeadon
(urg/kg-daY)
Chrontc Dally Inteke (CDI)
lnhalallon (Shower)
(mg/kg-deY)
Chronlc Dally Intake (CDl)
Dersrel Abeorptlon Shower
(mg/kg-day)
McanTCA
Concentrellon
1pg/t)
69
0
5r8
4
2E-02
_b
rE-02
tE-04
2E-V2
_b
2E-02
rE-04
4E-05
_b
3E-05
2E-O7
a chronlc Dally Intake (cDI) estimated for 30-y-ear non'carclnogenlc P"tls'
b No rlsk analysls perforrred for thls remedlal llternative, due t6 pr"dl"t"a concentrations of 0 throughout exPosune pertod'
Burn Grounds. Ihe negative factors influencing this developnent potential are in follows:
1) No resident populations orrently exist within the immediate vicinity of the M-136 Burn
Grormds;
2, No future residmt populations are lilcely to exist in the imrrcdiate vicinity of the M-136
BumGrounds;
3)The shallow ground water aquifer is of poor quality and low yield in the vicinity of the
M-l36 Burn Grounds. Higher qua[ty aquifers with better yields qist at reasonable
depths, thereby making the shallow agurfer a relatively undesirable source of domestic
water;
4', A recent well sunrey of the locd area indicates that no domestic wells developed in the
shallow ground water aqpiftr exist within the immediate vicinity of the M-136 Burn
Grounds
12113 Ground WaEr Monitoring E ftapolations
A second uncertainty associated with the erposure pathway analysis is the assumption that
ground water concentrations predicted for a partiodar monitoring well acrurately reflect
concentratioru that would be observed in a donrestic well. Corsidering the locations of all
monitoring wells used for this risk analysis (within or adiacent to the property boundaries of
the Thiokol sit+ it is highly unlitely that a domestic well would be developed in the
immediae vicinity of the Thiokol monitoring wells used in this analysis Since any domestic
well that might be developed in the future would probably be located at some distance away
from these wells and the contaminant source M-136 Burn Grounds), contaminant cpncentrations
in this dornestic well would potutially be less than those measued and predicted for the on-
site monitoring wells. llrerefore, it is likely that the use of on*ib and boundary monitoring
well predictions teneraEs a worst case, or up,per bound, estimaE fur contaminant concentratiors.
13
13.1
TONCITYASSESSI\{ENT
nackgpund
13.1.1 The pulpose of a bxicity assessrrtmt is to weigh available aridmce regarding the
potential for partiortar oonhninanB to cause advetse effecB in aposed individ"als and O
provide, where possible, an estimaC of the rclationship between the exErt of ogonrre to a
contaurinant and the incrcased Ukelihood and/or severity of adverse efftcts.3
3tbid1
13.12 Toncity assessments are generally accomplished in two steps. HaZard identification
involves determining whether the chemical causes adverse hedth effecs, and, particulafly, if
the effec(s) occurs in humans. The second step, dose-response evaluation. is the quantification
of the relationship betrreen dose of the ctremical rreived and the incidence of adverse effects
in the el<posd population. Quantitative risk assersmmts typically address two categories of
effects: 1) the potentid aorE or chronic non<arcinogenic effecB of the chemical, and 2) the
potmtid carcinogenicity of the chemical. When applicable, information of the potential
developmental and reproductive health effects is also included.
13.13 Of vital importance to the toxicity assessnent process is the concept of a threshold of
response. The basis of safe levels of ocposure for certain chemicals is that there is a
"threshold" dose below which there is no demonstrable effect. This applies to both acute and
chronic non<arcinogenic effects. The threshold of effect for a particular chemical is described
by the Reference Concentsation (RC) and Referencrc Dose (RfD) determined from chronic and
subchronic inhalation and oral o(posurcs. For orample, a g!U!S-@BfD is an estimate of the
daily ocposure for a human pop'ulation, induding sensitive individuals, that is likely to be
without appreciable risk of adverse effecB during a lifetime.
13.1.4 Carcinogenic &emicals ar,e considered not to have a threshold of effect. That is, no
dose, however snall, is cpnsidered b be risk-free from a carcinogmic effect. In this case, EPA
uses a twe'part evaluation in which a chenrical is assigned a'weight of eviderrce"
classification as shown in Table 13.1, and then a slope factor is calorlared. The slope factor.
usually the upper 95th percent ctnfidence limit of the slope of the dosercsponse cune, equals
risk per unit dose or risk permg/kg/day and is ergressed as (mglkgdayF. the oral and
inhalation slope factors for TCE that have beo dareloped by EPA and described in Health
Effects Summary Tables4 have been used in this assessment and are shown in Table 13.2
4US. ffa, Health Effects Assessnrent Sumrnary Tables (HEASD. 190. Fourth Qtrarter FY-
1990. Pts9G9211U.
Gury
TABLE13.1
EPA 1{'EIGI{TOF.EVIDENCE
CIASSIFICATION SYSTEM FOR
c.nncuvocnncrnF
Desciption
A
Bl or
92
Hurnanorcinogen
Probable hurnan carcinogar
81 indicates that limited human data are available.
82 indicates sufficimt evidence in animals and inadequate or no
evidmce in hurnans.
Possible hurnan carcinogm
Not dassifiable as to human carcinoggnicity
Evidence of non<arcinofnicity for hurnans
c
D
E
73.2 ToxicologicdProfiles-TCEmdTCA
1.3.2.1 Summaries of the toxic effecc of TCE and TCA are presened in Appendix B of this
report The bxicological profiles provide descriptiors of both the aorte and duonic non-
carrinogmic effects of both chernicals and the potential effecs of TCE.
133 ToxicityAssessmmtforNo*C-acinogenicE0ftds
133.1 The Reftrcnce Dose RfD) is the most commonly used toxicity nalue for evaluating non-
carcinogenic effece resulting from ogosrre to chesricals at hazardous waste sites The
Integrated Risk Information Sptem (IRIS) is an EPA data base containing uptodate health
risk and EPA regulatory information br a number of cheuricals IRIS contains only those RfDs
and slope factors that have been verified by the RID or Carcinogm Risk Assessrnent
Verification.Endeavor (CRAVE) Workgroups and is considered to be the preferred source of
toxicity information.
sDial
,
1332 A search of IRIS on8/15/97 indicated the status of the Oral RfD and Inhalation RC
Assessments for TCE to be "pending." The Oral RfD for TCA was withdrawn as of 8/1/97; the
Inhalation RfC was listed in IRIS as ?ending.- llrerefore, the Toxicity Values for TCA used in
this risk assessment atr those values listed in the US. EPA Health Effects Summary Tables
(HEAST), 1990. Chronic RIDs, for oral and inhalation toutes of expozure, the confidence level,
the critical effect, the RID basis and source along with the uncertainty and modifying factors
are presented in Table 132. Similar information for the chronic effects of TCE is not available
in the orrrent HEAST tables firetefore, an oral RID for TCE of 0.W mg/kg/day for chronic,
non<arcinogenic effects, was used in this assessment based on an EPA Lifetime Drinking Water
Health Advisory for TCE.6 Health Advisories are developed for Onedan Tenday, Longer-
term (approximaely Tyears) and Lifttime qposur€s based on data desoibing noncrcinogenic
end points of bxicity. In this case, EPA used a study by Kimmerle and EbenT to identify a
LOAEL of 55 ppm (300mg/m3) for liver and kidney effece. Udng the assumptiors of 8 m3/day
as the volume of air inhaled during a day,70 kilograms as the body weight for an adult, 5/7 as
an adiustsrent from 5 days/week exposure to a daily dose, and 03 as the ratio of the dose
absorbed, a Total Absorbed Dose OAD) was calorlaed as follows:
TAD= (3fl)mg/m3l@/da9@aosl = 73img/kg/day
(Dkg)
The Reference Dose (RID) was determined according to the equation:
RfD=73imgrkgtday=Q.N73|mgkg/day
(100x10)
Where 1,00 is an uncertainty facbr, chosen in actordancc with N.&S/ODW guidelines for use
with a LOAEL from an anirnal study. From this value a Drinking Water Equivalent Level
(DIVTL) can be determind again using the assumption of Z) kg body weight for adults and 2
L/day water consumption by an adulr
DWEL =(0.00735 mg /kglday)0D kg)
2L/day
o26mg/LtCfiWL,
6trichloroettrylene Health Advisory, Office of Drinking Water, US. Environmental hotection
Apncy,[darch 37,19E7.
7rcmmerle, G., ard A. Eb€o. 1973. Meabolisur, exoetion ard bxicologCr of tsichloroethylene
after inhalation. 1. fxpairwmt exPosute on.Ets. Arclr. Toxicol.3Oslls.
Table133 TO)OGTYVALITES: POTENTIALNON4ARCINOGEMCETTECTS
Chemical Chrcnic RfD
(mg/ktaay){
Confidence
lcvel
CriticalEftu RfDBasis/
Source
Unctrtainty/
Modifying factors
Oral Route
ItrA
TCE
Inhalation Route
lCA
TCE
009
0.fi7
03
o.67
1m0
1m0
M
M
M
M
Hepatotoxicity
Kidney/CNS
Hepatotoxicity
Hepatotoxicity
a/HEAST
Water/
Calculated
b/HEAST
Water./
Calculated
1m0
1m
a Based on route-b-route extrapolation
b These values differ ftom those in the HEA (US. EPA, 1984) because the study drosen as the
basis for the inhalation RID values was changed to conform to the inhalation study chosen as
the basis of the oral R(D derived in IRIS butwithdrawn asof 8/7/97.
M = Medium confidence level (assumed)
1,3.4 ToxicityAsscssmcntforCarcinogenicEffects
1.3.4.1 Weight of Evidmce-Since the EPA carcinogm policy states there is no safe level of
orposure for a carcinogen, we must, therefore, address orposure in terrns of "accephble" risks.
EPA has placed TCE in the 82, Weight of Evidence Caegory, as a hobable Human Carcinogen
with sufficient evidmce in animals and inadeqpate or no evidenct in humansE (see Table 133).
TCA has beor asdgned by EPA to "Category D Not Classifiable as b Human Carcinogenicity."
Ilrereforc, the carcinoguric risk of TCA is not considercd further in this docurnenl
!3.42 Slope Factor-An IRIS search on7/18/91lismd the status of the Carcinotenicity
Assessment (CAD for TCE as'withdrawn" for further review. However, EPA has assigned
TCE a slope factor of (0.011 mg,/kg,/ day)-l for ingestion, based on studies by NCI (1976) and NTP
(19&l) and has assigned an inhalation slope factor of (0.017 mgtkg/day)-l Uasea on the
evidence of lurg cancer in mice.9
Erbid4
elbid4
13.43 The Toxicity Values for the potential carcinogenic effects of TCE are zumrnarized in
the Table below:
Table 133 TOnCInr VALITES: POTENTIAL CARCINOGEMC ETTECTS
Chemical Slope Factor (SF)
(rnc/kc-dav)'1
Weight-of Evidence TlpeofC-ancer SF/SFSource
Classification
Oral Route
ICE
lnhalation Route
ltcE
0011
0017
82
82
a Water/HEAST
Water/HEAST
r lhe type of cancer is identified only for Cass A carcinogens.
1.4 RISK CHARACTERIZATION
1.4.1 This section integrates the ocposure and todcity ass€s$nents into estimates of the
health risks associated with shallow ground water contaminaHon in the viciltty of the M-136
Burn Grorurds Hunran health ri*s are divided inb two distinct categories carcinogmic and
c (chronic) risks. Carcinogmic anit duonic health risks for exposure to TCE are
evaluated in this section; only dronic (nonorcinogenid health risks for lCA ocposrre are
evaluated, due to the absence of carcinogenic evidmce for this chemical. Additionally, a risk
characterization of the ormulative total of these independent pathway risks will be estimated
and evaluated.
1.4.2 Carcinogenic Hedth Risks - Methodology
l.4.Ll Carcinogenic hedth risks are estimated as the incremental probability of an
individud derreloping cancer over a lifetime as a result of exposurc. Carcinogenic risk
characterization uses a variable known as the slope factor (SF)- which convefts estimated
daily intakes averaged over a lifetime of eccpozure dirrtly to the inernental risk of an
individual developing cancer. To determine carcinogmic "risk' the slope factor is used in the
following way:
Risk-CDIn xSF
Where: Risk a unitless probability of an individual developing cancer
CDTTO the chronic daily inake br eadr potential o(posure pathway,
averaged over Z) years (mglkgday)
the slope factor (mglkgday)SF
1.4.22 Cancinogenic risks for the inhalation and ingestion exposure pathways were calorlated
separatel, since thm are different slope factors for these two exposur€ routes. For inhalation,
a slope factor of 0.017 mg /kgday was used in the risk eqgation; for ingestion, a slope factor of
0.011 mglkgday was used. For the dermal abeorption pathwan the inhalation slope factor of
0.077 mg/kg4ay wils usd, based on evidene by Io, et d (1990) which indicates that the
inhalation and dermal absorption pathways are similar in the rate of uptake of a chemical
similar in properties to TCE.
1.4.23 Once carcinogenic risks were calorlated for each exposure pathway, a total risk profile
for each remedial renario was obtained by adding the individual pathway risks. This
calculated figure was tlren comparcd to orrently existing guidelines for acceptable levels of
risk Accordint to the National Contingency Plan (NCP), a risk of 1 x ld, (that is, a
probability of one additional case of cancer for errery million people exposed) is the talget
residual risk level for a site.
1.4.3 Chronic Non<alcinogenic Health Risks - Methodolory
1.43.1 The poEntid for a duonic nonatrinogpnic health effect to ocor is evaluacd by
comparing an exposurc level over a specified time pedod (e.g.,lifetime) with a reference dose
derived for a similar €r<Posutt period. The reference dose (RfD) is the dose reqgired b cause a
health effect. The Hazard Quotient is the ratio of an exposrre level for a subsance over a
specified time period to refer€llcedose ftpm the subsance derived from a similarergonre
period as shown in the eqpation below.
Hazard Quotient = CDI30IRID
Where:CDI3O Chronic daily intake for a particular ocposure pathway and
chemical of conctrn, averaged over 30 years (mglkgday)
RfD Reference dose (mglkgday) for chernical of cpnctrn
As a general rule, if the hazard guotimt o<ceeds unity, there is concern for non-carcinogenic
health effects.
1.4.3.2 Non<arcinogenic health risks for the Thiokol sits were calculated in terms of a chronic
ocposrre only; dronic elgosrres for hurnans range in duration fmm seven years b a lifetinre.
This strategy rests on the assumption that the non-carcinogmic health risks of the selected
exposurc pathways (domestic use of the shallow ground water aguifer) are ormulative in effect
and would not be observed in duratioru shorE than a chronic erponrre period.
1.4.33 Once the hazard quotient for a partiorlar ogosurc pathway and substancr was
estimated, the overdl non<arcinogenic potential for each pathway was determined for both
TCE and TCA. lhisapproach .rssutnes that simultaneous subthreshold e,xposures to several
chemicals could result in an adnerse health effu. This sum, calld the hazard indo<- is eqgal
to the sum of the hazard guotimB of each srbsAnce in a partiodar oposure pathway, and was
generated in the following way:
Hazard Index - CDIIIE/RIDIGE + CDIrcAlRID"ca
Where: CDfrcE Chronic daily intake of TCE for a partiorlar o(posure pathway
(e.g., ingestion of drinking water fum ground water)
CDIrat = Chronic daily intake of TCA for a particular sposute pathway
(e.9, ingestion of drinking water from ground waer)
TABLE 1.4.1
CAI{CER RISK ESTIMATES
Pethway/Rcmedlal
Sccnarlo
CDI
(mg/kg-day)
CDIAdf.for
Absorp.
SF
(mg/kg-day)
Welght of
Evidence
SF Basls
(Vehlcle)
Total
Pathway Rlsk
SF
Source
Expocure Pethwap Ingeodon of Drlnklng Water
Remedlal Soenarlo fl
Remedial Scenario il2'
Remedlal Scenarlo il3
Remedlal Scenarlo #4
68 -(}2
9E-04
5E -m
5E -04
No
No
No
No
0.011
0.011
0.011
0.011
B2
B2
B2
B2
Heast
Heast
Heast
Heast
Water
Water
Water
Water
7E-0{
9E-06
6E -04
6E-06
Brpoiurc Pethwey: Inhalatton of Volatallzed TCE Drulng Showerlng
Remedial Scenarlo #t
Remedial Scenarlo #2
Remedlal Scenarlo #3
Remedlal Scenarlo #4
8E -(n
lE-03
6E -02
7E.M
w
w
w
w
No
No
No
No
0.017
o.017
0.017
o.ol7
B2
B2
82
B2
Heast
Heast
Heast
Heast
ater
ater
a ter
ater
lE-03
2E-05
lE-03
1E-05
Total CmcerRlsk (Ingestlon + lnhaladon) Hypothetlcal Residentlal Populatlon (Welght of Evldence 82)
Remedlal Scenarlo #t
Remedial Scenarlo #2
Remedial Scenarlo #3
Remedlal Scenarlo #4
lE -03
3E-05
lE-03
2E-(E
SF=Slope Factor
CDl=Chronic Daily Intake (from Tables 1.2.2 and 1.2.3)
TABLE 1.4.2
CHRONIC HAZARD INDEX ESTIMATES
(Iremleal AvgConc(rroll)CDI(mo/ko/dav)
RfD
(mo/koldav)
Hazard
Ouotlpnt Palhwav lfazard fnder Tolal F-rnosurp Haz Indcy
D(POSURE PATHWAYs INGESTION OF CONTAIVIINATED WATER Pathway Scenarlo Index Scenario Index
TCE 2099
30
1587
19
5.&lE-02
8.57E-04
4.53E-02
5.43E-04
0.007
0.007
0.007
0.007
8.3
0.1
6.5
0.1
o.2
0
0.2
0
TCA 699
0
51EI
2.008-02
0
r.488-02
r.14E-04
0.09
0.09
0.09
0.09
Ingestion 1
2
3
4
1
2
3
4
8.5
0.1
6.7
0.t
t
2
3
4
19.4
0.3
r5.3
0.2
Inhalation I0.9
0.2
8.6
0.t
D(POSUBE PATHWAY: INHALATION Or VOCS DURING SHOWERING
TCE 2039
30
1587
19
7.68,E42
t.l3E-03
5.98E-02
7.30E44
0.007
0.007
0.007
0.007
10.8
o.2
8.5
0.1
TCA 699
0
518
4
2.50E-02
0
1.85E-02
1.43E-04
0.3
0.3
0.3
0.3
0.1
0
0.1
0
Once the hazard indices for each pathway wete estimated, the total hazard index for all
pathways was estimated using the following equatioru
Total Exposure llazard Index HIi + HIs 6+ HIy6
Where HIi = lfazard index for the ingestion (drinking wat€r) pathway
cdorlated as a sum of TCE and TCA hazard qgotimts
HIs/i = Hazard index for the shower (inhalation) pathway calorlated as a
zum of TCE and TCA hazard guotimts
HIs/d = llazard index for the shower (dermal abeorption) calorlated as
a sum of TCEand TCA hazard quotienc
A total hazard indoc was calorlated for eadr remedial alternative. These results are
presented in Table 1.42.
1.4.4 Quantification of Health Risks
1.4.4J IngestionofContaminaEdDrinkingWatc
Health risks for the ingestion of contaminated drinking water exposurc pathways were
calctilated forboth carcinogmic and noncrcinogmic health effects. ResulB of these
calorlations are presented in Tables 1.4.1 and 1.4.2 For the drinking water sctnario, the cancer
risk mnged from 6 x 106 to 7 x 10'4, depending on the rruredial alternative. Cancer risks
associated with each remedial alternative were highest for the "no action" scenario and
lowest with the northern/southern trcovery well alternative. The non-carcinogenic health
risk, or Pathway tlazard lndex shown in Table 1.42 for the ingestion pathway (sum of HQfCg
and HQ1q1), ranged from 0.1 for Scenarios #2 and #4 to 85 for the 'no action" alternative.
1.4.42 Showering - rnhdation
Carcinogenlc and non-carcinogmic health risks for the inhalation of volatilized TCE and TCA
were estimated and are presented in Tables 1.4.1 and 1.4.2. Cancer risks associaH with this
pathway range from 1.0 x 1O5 to 1.0 x 1O3. Cancer risks associatd with the "no ac6on"
renredial scenario (#1), were highesg the northern/southern rccovety well scenario gsneracd
the lowest cancer risks. Chmnic noncrcinogenic hazad quotienc br this pathway ranged
from 0.1 to 10& depending on the remedial renario. the PathwayHazard' Indices were 10.8
for Scenario #1 and 0.1 for Scenario #4.
1.4.43 Showering - Delutd Absorption
Carcinogmic and non<arcinogenic health risks for the dermal absorption of TCE and TCA from
shower water were calctrlated accprding to the Equation A-3 in Appendix A. Both the
carcinogmic and non-carcinogenic health risk for dermal absorption are much lower than for
ingestion and for inhalation from showering and thus did not contribute in the summation of risk
for either catqgory. For example, a total pathway risk of I x 1(I3 for ingestion vs. a risk of 3 x 10-7
for dermal absorption ( Scenario #1) was calorlated. lherefote, the dermal absorption during
showering erposure pathway is not induded in the calorlation of Carcinogenic Total Exposure
Risk or the Chronic Totd Exposure llazard Index.
1.4.5 Total CancerRisk
1.4.5.1 The btal cancer risks for each remedial scenario are preented in Table 1.4.1. These
estimaEs r€present the zum of cancer risks for eadr pathway, assming an averate contaminant
concentration generated by eact remedial alunative. Total cancer risks range from 2 x 1fr5
(northern/southern reoverywells) to 1 x 103 (#1 and #3).
1.4.6 Total Non<ucinogenic llazard Indices
1.4.6.1 llre sum of hazardqrotienB of each ocposrue pathway for a given rcrnedial
dternative was estimated as the toal hazatd index, presented in Table 1.42 The toal
Exposure Hazafi lndo< ranged from 02 to 19.4, with the'no action'remedial scenario (#1)
generating the highest hazard indo<, and the #4 scenario generating the lowest total hazard
index.
l.L7 Uncertainty Andysis
t.{.z,J The risk measurr usd in a siE risk asssment are tlpically conditional estimates
given a considerable number of assrmptions about o<posrre ard toxicity. Tygically, the
unertainties associad with a ri* assessment are a combination of the ucertainties
associated with the qposure and the toxicity assessments. Additionally, siterelated
variables often conEibute a significant amount of uncertainty to the asscsrrent, and are
therefore important factors to consider in an uncertainty analysis.
1,4.7 2 Toricity Assessmcnt Uncertainties
The most important uncertainty associated with the toxicity assessmmt is the absence of a
chronicnon<arcinogoricreftrcncedose(RfD)forTCE. Areviewofconrrentionalsotuctsof
toxicity information (e.g., the IRIS Database) did not indicaE a curren0y ttcommended RID for
this chemical. Consequentlp following EA guidance, a chronic R(D was derived from a lont-
Term Drinking Water Health Advisory.
A source of uncertainty in the estimation of chronic health risks associatd with TCE ogosure
is the assurnption that the RfD derived from the Health Advisory is appropriate for use in
ingestion and dermal absorption pathways Lacking further information on the chronic effects
of TCE, this assumption was made in order to generate hazard quotients and indicts for each of
the pathways under consideration. Because TCE has been dassified as a Group B: Probable
Human Carcinogm, and that the estimated ercess cancer risk associated with lifetime exposurc
to drinking water conaining TCE at2fo pglliter (the DWEL) is approximately 1 x 1014, the
relative importanct of chronic non<arcinogoic effects takes on a great deal of uncertainty.
Also, based on these uncertainty facbrs, the duonic non<arcinogenic hazard indices generated
from this derived RfD contain a largo degree of uncertainty than normal. It is unknown,
however, whether this uncertainty underestimaEs or overestimates the potential non-
carcinogenic healft risks associatd with dnonic TCE exposure.
1.4.73 ExponrreAssessmentUncefiinties
Uncertainties in the qposurE asses$netrt portion of the risk assessmmt have been examined in
Section 72.77. Of critical importance in the uncertainty assessment is the cucept of a complete
oryosure pathway. Pathways which lack one or morc of the exposure cmponmts (i.e., a soulce
of chernical release; an mvironmental transport nredium; a point of poEntial human exposure
and a rcute of ogosure at the receptor) atr mt compleE and therefore do not corutitute
legitimate health threats.
For the purposes of this risk asssment, both a hlpothetical rccepbr population as well as a
complete o(posutr pathway were creatd in order to quantify poEltial hedth risks associatsd
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i';l
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ri "'..:,t -!
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a!-'ratI':.|
I
with domestic use of the strallow ground water aquifer. A number of assrmptions, discussed in
Sections 122 and 12.4 were rnade in order to legitimize this o<posure pathway. In light of
these assumptions, a large degree of uncertainty is inherent to the exposure pathway analysis
of this risk asssmml This uncertainty is subsequently caried over into the risk
draracterization, which attempts to quantify long terur health risks associated with the site.
These health risks, quantified as either cancer risks or hazafi indices, are necrssarily suspect.
For enrrrple, although cancer risks associaH wi0r ingestion and inhalation of TCE-
contaminated water exceeded guidelines established by the NCP, these estimatioru cannot be
constnred as realistic health risks, based on the lack of complete exposure pathways.
In addition to the large degree of uncertainty associated with the hlpothetical ocposure
pathways, uncertaintie odst in the attempt to extrapolate monitoring well data to a potential
domestic water well. In light of the physical setting of the Thiokol site, it is uuemely
unlikely that domestic water wells would be established in proximity to monitoring wells
which provided data for this assessmmt. Thereforc, monitoring well daa and the associated
modelling predictions likely overestimaE the contaminant concentrations which would be
observed in a domestic well developed in the vicinity of ttrc M-136 Burn Gmunds.
In summary, the large degree of unctrtainty inherent in the el?osurr assessment necessarily
bias6 the subsequmt risk characterization. Cancrr risks and hazard indices gmerated from
the ogosure assessment estimatioru must be viewed with caution and in@reEd with a
sensitivity to the probability of any hypothetical s(posure pathways ever being completed
with regards to the M-135 Burn Grounds site.
1.5 Summary
1.5.1 Indicator Chemicd Selection
1.5.1.1 TCE and TCA were selecH as indicator chemicrals for the purpose of this risk
assessrnelrt 'lhe selection was based primarily on the fact that these chernicals were most
frequently found in the monitoring wells at the site and that they typicalty ocrtrred in the
highest concentratioNr.