HomeMy WebLinkAboutDAQ-2024-0104711
DAQC-963-24
Site ID 10676 (B4)
MEMORANDUM
TO: STACK TEST FILE – HOLCIM – Utelite Plant
THROUGH: Harold Burge, Major Source Compliance Section Manager
FROM: Robert Sirrine, Environmental Scientist
DATE: September 24, 2024
SUBJECT: Contact: Carsten Mortensen (801-467-2800)
Contractor: TETCO
Location: SR 32 West of Rockport Reservoir, Summit County, Utah
Source: Kiln #1 and #3
FRS Site ID #: UT0000004904300001
Permit #: 4300001004 dated May 24, 2023, revised May 24, 2023
Action Code: 3A
Subject: Review of Stack Test Reports received August 9, 2024
On August 9, 2024, the Utah Division of Air Quality (DAQ) received test reports for the Holcim – Utelite
Kilns #1 and #3. Testing was performed on July 10, 2024, to demonstrate compliance with the PM10
emission limits found in Permit Conditions II.B.2.a, and II.B.3.a. The DAQ-calculated test results are:
Source Test Date RM/Pollutant DAQ Result Source Result Limit
Kiln #1 7/10-11/24 201A/PM10 0.585 lbs/hr 0.58 lbs/hr 3.34 lbs/hr
0.006 gr/dscf 0.006 gr/dscf 0.024 gr/dscf
Kiln #3 7/10-11/24 201A/PM10 0.74 lbs/hr 0.74 lbs/hr 3.34 lbs/hr
0.006 gr/dscf 0.006 gr/dscf 0.024 gr/dscf
DEVIATIONS: None noted.
CONCLUSION: The stack testing reports should be considered acceptable. Measured
emissions appeared to be within limits at the time of testing.
RECOMMENDATION: Holcim – Utelite Plant Kilns #1 and #3 should be considered to have
been in compliance with the PM10 emission limits at the time of testing.
HPV: No.
ATTACHMENT: Stack testing reports for Kilns #1 and #3 received August 9, 2024
DAQ generated excel spreadsheets
g!1 HoLcrM
August 8,2024
Mr. Harold Burge
Utah Division of Air Quality
195 North 1950 West
P.O. Box 144820
salt Lake city, UT 84114-4820
UTAH DEPARTMENT OF
ENVIRONMENTAL QUALITY
AUG - rq '.:t)4
land deti,lued
DIVISION OF AIH OIJAI !T"
RE: Stack Test, No. 1 Bag House, Title V Operating Permit No. 4300001004
Dear Mr. Burge
Enclosed is a copy of the PMro Particulate Compliance Test, conducted in accordance with sections
ll.B.2.a.loftheOperatingPermit. TestingwasdoneattheHolcim,UtelitePlantonJulyl0&Ju|y1.1.,2024.
I certify that;
a) Testing was conducted while the source was operating at the rate and or conditions required
b)
by the approval order, operating permit or federal regulations.
During testing, the source combusted fuels, used raw materials, and maintained process
conditions that represented normal operations and was operated under other relevant
conditions specified by the Executive Secretary.
Based on information and belief formed after reasonable inquiry, to the best of my knowledge
the information found in the report is true, accurate and complete.
c)
lf you have any questions, please call.
Operations Manager
Holcim-US, Utelite Plant
Holcim US, 6375 W Three Mile Canyon Road,
Phone 801 -467 -2800, www. holcim-us. com
Coalville, UT 84017
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-]]fi[bTpARTMENT oF
erlviiouuglrnu ounUT
AUG - I 2024
DIVISION OF AIR OUALITY
PMIO PARTICULATE COMPLIANCE TEST
CONDUCTED FOR
UTELITE CORPORAI"ION
KILN #I BAGHOUSE
July l0-l1,2024
by:
TETCO
391 East 620 South
American Fork, UT 84003
Phone:801 492-9106
Fax:801 492-9107
I Frepared for:
I ffi[:::rporation
I
Coalville, UT 84017
I r,r;i;"ffi"
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CERTIFICATION OF REPORT INTEGRITY
Technical Emissions Testing Company (TETCO) certifies that this report represents the truth as
well as can be derived by the methods employed. Every effort was made to obtain accurate and
representative data and to comply with procedures set forth in the Federal Register.
Michael McNamara
Reviewer:
Date:
Dean. Kitchen
Reviewer:
Date:
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TABLE OF CONTENTS
Perge
Introduction
Test Purpose.............. ......,..........1
Test l,ocation. 1'ype of Process. ...................1
Test Dates ............. "..1
Pollutants Tested....... .................1
Test Participants........ .................1
Methods Applied..... ................... i
Principle of EPA Method 2014........ ...........2
Discussion of Errors or lrregularities.......... ...................2
Quality Assurance. .....................2
Summary of Results
Emission Results...... ..................1
Process Data.......... .....................3
Allowable Emissions ................._j
Dcscription of Collected Samples. ...............3
Cyclone Cut Rate and Isokinetics............ ......................:i
Sourcc Operation
I)rocess Clontrol Devices Operation .............-5
Process Representativeness..... .....................5
Sampling and Analysis Procedures
Sarnpling Port Location............. ..................6
Sampling Point Location........... ...................(r
Sanrpling Train Description .......6
Sampling and Analytical Procedures........,.. ..................7
Quality Assurance ......................7
Appendices
A: Complete Results and Sample CalculationsB: Raw Field Data
C: Laboratory Data and Chain of CustodyD: Facility Schematic Representation. Production ar-rd Control Equipment DataE: Calibration Procedures and ResultsF: Related Correspondence
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Table
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II
III
IV
Irigure
t,IST OF ]-ABLES
Paqe
Measured PMro Emissions......... ........................3
Cyclone Cut Rate and Isokinetics............ ..........4
Sample Point Location............ .........6
Complete Results Appenclix A
LIST OF- FIGURES
Schematic Representation of Facility ................./\ppendix t)
Schematic of Method 201A1202 Sanipling T'rain......... ....... Appt:ndix E
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INTRODUCTION
Test Purpose
This test was conducted to determine the PMro particulate emissions from the baghouse serving
Kiln # l. Emissions are expressed in grains per dry standard cubic foot and pounds per hour.
The results are used to determine compliance with the facility Title V Operating Permit,
Permit No. 4300001004.
Test Location. Tvpe of Process
The facility is located south of Wanship, Utah. The process consists of firing calcine shale as it
passes through a rotary drum and expands to a less dense material. The expanded material is
used in the construction industry as a lightweight aggregate.
A schematic of representation of the Kiln #l exhaust stack is given as Figure I in Appendix D.
Test Dates
Three test runs were completed July l0-11, 2024.
Pollutants Tested
The tests were a gravimetric determination of PMro particulate in accordance with EPA Method20lA and202 found in 40 CFR 51 Appendix M. Method 202 for condensable particulate
matter (CPM) is for informational purposes and not for compliance.
Test Participants
Test Facility
State Agency
TETCO
Alex Judd
Robert Sirrine
Mike McNamara
Dave Vernon
Xaun Dang Jerimiah Opthof
Methods Applied
EPA Methods 201,4' and202 were used for each of the tests.
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Princirral of EPA Method 201A
A gas sample is extracted at a constant flow rate through an in-stack sizing device. which separates
particulate matter (PM) greater than PMro from particulate nlatter lcss than PMro. Variations
fiom sampling conditions are maintained within well delrned limits. 'fhe particulate mass is
detenrrined gravirnetrically after removal of uncombined water.
A schematic of the sampling train is given as Figure 2 in Appendix E.
Discussion of Errors of Irregularities
There were no errors or irregularities.
Quality Assurance
1'esting procedurcs and sample recovery techniques were according to those outlined in the
Federal Register and the Quulity, Assuruncc lTundfuxtk.for Air Pollution lvlcusurcmerrt Sv.stcm.t'.
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SUMMARY OF RESULTS
Emission Results
l'able I presents the compliance test results.
P-rocess D_eta
The process was operated according to standard procedures. All pertinent process data was
available lbr recording by agency personnel. Baghouse AP readings are included on the daily
log sheet fbr Kiln # l. in Appendix D.
Allowable Emissions
The allowable PMro concentration for this source is 0.024 grldscf. The allowable PMrg
emission rate for the Kiln # I Baghouse is 3.34 lb/hr.
Description of Collected Samples
The sample filters for all three test runs were lightly discolored with gray colorcd particLrlate.
The front washes were all clear in appearance.
Cvclone Cut Rate and Isokinetics
The Federal Register specifies that tests for PMro using EPA Method 20lA shall either not
exceed +1p of 10p and the measured flow rates (AP's) shall not exceed the calculated Ap
-)
TABLE I Measured PMro Emissions
0.0062
0.00ss
0.00s5
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maximum or AP minimum, or one AP may exceed the AP tnaximum or rninimum if the
isokinetics remain within +20oh of 100%.
The cyclone cut rates. isokinetics. and number of AP's which exceeded the allowable range arc
shown in Table Il.
TABLE II Cut Rate and Isokinetics
Run ##pts <APnrin or )APnra.
1
2
J
0
0
0
% lsokinetic
9.96
10.13
9.91
t07
103
107
SOURCE OPE,RATION
Process Control Devices Operation
All process control devices were operated nonnally. Baghouse AP readings are found on the
daily log sheet for Kiln #l in Appendix D.
Process Rerrresentativeness
Tlic facility was operated normally. Production data is found in Appendix D.
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SAMPLING AND ANALYSIS PROCEDURES
Samplinq Port Location
The stack inside diarneter is 47 inches. Poft location is depicted in Figure l. 1-he ports arc
iocatcd I 1.5 dianteters (45 feet) downstrearn fiom the last disturbancc and 8.4 diarrieters (ii tect)
upstream fiom the next distllrbancc. There are two samplc ports with inside diameters ol sir
inches.
Samrrling Point Location
'fable Ill shows the sarnpling point distance from the insiclc wall according to Fil'}A Method l.
Each point is markecl and identified with a glass tapc wrapping and numbered. l'hersc lroints arc
determined by measr"rring the distance liom the inside wall ancl adding the rclerencc (port)
measurement.
TABLE III Sam Point Location
Distance (inches) fiom
lnside Wall
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5
6
2.07
6.ti6
13.91
33.0e
40.11
44.93
Samnling Train Description
'fo determine the actual emission rates fbr this stack, 40 CFR 51, Appendix M.
and202 were fbllowed.
All sampling trains were made of inert materials, (i.e., Teflon. Stainlc'ss Steel.
prevenl intcrfcrence of the sampled gas and particulate.
l'hc stack analyzer used to conducl Methods 20lA and202 is constructccl to ntcet tlre
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specifications outlined in the CFR. The temperature sensors are K-type thennocouples.
Heater. vacuum and pitot line connections have been designed to be interchangeable with all
units used by the tester. The probe liner was of Teflon. A sarnpling train sketch is found in
Figure 2 in Appendix E.
Sample boxes were prepared fbr testing by fbllowing the prescribed procedure outlinecl in
Method 201A and202.
Samnling and Analvtical Procedures
All test sampling and analytical procedures employed were as specified in 40 CFR 60 Appendix
A and 40 CFR 5l Appendix M.
Qualitl' Assurance
All equipment set-up, sampling procedures, sample rccovery and equipment calihrations werc
carried out according to the procedures specified in 40 CFR 60,40 CFR 5l and the Quulitv
Assurunce Handbook./or Air Pollulion Meus'urentent Syslems.
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APPENDIX
Complete Results and Sample Calculations
Raw Field Data
Laboratory Data and Chain of Custody
Facility Schematic Representation, Production and Control Equipment Data
Calibration Procedures and Results
Re lated Correspondence
APPENDIX A
Complete Results
Nomenclature
Sample Equations
A
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TNBI,II IV
COMPI-EII: RtrStJl.TS
PM r(, PnRTtC'UI-A-rE MA rrEIt
KIt,N I BNCHOI.JSF-
Synrbol
Date
[]rlter #
llcgin
I:nd
Irb,,
,\l.l
Vrn
'1 ,"
Ahead
b,
,,np,,
./,11r,.n.,,,.,,
,/.^t,
lr
('f
I)u
('or
o:
N. & ('o
Vttt.,j
Ilw.
xd
M,i
M.
'%t
lt
QsS't
Qst i'c'
Nrc
('
l).,,
l)t"
C'r
I)io- r
7.
T
PC
lrhn
lr.
()
4,,
Mpu r,,,
Mrrr,,,,,
M.,ru,
CPM t,,,,
Crpul,,,,,
C..rn,
FiRp1111,11
1..:R>pM l0 (l
[:R"r,n
Dolc
_llnle Tesr Bc!]m
l irnc'l lsl t-nd.'d
Mctcr BrronLlnc Pressurc
Orficc Prcssurc Drop
lvlcrer ( i|bralroil \' ,:iclor
Volumc 6as Sxmpled--Meler Condrtors
A\:j l\4clcr'fernperJturc
Arc r\r(:x lllocled b\ Srnrple I ranr
Sric[ ( ros5 Ssrtrnrxl Arcx
Probc Bk)ckgc fnclur li,r I'Ml 5
Sq Roor Velocrt\ ltcssure ( orerdd for hl'
Sq Ro(!l V.lftll\ Hcad ( r\ rnsurcd)
Sq R(xn Vclocrt\ llcad (adt lor blocltrlc rl'il('ccrsi^ )
WcIlhr \Villcr (i)llt'.lcd
Durxlkil r)l Tr\l
Pilot lirbc ( ocllicrcnr
No//le Drinlcrer
volumc ", ( irlrn Dro\rdc
Volunlc ". ()\\gcn
Volunrc'1, Nrlrogcn Md ( arhon Mrrno\rde
voluilc C$ Simplcd (Slindxrd)
Volunc Wnler Vanor
I racl(n H.,O rn Stxcl Cs
F'ractron of Dn Cas
Molccular WI Dn Cas
ivolccular Wt Slacl Cas
Pcrccnl lsoknclrc
(;N slrcxnr viscosit\
D^ Cns SnmDlc Rile
Srnrp[rU liale
Reynolds Ntrmbcr
( unrilllhanl ( orrcetron tncktr , PM: 5
P['ll0(ull'ornt
PN'll i (il |,otril. (ondrlrt,n llurll lr
Re'-cstrnratcd ( unnnrlilanr ( orr*tron ljJckrr
PMI s ( u1 Pod ( ondilron Burll ln
Rrlrool D5l)/DslLl (0,99<Z< l.0l)
r\rlj Strcl Tcmpcraturc
Strcl ( ros\ Scclrontl Arca
slrcl Slatc Prcssure
Simpl(' Pon lJaftrmctrrc Pr6surc
Strcl Prcs\urc
StacL Cas Vollnrcrrc lrlotr Rile lStd) i\{'csurrd
Stacl (;a$ Volurclnc l_lo\ Rate {Aclual} Mcsurr'd
velGtt\ ol'Slucl Cs Meourcd
MGs ol P\'llll.(, l,r(tculalc
Viss ol >PM I r) ll I'arlrculilc
Mrss ol-(ondensrbles
Concenlrauon ofl,M lt) l) Pilruculntc
('oilccnlrot,on ol >PMI0 o Parlrculxlc
( onccn[alron ol Condcnsrbles
HmrslroD Ralc ol'PM I () ll Ptnrculale
Emrssiur Rile o[>PM lo {r Pantculatc
[:mrssroil Rale of( ondulsrbles
Dintensions Run # I Run #2 &I]-{J
1n0t2024 7/t v2024 7fi l/2024rtq0 49 t 4q?i4:40 8:15 t)..15
15:41 9:16 10:48
Description
ln llg Abs
ln Il.o
drntcnstonles!
24.10
0.-16()
0.994
25 26.1
99.1
17.(x)
t7-14.e
0.009tt
0 4869
().4{i2 t
0482t
(r3.7
60.25
0.713
0.21 5()
6.70
ll.l()
80.t0
t9. I l9
3.004
0. |.16
0.864
29 60
28.02
106 7
220.t
0.3 r7
0.64ti
2288.6
Ll()8
9.96
L39
l.l t3
2.39
0 99tt
'7.7
2.0
50.8
0.0062
0 00t6
0.04 r0
0,6-j-1
0.1 64
4.1 75
24.05
0 360
0.994
23 277
li6.-l
17 00
173.1.(,
0.()()9li
0.49t7
0.4889
0.4lill9
6.i.6
58 75
{t.769
0.1150
650
I -r. l0
80.40
17.994
2 999
0. l4-1
0.8-s 7
19.5()
?7 91
roi 2
220 7
0.306
0.616
2212.4
L r09
10. 13
2.47
r.lll
147
0.q99
24.05
0 160
().994
25.-+26
96..1
17.(x)
t7i{ q
0.(x)efi
0..l8lt.l
0.t836
()..tt{-16
67.Ii
61.00
0.77 3
0.2.150
l). i0
12.n0
80.70
t9.302
.i. t 97
0. lrl2
0.85tt
29 55
?7 91
I07.;l
l2 I ..1
0.:i I6
0 65q
2277.7
1 il0
9.9 t
2..ttt
1 il5
2 lli
() 99[i
Root ln ll,0
Rool lD ll,o
R1)oi l[ ll.0
Granl"
lUrnulcs
Drlrensronlesr
lnchr'r
Pcrrrnt
Pcrcurl
l,cracnt
dscl
5cl-
F-rJCnoo
[:rncton
lb/lhnx)l
lh,lbrnol
l'erc$l
tnltroDotsc
dsclrl
Drm(.N!onl!'ss
f)rDrcnsronlcss
Sq Ft
hr HrO
ln Hg Abs
ln llg ,\bs
dsclin
clrrr
lpnl
millrgmms
nrlLgranrs
nrllrBrtrilrs
tr, dscl
gr / dscl'
rr i dscl'
lb/hr
lb/hr
tb,,hr
.,\ \/(;
2118.2 293.1 29(r.5 2t)2-B
r2.018 I2.048 I? 04n-0.220 -0.120 -{t 220
24.04 21.99 23.9e
24 024 23 971 23 e71
l.l9Er'01 l.l9l:+()4 l.lltlr+().1 l.llltl+0{
2.4-1t'.+04 2.471:+04 l.46lt+04 2.{58+0.1
2.01E+01 ?.()sFr0l 2.()41:+0-l 2.0JU+03
6..1
?2
62.7
0 0055
0.00 t 9
0.0538
0.558
0.192
5.464
(r.9
2t
5li ;t
0.005-s 0.0057
0.00 | 7 0.0017
0.0467 0.0{71
0 5.i7 0.5tt25
0. t6q 0.t752
1.7 13 4.7812
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Method 20lA 1202 Nomenclature
percent isokinetic
stack cross-sectional area (li'')
see r/aP
runit heat value (British thennal unit)
'liaction of watcr in stack gas
concentration ol condensibles ( grain/dscf)
concentration of coarse part icLrlate ( gr/dsc t)
percent cart'ron dioxide in the stack gas
pitot tube coefficient (0.84)
concentration of PM r0 particLllale (gr/dscl)
equivalent stack diameter (inches)
oril'ice pressure drop (inclrcs I IlO)
olillce pressure (inches l{,O)
oril'ice pressurc head (inclres H,O) needed lbr cl,ckrnc florv rate
nozzle d iameter ( i nches)
stack flolv pressure diffbrential (inches H20)
-50o,'o effective cutofT diarnetcr of parlicle ( pr)
dianreter of the stack (t'eet)
pcrcent excess air
ernissiorr rate ol condensibles (lb/hr)
emission rate olcoarse palticulate (lb/hr)
ernission rate per rnrnBtu or torr of tuel etc.
ernissiorr rate of PM
',,
particulate (lbrhr)
emission rate of compound which replaces x
lengtli of rectangular stack (inches)
thor,rsand [Jtu
rnass of condensibles (mi I I i grarns)
rnass of coarse particulate (rnilligrarns)
nrolecular weight of stack gas. dry basis (lbilb-nrol)
rnillion Btu
rnass ol PM,o particulate (milligrarns)
rnolectrlar weight of stack gas, wet basis (lb/lb-nrol)
gas viscosily ( rnicropoisc)
t
9,bt ..
A' -'
ASAP
Btu -
B*"=
C.p'u -
L.,,rt
COr =
(',,
t'\ t'\lI0
D.,,
AII
.\l l.^. ,
\lld ,
[),,
lP=
DPs. '=
D. '-
t,A ='
Fir.n,,
El'.u,, -=
8R,,,,,,8,,
ERprr Io -
ERr :
L-
nrBtu ''
M.n,,,l =
M.,,,t ='
Ma=
mnrBtu '=
Mlvro -
M,-
Its --
T
t
T
T
t
t
T
T
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t M*",,, ,- rnolecular rveight ol'gas species (lbilh-rnol )
N, - percent nitrogen in tlre stack gas
O, " percent oxygen in the stack gas
VAP - average of the square roots o1-,AP (rnay also be referred to as ASAP)
{APr : squarc root of AP at point I o1'the clrrrent test. Method 20lA
./AP,' .= square root of AP at point I of the previor-rs traverse, Method 20 lA
{AP',,,.. = averoge of the square roots of AP fiorn the previous traverse. Method 20 lA
Pb,, =- absolute lraronretric pressure at the dr1 gas rneter (inches Hg)
Pbn - absolute barornetric pressure at the sample location (inches Flg)
P., - stack static pressure (inches I-l.O)
P, : absolute stack pressure (inches Hg)
P,,,, - absolute pressure at standard conditions \29.92 inches Hg.)
pls = number of'traverse points during the test (rninimum of 6. maximum ol' l2)0 - time of test (rrrinr,rtes)
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0r :
0,, =
Q,:
Q,:
Q,. :
Qr.' --
Q* '=
R*0" :
Il,ni,, :
T,,, :
T'=
T.ra =
Tr .=
Vm=
Vfflrr.t -=
Vn,iu =
w=
W1'u. --
X,r =
Method 20lA 1202 Nomenclature
sample time (duration in minutes) at first sample point for Method 20lA
sample time (duration in minutes) at sample point "n" fbr Method 20lA
stack gas volumetric flow rate (acfm)
stack gas volumetric flow rate (dscfm)
actual gas flow rate through the cyclone (acfm)
predicted actual gas flow rate through the cyclone (acfin)
wet stack gas std. volunretric flow (ftr/nrin" wscfin)
multiplier for V,,
mr-rltiplier tbr V,,
meter temperature (oF)
stack temperature ("F)
absolute ternperature at standard conditions (528'R)
see 0
sarnple volurne (ft3) at meter conditions
volume standard (dscf), sarnple volume adj usted to 68"F and 29 .92 inches l'lg.
nraximum allowed nozzle velocity (fps)
rninimum allowed nozzle velocity (fps)
target nozzle velocity (fps)
velocity of stack gas (fpm)
volume water vapor (scfl at 68"F and 29.92 inches Hg.
width of rectangular stack (inches)
weight of the condensed water collected (grams)
liaction of dry gas
rneter cal ibration Y-factor (di nrension less )
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Method 20lA 1202 Sample Equations
7ol : Vtn.,6'(T, + 460)' 1039 / (0'V.' P,'Xl' D,r)
4. : lDsr I 4). n
B*, = V* / (Vm.,,' +V*)
C.pr, - M.pr.0.0 1543/Vmr14
C"ur. = M.,,r,. 0.01543 /Vmr,,1
Cpr,rrt, -- Mu1r,r, .0.01543 / Vm.1,1
D"n = 2.L.Wi (L+W)
AHd = [Q,.',. Xd. P./(T, +460)]2. [(Tn, + 460) - M.r. 1.083. AH(,,,/ Pb,,,]
Dpio -, 0.15625 . [(T, * 460) / (M- . P.)]t"0"' . (p, / Q,.)"'nn'
Ap,u., : 1.3686. l0-4. P,. M.. Vn,,"2 / [(T,+460). cpr]
Ap,,,,, = 1.3686. l0-1. P,. M.. vn,iul / [(T. + 460). Cp2]
EA =. (9/oor - 0.5 %CO) 1t0.264 %Nr - (%Or - 0.5 %CO)l
Er.p,,, = C.r,n,. Qr. 0.00857
[JI'.,-r, : C.,,* . Q, .0.00857
FlRn,n,131,, = ER/(rnrnBtu /hr)
ERpn,', ' CuM|o. Q-. 0.00857
M4 : CO3 .0.44 + Or . 0.32 + N, .0.28
M, == (Mu . Xu) + ( 18 . B*,)
lk .- [51.05 + 0.207. (]',-r 460)+ 3.24-10'5. (T, -r460): + 0.53147 -o/oO:-74.143
P. - P['r,,+(PG/13.6)
0, = 1rilP,'/./AP'.".;. (0,"., i pts)
Qn = V,'A,
0,, : 0r . r/AP,, /./APl
Q, ' Qo . X,r . P,. Tuo / [(T, + 460)' P.rd]
Q.. - [(T',+460). P,r.r/(Tuu. P,)] . [(Vrnu6 + V*)/e]
Q..' = p, . 0.002837 . [(Tr +460) / (M. . P.)]n t"'"
Q,, = Q./Xa
R,,u, = 0.4457 + i[0.-soso + (0.2603 . {Q,.' . 1., / V,,' ')]
R,,i,, : 0.2457 + ![0.:OZZ - (0.2603 . iQ*"' . pr, / V,,r 5;1
V,uo, - Vr.Rn,u*
V,n,u - V',' Rr,i,,
Vr.r'r,,,1 = Vrn.Y. T,td .(Pb,,,+ AH / 13.6)/[P"0.(T,,,+ 460)]
V, : 3.056 . Q..'/ Dn2
v, =- 85.49 . 60 . Cp. ilP . { 11t, + 460) / (P.. M-)l
V* = Wt*..0.0471-5
X6 = l-B*.
T
I
I
I
I
T
t . B*,.i . l0''
I
I
I
I
T
I
t
T
I
I
APPENDIX B
Preliminary Velocity Traverse and Sampling Point Location Data
Particulate Field Data Sheets
Preliminary
Facility Utelite co
Stack ldentification Kiln #l Baghouse Exhaust
Barometric Pressure
Estimated Moisture (Bw") l0 N
Sample Heighr from Ground 60 feet
N
Stack Dia. 47"
Ports arc 33'
,,onr rra--F-
Reference: 6"
Upstream from next disturbance
I)ownstream from last disturbance
Comments:
Averages:
TS
AP
Z Flow
Ts ZFlow
AP
Traverse
Point
Percent
Diameter
Distance From:
A r-E .
PoI--rrtsfl---rlElFIDReference
44 2.07 8.07
2 14.6 6.86 12.86 -ta,.,lj
J 29.6 I3.9r 19.91 i$c.:
4 70.4 33.09 39.09 ;8(; : ")
5 8s.4 40.14 46.14 |,b
6 95.6 44.93 50.93
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APPENDIX C
Sample Recovery
Particulate Analysis
Condensible Particulate Matter Analysis
Gas Analysis Data (ORSAT)
Chain of Custody
C
['ac i I ity
Stack Idcrrti licaliotr Kiln #
I)atc:
Mctiurd:20 tn /202
tllflIcElt$
Itiltcr Nunrber:
Irinal tgt
Inirial rgl
Nct rgi
-our-lLitcdcsllCIlien
Purgc stirrl
l)rrrsc crtd+
ml I I-0 addctl
Srrtttltlc [],rx
lmninger Numfrer lnitiuls
Inilral Volrunc of lrqrrrrl (I l;O) rn
wcigh and tliscnrd
T
T
T
T
T
T
T
T
t
T
I
I
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t
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t}utt-i\liltts
lrihcl Nuntbcr:
Sarnplc lhx
I)rlr[c stirrl
Pur!.c cnd
rll I 1"0 addccl
Imoinger Numbcr
Initial Volrrrnc ollrqrrid (l lr()) in irrrlingers. trnl)
I nitialr
I lcxnnc
rvcigh & arrall'zc ucigh arttl disc
ntPt}('I.RS
lriltcr Nrrnrbcr:
I:inal tg)
lrritial rgr
t.\ct (gt
nrn llltcr dcscrintiorr
I)rrl1lc starl
S:rnrplc llor
lmninser Number I nili:rh
nrl I I.0 acldcd
490
I
I
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t
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T
t
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T
I
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T
T
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t
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Facilitl:
Stack ltlcnti licatiort :
lriltcr Nunrbcr':
Urelite
Rinse Vol. I'iltcr & I)M|,6
> l)lvlr,,
[)atc: l lll)1202.1
Ilrrrr:
Sanrplc Bor:
nrl
nrl
Kilrt # I
Blanks &
Rinses
Filter
> PMro
Wash
n cctonc lJlank ('orrcction 0.(XXXX) g/ I 0()rr I
60.8792
0.12 r7
0.1215
s
b
b
I
2()
2()
( til'lljRIn
liinull:
Irinai.:
[;irral,111;: 0.1 2 1 (r g
l)rilveight: 0. I I67 g
Nct 0.(X)49 !
Net 4.9 mg
[:inal,111;: 60.li820 g
lnitial,ryl;: frtl*;,lZ g
(iloss: 0.002[l !r
lllank: 0.000t) g
Nct 0.0028
Net 2.8
F-irral,ry6: 60.7626 g
lnitialor,,;: (r0.7606 g
(iross: 0.0020
[]lartk: 0.0000
Nct
Nel
I'M,,,
0.0020
.1.9 n1g
2.tl nr_q
---Jt--^e
I)atc: ill6/2024 'l intc:
l)nt.,-7i?DIIJ- tinrc:
t)rrtc: 7/16/2024 .l irnc: ll:(X)
t)r,.,-7ilDIIt ti,,'.,-tJJtr,-
[)atc: Ill1612l\)3 'l irnc:
Dut.,ll7l?DDl- t i,nc:
Datc: 7l1612(124 l inrc: ti:0()
l),,t.'lTEEEi- 1i,,,", l+'l)rt
I)N{ (lnlirlnration Onll )
t,L,,lr, 7.7 ntlt
t'M,,, f.0 rlt!:
Total 9,7 nrg
l)irt,:: 7/ l-j/2-l
l)rrrc: 7ll6124
PM11y Wash l:inirl ,:
l)itral":
lnitial,:
I n itia ll:
llcakcr N unrhcr:
60.88 t9
60.8820
(r0.8'792
E
mg
Final ,:
l'inal.:
I nitiirl , :
lnit ial,:
60.7624
60.7628
60.760,1
c
b
mg
(r0.7608
llcakcr N tlttbcr:
BESULTS
l:rlter (Ivl )
I)N4r,, Wilsh (M,)
Total
I-ab l'cchnrcrau: MikclVlcNarnala
l.ah l-cchnrcian l)can Kitchcn
l,J:(X)
4.2
1J
75
t
I
I
I
I
I
I
I
I
I
T
T
I
I
t
t
I
t
T
I:lcilitr': LJtelite [)ate: l ll I120?1
llrrrr: )
Sarnplc llor: l-)
Stlck lrlcrrtillcation: Kiln # I
l:iltcr Nurnbcr 491
BIanks &
Rinses
Filter
FM11, Wash
> PMro
Wash
Acct()nc Illank C'orrection 0.0000() gi l(X)nrl Rinsc Vol. lriltcr'& ['M,,, -ltt
' l)Nl !,
().1 t99 g Finally,;:
g Prcwcight:
0. I lgti s
0.1 156 c
Nct 0.(X)-12 !r
Nct il.2 mg
62.5277
--]0
nrl
rnI
[ , lrllll2l\ ilt_______:i_'" ____r
lrinal,:
l:inal.:0.I t97
I:inul,:
ltinll":
lnitial,:
Initia l1:
ltirral 1:
l'inal.:
lrritial,:
Initial.:
62.52'76 b
Final.r1.,: 62.5277 g
Initial.ry,,: (r2.5255 g
( iloss: 0.0()22 U
Illank: 0.0000 g
Nct 0.(X)22 tr
Net 2.2 nrg
lrinal,lyl;: 62.054tt g
lnilialn"l;: 62.0526 g
(iross: 0.0022 !r
Lllank: 0.0000 g
Nct _0.9922_8
Net 2.2 nrg
PM,,,
l)atc: 7/ 16i202.1 'l irnc: lt:00t)"t.,li6EIlI- 1i,,,., l-l'o,t
[)atc: I lll612023 'l inrc:
I),,t"'lTTilDDf tir,c:
t>atc: 7/1612021 l inrc: lt:(X)
D,,t"'-7fir2EJ- 1 i,,,.,-lJil-
[)M 1 I nlirnnatiorr ( )rrly')
62.525,t
62.5256
Ilcakcr Nurlhc:r':
62.0548
(r2.054ti
s62.052'l
62.0525
Bcirker Nunrbcr:
RESULTS
l tltcr(Mr)
I'M,,, Wash (M,)
Total
2.2
6.4
ntg
nl8
mg
lrM,,,
l'M,,,
'I otel
Mikc McNanrara
[-rh lcchnician: Dean Kitchcn
6.4 nlg
n1g
ntg
11
li.6
7ll612.l
lo
4{)
mg
-3"0
I
I
T
I
T
I
T
T
t
I
T
T
I
T
I
T
T
T
T
l:acil it1':
Stack ldcntillcation:
[:ilter Nunrbcr:
[Jtelite l)alc: 7ll I l2n4
l{urr: -_ -j
Sarrplc llor: Il
Kilrr # I
Blanks &
Rinses
Filter
, PM,,,
Wash
l;inall:
l:irra l.:
492
Acct()nc lllank ('orrcctron 0.0(XX)0 g/ l(X)rnl
57.78Ul
62.2047
0.1 I 12
(). il 12
u
s
s
c
c
I-'inal.,,y6:
l)rewcight:
Rinsc Vol. l:iltcr & I)N4,,,
.. l,N4r,,
rnI
rnI
PM,1, Wash l;inirl,:
lti nrtl":
Initiirl,:
I rritial,:
lJcakcl Nrrnrhcr
5 7.7 ri06
Nct (0.0010) g
Net (.].0) mg
l:irral-ru.,;: 57.7806 B
lnitialny,,;: 51 .7707 g
(irrss: 0.(X)99 I
lllank: 0.0000 g
Nct _ 0.9099_ S
Net 9.9 mg
l-'inal.nu,1;: 62.2068 g
Ini{ial,rr,,: 62.201'l g
(iross: 0.(X)2 I
Illank: ().()000
N"t -lfoou t
Net 2.1
PM,,,
nlg
nr8
mg
Datc: '7/1612021 l inrt:
I)nt.,-TIZDIJJ- tinre
t)atc: 7/ l61202.1 l irnr:: ll:(X)
t),rt.,-i,fiDll]- I i,,,,',--1.fiil-
Datc: I ll1612()23 I inre :
D,,t",ll7iJZIJ3- [ir,c:
I)arc: 7il61102.1 'l'inrc:
Dut.'1G.EEI- t i,r,:.
I)M 1 Intirrrnation ()nlr')
l'M1,, (r.9 ntt
l>Mr , 2.1 tnq
Total_!0 __ mg
I)irte: .l5lli{J
l)atc: .l-5.lti()
5 ,-.11011
57.7706
I'inal,:
I- ina l":
lrritirrl,:
I n itia l.:
6).2069
62.206(r
62.20,17
Bcakcr NLtrnbcr:
BESUTTS
I-rltcr (Mr)
l)Mf , Wosh (Mi)
'I'ota I
9.9
6.9
[.ab lcchnician. Mike McNurrtala
I-uh lcchniciln. [)can Kitchcrr
l.t:(X)
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UTELITE DAILY KILN REPORT
5:00 PM
6:00 PM
5:00 AM
END OF
END OF
DAY SHIFT TONNAGE
NIGHT SHIFT TONNAGE
oares T rtr-'(i/
FEED
TAN K
RATE
TPH BH DP
GAS
SETTI NG
BH
TEMP
ID FAN
AMPS
KILN EXIT
TEMP
COAL
MILL EXIT
TEMP
COAL
MILL
AMPS
COAL
SETTING
day/date
7:00 AM
8:00 AM t;,,,ft .t )'t :
9:00 AM f'.,l- '-:.-' I f
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10:00 AM ljtr/L]-1
11:00 AM 0,r'
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9:00 PM . ) _-:-
10:00 PM ,
11:00 PM I r''I
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1:00 AM
2:00 AM I.t-1
3:00 AM 1 t, /r'L l-i
4:00 AM :''t .,, ,-
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,.,, ). ,5:00 AM
DAY SHIFT: Thurs thru Tues: (12 hr shifts) 7am to 7pm;
Burner: 51t.1 i
4 (circle one)
Wed: (6 hr shifts) 7am-1pm & 1pm to 7pm
KILN OPERATION
KILN OPERATION ..1
Gas on:Gas off: Reason:
Gas on:Gas off: Reason:
Gas on:Gas off: Reason:
Feed in:Feed out:
Feed in:Feed out:
"?ct: Lt
TANKS:
Silver
Rus
Coarse
Problems, Goncerns or Events:
NIGHT SHIFT Thurs thru Tues: (12hr shifts) 7pm to 7am; Wed: (5 hr shifts) 7 pm-1am & 1am to 7am
Utilitv Hand: -f,e ,.,. -ro
Gas on;Gas off: Reason:
Gas on:Gas off: Reason:
Gas on:Gas off: Reason:
Feed in:Feed out:
Feed in:Feed out:
TANKS:i o'. aL\ '1"i
Silver 5',riC L!"j
Orange
Rus
Coarse
Problems, Concerns or Events:
Bin Vent:
t
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UTELITE DAILY KILN REPORT KILN
,,/\\o' 3 4
END OF DAY SHIFT TONNAGE
END OF NIGHT SHIFT TONNAGE
FEED
rANK
RATE
TPH BH DP
GAS
SETTING
BH
TEMP
ID FAN
AMPS
KILN EXIT
TEMP
COAL
MILL EXIT
TEMP
COAL
MILL
AMPS
COAL
SETTING
day/date
7:00 AM lt i\,": 'l u,a t"tI:t1-i-.
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12:00 AM
1:00 PM
2:00 PM
3:00 PM
4:00 PM
5:00 PM
6:00 PM
7:00 PM
8:00 PM
9:00 PM
1O:00 PM
t1:00 PM
12:00 PM
day/date
1:00 AM
2:00 AM
3:00 AM
4:00 AM
5:00 AM
5:00 AM
KILN OPERATION KILN
DAY SHIFT: Thurs thru Tues: (12 hr shifts)7am to 7pm;
Burner: | - ..,
Wed: (6 hr shifts) 7am-1pm & 1pm to 7pm
i7 t'4 (circle one)
KILN OPERATION
Utilitv Hand:
Gas on:Gas off: Reason:
Gas on:Gas off: Reason:
Gas on:Gas off: Reason:
Feed in:Feed out:
Feed in:Feed out:
TANKS:
Silver
Oranqe
Coarse
Problems, Concerns or Events:
NIGHT SHIFT Thurs thru Tues: (12hr shifts) 7pm to 7am; Wed: (6 hr shifts) 7 pm-1am & 1am to 7am
Utilitv Hand:
Gas on:Gas off: Reason:
Gas on:Gas off: Reason:
Gas on:Gas off: Reason:
Feed in:Feed out:
Feed in:Feed out:
TANKS:
Silver
Orange
Coarse
Problems, Concerns or Events:
Bin Vent:
I
T
T
T
T
I
T
T
I
I
T
APPENDIX E
Calibration of the console dry gas meter(s), pitot tubes, nozzles diameters, and
temperature sensors were carried out in accordance with the procedures outlincd in the Quality
Assurance Handbook. The appropriate calibration data are presented in the following pages.
The nozzle calibrations are recorded on the first page of the field data sheets.
Figure 2 Schen-ratic of Method20lAl202 Sampling-l'rain
Meter Box Calibration Data and Calculations Forms
Post-test Dry Gas Meter Calibration Data Forms
Type S Pitot Tube Inspection Data
Salnple Box 'femperature Serrsor Calibration
F'ilter Balance Calibration
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Sample Box Temperature Sensor Calibration
Darc ll2l21 Calibratur'Xuan N. Dane Rclercncc: Onrega Ct,35 llA
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H Oven Watcr 33 0
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lrnpingcr Out A
Impingcr Out B
ftnpinger Out D
lmpingcr Out E
Impingcr Out F
Impin-eer Out C
lntpinger Out H
lmpinger Out I
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Annual Balance Calibration Check
Date 1123124
Denver lnstruments, ModelA-250, SN 8045284Balance
Weights Used Troemner Weight Set,
sN 98-115146
Technician
Certified Weight
orams
Measured Weight
orams
Difference
qrams
0.1 000 0.1 000 0.0000
0.5000 0.5000 0.0000
1.0000 1.0000 0.0000
10.0000 10.0000 0.0000
50.0000 50.0001 -0.0001
100.0000 100.0000 0.0000
120.0000 120.0001 -0.0001
150.0000 150.0000 0.0000
Michael McNamara
APPENDIX F
Tlre testing protocol and other correspondence related to the tests are included here.
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State of Utah
SPENCERJ. COX
Covennr
DEIDRE I{ENDERSON
Lic.Uaa* Gownor
Deparfinent of
Environmental Quality
Kiubcrly D- Shellcy
Exctulit+Dir*w
DrvrsroN oF AtRQUALTry
Boacc C' Bird
Dlrcctor
June 28, 2024 DAQC-636-24
Site ID 10676 (84)
Dave Vernon
Holcim Utelite Plant
P.O. Box 387
Coalville, Utah 84017
Dear Mr. Vernon:
Re: Holcim SWR,lnc. Utelite Plant -Kilns #l and #3 * Protocol Review and Test Date
Con{irmation - Summit Couuty
The testing protocol for the Holcim Kilns #l and #3 received June 6, 2024, has becn reviewed and
found acceptable. The agreed upon test date is the week of July 8,2A24.
Acceptance of a protocol does not relieve the ownerloperator and the testing contractor from strict
adhsrence to all applicable EPA Be*rods, Utah Division of Air Quality (DAQ) policies, Utah Air
Quality Rules (UAQR), and methods approved by the director. Any deviation from EPA methods,
DAQ policies, UAQR, and methods approved by the director must be addressed separately and
express written consent given prior to commencement of testing.
The DAQ requires that all test reports include a statement signed by a responsible official
certi$ing &at:
A. Testirg was conducted wbile the source was operating at the rase an&or conditions
specified in the applicable approval order, operating permig or federal regulation.
B. During tcsting, the source combusted firels, used raw materials, and maintained
process conditions representative ofnormal operations, and operated under such
other relevant conditions specified by the director.
C. Based on information and belief formed after reasonable inquiry, the statements
and information contained in the report are true, accurat€, and complete.
t95 tffi 1950 W.r{'Sslr L.k! City, IrfM.it"g Ad&Bs: P.O. Box 1448!0 . Srlr Lrkc CrB, Uf E4l ld4820Tohehac (801 ) 536-{000 . Prx (80t ) 5364099 . T.D.D. {80 I } 90t-39TE
w.b1.aah"gvv
Pdnrod oa t00ki, rclclcd Fpdr
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COMPLIANCE PMro EMISSION TESTING PROTOCOL
HOLCIM UTELITE, COALVILLE UTAH
KILN #I AND KILN #3
PROJECT ORGANIZATION AND RESPONSIBILITY
The tbllowing personnel are presently anticipated to be involved in the testing prourarn. Thc
tJtah Division of Air Quality (UDAQ) and EPA may have their orvn personnel to obsclve all
phases irrcluding the process.
Company
Holcirn [.ltelite Plant
P.O. Box 387
Coalville. Utah 84017
.r't-.-fco
391 East 620 South
American Fork^ tjtah 84003
Contacts
Dave Vernon
Alex Judd
(80 r ) 467-2800
(80r ) 467-2800I
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Dean Kitchen 80l-492-9106
l)uring these tests only lJolcim personnel listed above or assigrred pcrsonnel liorn the opcrating
departrnent are authorized to answer or obtain answers to pertinerrt questions on the proccss
corrditions or the test protoccll.
PRO.IECT pESCRTPTTON ANp METHOpS AppLrEp-
The sources to be tested are the baghouse exhausts of Kiln #l and Kiln #3. at the Ilolcinr lbcilitl,
located south of Wanship. Utah. l'his test will be conducted to demonstratc cornpliance witlr the
lacility's Title V Operating Perrnit nurnber 4300001004. Tcsting procedures rvill includc
accumulating process and production data as well as testing fbr PMrg emissions using EPA
Method 201A. Condensable particulate matter (CPM) will be measured according to EPA
Method 202 and is not for compliance, but informational purposes only. Tesling will consist of
three test runs.
TEST SCHEDULE
It is planned to cornplete alltesting the week of July 8.2024. The tcsting c,rew will arrive and
set up and start testing on.luly 9tl'and continue until all testing has been cornpletcd.
A pretest meeting can be scheduled il'requested by l-lolcirn or DAQ.
TEST PROCEDURES
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Three test runs will be conducted on each kilnl for PMro emissions. 'festirrg will fbllow [:Pr\
Metlrods 20lA and 202 as specified in 40 CFR 5 I Appendix M.
EPA Methods20lAl202.
The following specific items will be followed for Methods20lAl202:
l. 'fheKiln#lstackinsidediameteris4Tinches. Therearetwoportsavailablefortesting
that meet the upstrearn/downstream requirements o1'Method l. The ports are localecl 45
lbet downstream and 33 feet upstream lrorn any florv disturbancc. A total of l2 points
will be sampled, six per port. Minirnum target sarnpling tirne will be 60 rninutes. The
stack llow rvill deterrnine the dwell time at cach point and actual test tirrie.
'l'he Kiln 3 stack inside diameter is 46.5 inchcs. Thc're are trvo porls available that mcct
thc upstrcam/downstream requirements ol-Method l. '['he ports are located 45 {Lct
dorvnstream and 35 feet upstream from any {low disturbance. A total ot'12 points will be
sampled. six per port. Minirnum target sarnpling tirne will be 60 rninutes. I-he stack llorv
rvill detcrntinc thc dwell time at each point and actual test
2. EPA Method 2 will be used to determine gas stream velocity. Calibration data lbr tlre
type "S" pitot tubes are included with this protocol. Dual inclined/r,ertical rnanonreters
rvithgraduatiorrsin0.0l inchesofwaterwill beuscd.'l'heabsenceol'cyclorricllorvwill
be checked during the prelirninary run.
3. A barometerwill be used to measurethe barometric pressure. lt is perioclically chcckercl
against a mercury barometer. Prior to testing it will be checked to assurc an acourate
barornetric pressure.
4. An integratcd sanrple of the flue gas will be taken liom the exhaust linc after thc dry gas
nreter orifice during each test run and analyz-ed at the test's completion by Fyritc to
detennine the gas stream molecular weight.
5. The probe liners will be borosilicate glass or'l-eflon.
6. I)reparation and clean-up by the contractor will be performed in the contractor's testing
trailer. Laboratory work and analysis will be done by the testing conlractor as soori as
possible after all tests have been completed at 391 East 620 South. Arnerican Fork, Utah.
7.Uack hall-will be determined by EPA Method202. EPA klethod 202 analysis will bc
fbllowed as in the method.
If plant maintenance or operating problems arise during the test. the test rnay be sbpped.
This determination will be rnade by the Holcim Corporation representatives or operatiug
personnel in consultation with agency representatives
8.
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9. Current calibration data is subrnitted in Appendix B of this protocol. Any equiplnent
calibration that fall past due prior to the test date will be recalibrated prior to use.
OPERATIONAL DATA AND INSTRUMENTATION
Pcrtinent operating data rvill be made available by t{olcirn upon request by agency personnel.
TE,ST AREA
The test area slrall include the control room" stack and associatcd areas. and thc alea arorrrd thc
contractor's testing trailer for preparation. and clean-up.
TEST SITE
A sketch oi"the source is included with this protoco[.
ACCESS TO SAMPLE SITE
T'he site is accessed via stairs and ladders.
POTENTIAL HAZARDS
Moving Equipment Yes
I'{ot Equipnrent Yes
Chernical
Other
No
No
ESTIMATES OF TESTING PARAMETERS
The volumetric flow ratc. rnoisturc and stack tenrperatures are similar for both stacks.
Volumetric FIow Rate 12.000 dcfin
Moisture l4oh
Temperature 325'F
OUALITY ASSURANCE
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All testing and analysis in these compliance tests will be conducted according to Methods 20lA
and 202 and appropriate sections of the EPA Quali4t -As.surant:e Hantlbook.for Air Pollutiort
L[e a :nrrem en I Sy,stent,s Vo I u me I I I.
REPORTTNG
The emissions test report will be prepared by the testing contractor according to EPA Quality'
Assurance Guidelines. l'he contractor will furnish several copies of the test repoft to l-lolcirn.'l'his report rvill be submitted within 30 days following the completion of the tests.
EPA Method 202 rvill be included in the written report for inforrnational purposes only.
Complete copies of raw data, calculations and summary of test will be included in reports. All
process and production data will be recorded and retained for inspection and <;opying by DAQ
and EPA.
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Appendix A
Facility Schematics
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Date:
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'l'vpo S Pitot Tube Inspection Data
Pitot l ube ldentrfication:
Technician:
0 375
M. McNanrara
D,=ls l)1: I)n ?
Is I 05. D, < P^& Pr < I 50. D,'i
Yes
Ycs
Pr=0.4'76
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Ps=0.4't6
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7. < 0.125 in. Z =0.002
, .:=?.,=t - -- -\ -'- -'-w < 0 03125 in 0.004
W > 3 inchcs
Z.> 3/4 inch 7=I
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l-- - --"-- i---- ,-.-- l
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\'> 3 inchcs Y.= -1 l/2 in.
l'he pitot tubc nrccls thc specilications lbr a calibratlon faotor of0.84? Ycs
Sensor (lalibration
Heat Check 24tl
ICE WATF,R
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Datc
Dr
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Type S Pitot Tube Inspection Data
Pitot Tubc ldcntification:-51 c-2
M. McNamara
I),=0 37s ls P.r = P, 't
Is l0j.I), < P^&l)r, < 150.D,?
Ycs
Ycs
Po=0.470 tn.
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Ps=0.470
<r, < l0o
ct1 < l0o
0, '5o
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dt =
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9r= 2
0:= 3
Z<0.125in 7.=0.065
W < 0.03 125 in. W - 0.016 in
W > 3 inchcs
/,> 314 ittclt 7 ---"
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in
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lhc pitot tubc rrccts thc spccifications l'or a calibration l'actor of 0.84'l Yes
Contiuuity Check
IC]E WATER
BOII- WA ER
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TETCO
Sample Box Temperature Sensor Calibration
Ovc:n (3)
Oven (4)
Ovcn (3)
Ovcn (3)
Ovcn (4)
()vcn (3)
Oven (4)
Oven (3)
Oven (4)
Datc. ll2lA Calbrator Xuan N. Danc Rcferorrce: OnlcPa ('L35 I2n
Itnit lD
Tcmpcrature
Dil'ferencc
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In:pinger Out I)
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Impinger Out F'
lmpingcr Out C
Impinger Out H
lmpinger Out I
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TETCO
Annual Balance Calibration Check
Dale 1123124
Denver lnstruments, ModelA-250, SN 8045284
Weights Used Troemner Weight Set,
sN 98-115146
Technician
Cedified Weight
qrams
Measured Weight
orams
Difference
qrams
0.1 000 0.1 000 0.0000
0.5000 0.5000 0.0000
1.0000 1.0000 0.0000
10.0000 10.0000 0.0000
50.0000 50.0001 -0.0001
100.0000 100.0000 0.0000
120.0000 120.0001 -0.0001
150.0000 150.0000 0.0000
Michael McNamara
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C HoLcrM
UTAH DEPAHTMENT OF
Ei.|VIROI'IMENTAL AIAUTf
August 9,2024
Mr. Harold Burge
Utah Division of Air Quality
195 North 1950 West
P.O. Box L44820
Salt Lake City, UT 84174-4820
AUG
flan rt
DtvrsloN
- 9 ?t,24
lst;{{t!*,
RE: Stack Test, No. 3 Bag House, Title V Operating Permit No. 4300001004
Dear Mr. Burge
Enclosed is a copy of the PMro Particulate Compliance Test, conducted in accordance with sections
11.8.3.a.1 of the Operating Permit. Testing was done at the Holcim, Utelite Plant on July 70,2024.
I certify that;
a) Testing was conducted while the source was operating at the rate and or conditions required
b)
by the approval order, operating permit or federal regulations.
During testing, the source combusted fuels, used raw materials, and maintained process
conditions that represented normal operations and was operated under other relevant
conditions specified by the Executive Secretary.
Based on information and belief formed after reasonable inquiry, to the best of my knowledge
the information found in the report is true, accurate and complete.
c)
lf you have any questions, please call.
Operations Manager
Holcim-US, Utelite Plant
Holcim US, 6375 W Three Mile Canyon Road,
Phone 801 -467 -2800, www. holcim-us.com
Coalville, UT 84017
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AH DEPARTMENf OF
DIVISION OFAIR QUALITY
2024
liv
PMIO PARTICULATE COMPLIANCE TEST
CONDUCTED FOR
UTELITE CORPORATION
KILN #3 BAGHOUSE
July 10,,2024
by:
TETCO
391 East 620 South
American Fork, UT 84003
Phone: 801 492-9106
Fax:801 492-9107
Prepared for:
Utelite Corporation
P O Box 387
Coalville, UT 840t7
Date of report:
July 24,2024
CERTIFICATION OF REPORT INTEGRITY
Technical Emissions Testing Company (TETCO) certifies that this report represents the truth as
well as can be derived by the methods employed. Every effort was made to obtain accurate and
representative data and to comply with procedures set forth in the Federal Register.
Mike McNamara
1'
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/i I i I .- .
Dean Kitchen
Reviewer:
Date:
Reviewer:
Date:
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TABLE OF CONTENTS
Page
Introduction
Test Purpose.............. .................1
Test Location, Type of Process. ...................1
Test Dates .................1
Pollutants Tested ........................1
Test Participants........ .................1
Methods Applied..... ...................2
Principle of EPA Method 2014........ ...........2
Discussion of Errors or lrregularities......... ....................2
Quality Assurance. .....................2
Summary of Results
Emission Results...... ..................3
Process Data.......... .....................3
Allowable Emissions .................i
Description of Collected Samples. ...............3
Cyclone Cut Rate and Isokinetics.......... ........................3
Source Operation
Process Control Devices Operation .............5
Process Representativeness...... ."................."5
Sampling and Analysis Procedures
Sampling Port Location............. ..................6
Sampling Point Location........... ...................6
Sarnpling Train Description .......6
Sampling and Analytical Procedures........... ..................7
Quality Assurance ......................7
Appendices
A: Complete Results and Sample CalculationsB: Raw Field Data
C: Laboratory Data and Chain of CustodyD: Raw Production and Control Equipment Data
E: Calibration Procedures and Results
F: Related Correspondence
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Table
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II
III
IV
LIST OF TABLES
Page
Measured PMro Emissions......... ........................3
Cyclone Cut Rate and Isokinetics............ ..........,1
Sample Point Location........... ..........6
Complete Results ..... .....Appendix A
LIST OF FIGURES
Figure
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2
Schematic Representation of Facility Appendix D
Schematic of Method 201A1202 Sampling Train ........ ........ Appendix Il
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INTRODUCTION
Test Purrrose
This test was conducted to determine the PMro particulate emissions from the baghouse serving
Kiln # 3. Emissions are expressed in grains per dry standard cubic fbot and pounds per hour.
The results are used to determine compliance with the facility Title V Operating Perrnit.
Permit No. 4300001004.
Test Location. Tvrre of Process
The facility is located south of Wanship, Utah. The process consists o1- firing calcine shale as it
passes through a rotary drum and expands to a less dense material. The expanded material is used
in the construction industry as a lightweight aggregate.
A schematic of representation of the Kiln #3 exhaust stack is given as Figure I in Appenclix D.
Test Dates
Three test runs were completed July 10.2024.
Pollutants Tested
The tests were a gravimetric determination of PMro particulate in accordance with EPA Method
201A. Method 202 for condensible particulate matter (CPM) was also completed burt is lor
informational purposes and not for compliance.
Test Participants
Test Facility Dave Vernon Alex Judd
State Agency
TET'CO
Robert Sinine
Mike McNarnara Xaun Dang Jerinliah Opthof'
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I Methods Apptied
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EPA Methods 201A and202 were used for each of the tests.
t
Principal of EPA Method 201A
A gas sample is extracted at a constant flow rate through an in-stack sizing device, which separates
I particulate matter (PM) greater than PMro from particulate matter less than PMro. VariationsI from sampling conditions are maintained within well defined limits. The particulate mass is
determined gravimetrically after removal of uncombined water.
I A schematic of the sampling train is given as Figure 2 in Appendix E.
t Discussion of Errors of Irresularities
I There were no errors or irregularities.
I Oualitv Assurance
r Testing procedures and sample recovery techniques were according to those outlined in the
I Federal Register and the Quality Assurance Handbookfor Air Pollution Measurement Systems.
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SUMMARY OF RESULTS
Emission Results
Table I presents the compliance test results.
Process Data
The process was operated according to standard procedures. All pertinent process data was
available for recording by agency personnel. Baghouse AP readings are included on the daily log
sheet for Kiln # 3, in Appendix D.
Allowable Emissions
The allowable PMro concentration for this source is 0.024 grldscf. The allowable PMro emission
rate for the Kiln # 3 Baghouse is 3.34 lb/tr.
Description of Collected Samples
The sample filters for all three test mns were lightly discolored with tan colored particulate. The
front washes were all clear in appearance.
Cvclone Cut Rate and Isokinetics
The Federal Register specifies that tests for PMro using EPA Method 20lA shall either not exceed
+ I p of lOp and the measured flow rates (AP's) shall not exceed the calculated AP maximum or Ap
minimum, or one AP may exceed the AP maximum or minimum if the isokinetics remain within
+20%o of 100%.
TABLE I. Measured PMro Emissions
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The cyclone cut rates, isokinetics and number of AP 's which exceeded the allowable range are
shown in Table II.
clone Cut Rate and Isokinetics
#pts <AP.in or >APmax
0
0
0
4
Cyclone Cut Rate
10.28
9.89
9.91
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I souRCE .PERATT.N
t Process Control Devices Operation
I All process control devices were operated normally. Baghor;se AP readings are fbund on ther daily log sheet for Kiln #3 in Appendix D.
I Process Representativeness
I Thc facility was operated normally. Production data is found in Appendix D.
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I SAMPLING AND ANALYSIS PROCEDURES
Sampling Port Location
The stack inside diameter is 46.5 inches. Port location is depicted in Figure 1. The ports are
located 1 1.5 diameters (45 feet) downstream from the last disturbance and 8.4 diameters (35 fbet)
upstream from the next disturbance. There are two sample ports with inside diameters of six
inches.
Samnlins Point Location
Table III shows the sampling point distance from the inside wall according to EPA Method L
Each point is marked and identified with a glass tape wrapping and numbered. These points are
determined by measuring the distance liom the inside wall and adding the ret-ereng6r (port)
mcasurement.
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I TABLE III. Sam Point Location
Distance (inches) from
Sample Point
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2
1J
4
5
6
2.05
6.79
13.76
32.74
39.71
44.45
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I Samnling Train Description
To determine the actual emission rates for this stack. 40 CFR 51, Appendix M. Methods 20 I A and
202 were fbllowed.I
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All sampling trains were made of inert materials, (i.e., Teflon, Stainless Steel, glass, etc.) to
prevent interference of the sampled gas and particulate.
The stack analyzer used to conduct Methods 201A and 202 is constructed to meet the
specifications outlined in the CFR. The temperature sensors are K{ype thermocouples. I.leater,
vacuum and pitot line connections have been designed to be interchangeable with all units used by
the tester. The probe liner was of Teflon. A sampling train sketch is found in Figure 2 in
Appendix E.
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Sample boxes \ryere prepared for testing by tbllowing the prescribed procedure outlined in Method
20lA and202.
Sampling and Analytical Procedures
All test sampling and analytical procedures employed were as specified in 40 CF'R 60 Appendix A
and 40 CFR 5l Appendix M.
Qualitv Assurance
All equipment set-up, sampling procedures, sample recovery and equipment calibrations were
carried out according to the procedures specified in 40 CFR 60, 40 CFR 5l and the Quulit.t,
Assurunce l{undbook /br Air I'ollulion lvleasuremenl S1,stems.
APPENDIX
Complete Results and Sample Calculations
Raw Field Data
Laboratory Data and Chain of Custody
Raw Production Data
Calibration Procedures and Results
Related Correspondence
APPENDIX A
Complete Results
Nomenclature
Sample Equations
A
TABI,E IV
COMPI,ETE RBSULTS
PM IO PARTICUI,ATE MATTER
Kiln #3 BACI IOUSE
Compl.te Resuhts
I
Symbol
Date
Filter #
Begin
Lnd
Pb,,
AH
Y
Vm
T'.
Ahcad
A"
bf
iAp,,
iAp."u.ur"6
.iap
wr",.
Tr
cp
D,
Coz
o2
N2&CO
VITl.td
Bw.
xd
Md
Ms
Yol
u
QsS'f
QsCyc
Nre
C
Dso
Drn
Cr
Dso-r
Z
T"
As
Pc
Pb,
P.
Q.
QO
Mpuro o
M>pruto o
M"o.
Cpuro o
C>puro u
C"r.
ERp",o n
ERrpv'o n
ER"r-
Description Dimensions
ln Hg Abs
ln HrO
dimensronless
cf
,n'
tn'
Root ln H2O
Rool In HzO
Rool ln HrO
Crms
Mlnutes
Drmensronless
lnchcs
Perccnl
Perccnl
PercenL
dscf
scf
Fracllon
Fracton
lb/lbmol
lb/lbmol
Percent
mrcroporse
dscfm
Drmensronlss
mlcrons
mtcrons
I)rmensronless
mtcrons
DimeNronless
I
Sq Fl
ln HrO
In Hg Abs
ln HB Abs
dsc[m
c[n)
fp-
mrlliBrms
mrllgrm
mrlIgrms
8r / dscf
gr / dscf
gr / dscf
lb/hr
lb/hr
lb/hr
Run#[ Run#2'7/t0t24 7il0t24487 488
8:45 10:26
24.10 24.10
0 350 0.3900.994 0.99424.288 26 272
87.5 95.3
17 00 17.00
t698.2 t698.2
0.0100 0.0 r00
0 5685 0 s598
0 5628 0 ss42
0 5628 0.5542
474 544
59.00 60.25
0 769 0 773
0.2r60 02r80
4.20 4.20
14.80 14.50
8l .00 81 30
18.773 20.024
2.235 2 566
0 106 0.1 t4
0 894 0.886
29.26 29.25
28.07 27 97
r 03.9 r08 7
218 3 2t8.6
0.3 18 0 3320.608 0.6452241.6 2349.5l.106 l.106
10 28 9.89
2.s0 2 35t.106 r.l 13
2.50 2.34
r.000 0.997
2648 269 6
l 1.793 fi.793
-0.270 -0 270
24.05 24.05
24.030 24 030
1.42E+04 1.39E+04
2.718+04 2.70E+04
2.30E+03 2.298+03
Run #3
7/t0/24
489
l2:10
l3: l4
24.t0
0.400
0.994
26 642
99.9
17 00
t698.2
0.0 100
0.5s48
0.5492
0.5492
s0.3
60.00
0 769
0.21 60
4.00
14.90
81.10
20.139
2.372
0.r05
0.895
29.24
28.05
tt22
218.4
0.336
0.641
2359.2
r.106
9.91
2.35
1,n2
234
0 997
AVG
264.8 266.4
I L793
-0 270
24.05
24.030
1.39E+04 1.40E+04
2658+04 2.698+04
2258+03 2.28E+03
6.0
2.5
23.0
0.0046
0.0019
0 0r76
0.546
0.228
2.093
Date
Time Tesl Begm
Trme Test Ended
Meler B&ometflc Pr6sure
Orifice Pr6sure Drop
Met€r Calbraton Y [&1or
Volume C6 Smpled--Meter Condrlions
Atg Meler'Iemperalure
Are Area Blocked bv Smple Tran
Stack Cross S4nona.l Area
Probe BlochSe Factor for PM2 5
Sq Root Velocrty Pr6sure Corected [o, bf
Sq Rool Velocily Head ( 6 m6ured)
Sq Rool Veloci& Had (ad, lor blocka8e tlnecss6.)
Weighl Waler Collecled
Duraton ofTesl
Pilot Tube Coeflicrenl
Nozle Dreeter
Volume o/o Cdbon Diorde
Volume 7o Oxy8en
Volume 70 Nrtrogm ed Cubon Mono\ide
Volume G6 Smpled (Standild)
volume Water Vapor
Frelion H2O rn Srli C6
Fr&lion of f)N G6
Molcculd Wl Dry G6
Moleculd Wl Slack Gd
Percenl lsohnetic
06 stred viscosrty
Dry Cs Smple Rate
Samplmg Rate
Rcynolds Numb.r
CMmghm Cordtion Facror rg PM2.5
PM l0 Cul Pornl
PM2.5 Cut Potnr. Condrtion Built In
Re-6nmaled Cmrnghm Correction Faclor
PM2.5 Cut Pornt. Conditron Burlt ln
Rarioof Dso/D50-l (0.99S2S l.0l)
Avg Stek Temperalure
Stack Cross S@tonal Area
Shck Static Prssure
Smple Pod Buomelric Preslure
Stack Pressurc
SI&k C6 Volumelnc Flor\ Rare (Std) M6ured
Skl C6 Volumetnc Flow Rate (Actual) Mesured
Vel@rty of Srk C6 M6ured
M6s of PM 10.0 Pdiculate
M6s of >PMl0 0 PMiculalc
MN of Conde6ibles
Concfilrauon of PM l0 O PMicullte
Concenranon of>PMl0 0 Pdiculare
Concentrabon of Condensibl6
Emrssion Rde of PM l0 0 Pffrculare
Emission Rale of >PM I0l) Pfirculate
Emrssron Rate of Condensibl6
0.0058 0 0080
0.0037 0 0030
0.0238 0.0167
0.709 0.9ss0.450 0 3s82.897 1.993
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4.5
29.0
10.4
3.9
zt.7
0.0061
0.0029
0.0194
0.7368
0.3451
2.3277
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%t=
A, '=
ASAP .
BtLr '
B,,, =
C.p,, =
C.n,. =
Co: =
Cn=
Lptrtto -
D",,
AH .-
At-l@
Al-16 =
D,, =
AP -.
DP;o =
D.=
EA=
Ef"p,,, =
Efr,r. '-
Li11,,,,,,111u =
ERt'r'' rn =
EI{\ -
L=
rnBtu =
M.u,,d =
M.,,rt =
Ma --
nilnBtu -
M,lrro =
Mr=
Irs =
Method 201A I 202 Nomenclature
percent isokinetic
stack cross-sectional area (11i)
See lAP
Lrnit heat value (British thennal unit)
fl'action of water in stack gas
concentration of condensibles (grain/dscll
concentration of coarse particu late ( gr/dscl)
perce,rt carbon dioxide in the stack gas
pitot tLrbe coefficient (0.84)
concentration of PM r0 particulate (grldsct)
equivalent stack diarneter (inches)
orillce pressure drop (inclres H2O)
oriflce pressure (inches H,O)
orifice prcssure head (inches ll,O) needed fbr cyclone llorv late
nozzle d iameter ( inches)
stack flow pressure ditferential (inches HrO)
50% effective cr-rtoff diarneter of particle ([r)
clianreter of thc stack (f-eet)
percent excess air
emission rate of condensibles (lb/hr)
ernission rate of coarse particulatc (lb/hr)
emission rate per mnlBtll or tt-rn of fuel ctc.
emission rate of PM 1s particulate (lb/hr)
emission rate of compound which replaces x
length of rectangular stack (inches)
thousand BtLr
mass of condensibles (rn i I ligrarns)
mass of coarse particulate (rnilliglarns)
molecular weight o1'stack gas. dry basis (lb/lb-rnol)
million BtLr
rrass of PM,6 parlicLrlate (rnilligrarns)
molecular weight of stack gas. wet basis (lb/lb-nrol)
gas viscosity (rnicropoise)
M,,s,,, .-- rllolecular weight of gas specics (lb/lb-rnol)
N, : percent nitrogen in the stack gas
O, = pcrcent oxygen in tlre stack gas
r/Ap = average of the square roots of AP (rnay also be referred to as ASAP)
.i4fr, - square root olAP at point I of the current test. Method 20 lA
r/Af ,' .. square root of AP at point I of the previous traverse, Methocl 20 lA
VAP'.'" = averoge of the square roots o1'AP tiorn the previous traverse. Method 20 lA
Pbn, = absolute barometric pressure at the dly gas meter (inches Hg)
Pb, = absolute barometric pressure at the sample location (inches Hg)
P,' = stack static pressure (inches HlO)
P. = absolute stack pressure (inches Hg)
P,,., = absolute pressure at standard condilions (29.92 inches Hg.)
pts : number of traverse points during tlre test (minirnum of 6, maximurn of l2)
e = time of test (minutes)
I
I Method 20lA 1202 Nomenclature
I 0, : sample time (duration in minutes) at first sample point for Method 20lA
I t = :::ii*;:lnxi:lilffi [a#i;-''"
p'irr"n"ror Me'1h'd 20rA
Q,. : actual gas flow rate through the cyclone (acfrn)
I Q..' : predicted actual gas flow rate through tlre cyclone (acfm)I Q* : wet stack gas std. volumetric flow 1ftr/min, wscfm)
I [::: : Hi::iH[:l:
T,,, : Ineter temPerature ("F;
I ,: r;ffii:ffi;:[i,:lstandardconditionsls2s,,R;
Tt = seeO
I Vm = sample volume (ftr) at meter conditions
I Vln,,6 : volume standard (dscO, sample volune adjusted to 68"F and29.92 inches tlg.
V,u,, : maximum allowed nozzle velocity (fps)
I vi,,i" : minimum allowed nozzlevelocity (fps)
y'n = target noz.z.le velocity (fps)
I J; : lllli"S;ff:ffi:lT,T],68,,F and 2e e2 inches Hg
W : width of rectangular stack (inches)
I
*l: : ff:?[:"]h";::""0
water corrected (grams)
Y : meter calibration Y-factor (dimensionless)
T
T
T
I
T
I
t
T
T
T
T
I
o/ol
A.
B,o,
C.0,,
C"o*
Cprl o
D.u
AHa
DPtu
AP,u.
APn'in
EA
Er.p,,
Er.u^
ERn,u,t),,,
ERp*u
M,t
M.
lrs
P,
0l
Q,
0,,
Q,
Q*.
Qr.'
Q*
R.ot
R,i,
Vn,o"
V,niu
Vl11rrd
X,l
Method 20lA 1202 Sample Equations
: vln.rd . (T, + 460) . 1039 / (e . v". P.. X6 . D,,2)
= lDsr I 4). n
: Y*l(Vrn",o+V*): M"n,n . 0.01543 / Vmr,6
-- M.o.* . 0.01543 / Vmr,6: Mpuro . 0.01543 / Vm.,6
= 2.L.W/(L+W)
= [Q,.'. Xo. P,i (T,+460)]r. [(T,, +460).Md. 1.083.aH,,,j/ Pb,,,]
- 0. I5625 . [(T. + 460) / (M, . p,)]o'uo' . (p, / e,.)"'0"': 1.36g6. l0-4. p, - M, - V,uu*2 / [(T,+460). C,,2]
: 1.3686. l0-4. p,. M,. Vn,in2 / [(T"+ 460). Cp2]
= (%% - 0.s %co) t10.264 %N2 - (%or - 0.s %co)l: c.pn, . Q.. 0.00857
- C.,r,, . Q..0.00857: ER / (mrnBtu / hr)
= CpNrro . Q.. 0.00857: co: .0.44 + 02 . 0.32 + N: .0.28
= (Mo.Xu)+(18.8,,)
T
T
t
t
I
I [51.05+0.207.(T.+460)+3.24.10't.(T,+460):+0.53t47.o/o}1-74.143.8*.].t0-,'
Pbe+(Pc 113.6)
I : 1r/ne,'/ !ap',u"). (0,"., / pts)
= V..A,
- or . r/aP,, / r/AP,: Qn . X,r . P,. T.ra / [(T. + 460) . Psrd]: [('t, + 460). P",6 / (T,,a . P,)] . [(Vmu.r + V*) / 0]: F, . 0.002837 . [(T, +460) / (M, . P,)]0 "0": Q,/X.r
= 0.4457 + ![0.5690 + (0.2603 . Je,.' . t4 / v,r s)]
: 0.2457 + i[0.3072 - (0.2603 . iQ,.' . ]r, / Vu' ')l: V, ' R,.u*
: Vn' Rn,in: Vm. Y. T.ta. (Pb,n +AH/ 13.6)/ [Pua. (T,, +,160)]
: 3.056 . qr.'/ Dnl: 8-s.49. 60. Cp../Ap. {11t. +460)/(p,. M.)l: Wt*..0.04715: I -B*.
T
I
I
t
I
I
t
T
I
I
T APPENDI* B
I Preliminary Velocity Traverse and Sampling Point Location Data
I
Particulate Field Data Sheets
T
I
T
t
I
T
I
T
T
I
I
I
T
TB
t
N
B
Stack Dia.
Ports are
Ports are
.1(r.5 Reference: 6
35',Upstream from next disturbance
Downstream from last disturbance45',
Preliminary calculated
Comments:
Averages:
T, Lt"o ZFlow ' ri I
AP
KEY:>
r/ap
Ts ZFlow
AP
Stack ldentification Kiln #3 Baghouse
Date .' .' r.1 r .'-.\
Barometric Pressure
Static Pressure (P6) - . L;* in H2O
Estimated Moisture (Bw.) 12 o/o
Sample Height from Ground 50 feet
Traverse
Point
Percent
Diameter
Distance From:Ports
ID Reference A B C D E F
4.4 2.05 8.05 a',,f,3 j.)
1L 14.6 6.71)12.79 ,y1"Y1
-)29.6 13.76 19.76
4 70.4 i2.74 38.74
5 85.4 3().71 ,t5.71 -.^ :, ,.Jr
6 95.6 11.45 50.45 L;t' ,'5 .
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Sarnple Recovery
Particulate Analysis
Condensible Particulate Matter Analysis
Gas Analysis Data (ORSAT)
Chain of Custody
APPENDIX C
C
Facilitr: IJtclitc
Stack ldcntiljcation: Kiln # I
Datc:
Mcthocl:l() lAi 202
IIIPINGIIRS
l'iltcr Nunrbcr:
Final rg)
Initial ts)
Nct (s)
-un-lLXerdcserptiur
i<
l)urgc start
Purgc cnd i.
ml I1"0 atldcd r ..
Sanrplc llox
I n il ials
I lexanc
liquid (l I,O) ir irrpingcrs. (rnl)
T
T
t
I
T
I
T
T
T
I
I
I
t
I
t
I
T
T
T
IMPINCjIB.S
lrihcr Nurnbcr:
Irinal 1g1
lnitial 1g1
Nct (gr
*#suaelelluau
Purucstan i,:'-----s-
l'urgc cnd
nrl l l,0 addcd r ,
Run: l--
'fotrl t*,___ J '.' . 'i
RINSES tlro Acetonc
Sanrplc Box: D
I ni(ia ls
(hl,()1 in rnrpingcrs, (ntl)
' .i )L .r-t
5t .-t,
ir .l
IMTTNCERS
Filtcr Nunrbcr:
Iz ' .-.
Finallc)
Initial (gt
Nct (g)
prn-fiXeldexriptiop
l)urgcstart ''" '
I'urgeend ,.- l-:,i
nrl H,0 addcd 'l:..
Run: t
Total 1gy
Sanrplc Box:
I nitials
lnitial Volurnc of liquid (l{:O) irr
RINSES H2O tcctone I lexane
t
T
T
T
T
t
T
T
I
I
t
T
I
T
I
T
I
I
lfacility:
Stack Idcnti llcatiorr :
lriltcr Nunrhcr:
LJrel ite I)ate : 1ll0l20?-4
[{un:
Sarrrplc 13or:
Kiln #3
Illanks &
Rinses
Filter
PM,,, Wash
> PlvIro
Wash
I
( omnrcnts:
487
Acctonc lllank Corrcction 0.(X)(XX) gi l(X)ml Rinse Vol. []iltcr & l)lvl r()
'I'M,.,
I,Mr, 7.1 ntg
't'V,,, '1.5 nrg
Total I 1.6 mg
l) I llc,c shilll l)c nt lcasi b hrs bctuccrr rrcri:hrngs
l-ab "[cchnician: Mikc McNanrara
l.ab 'lechnicran: [)can Kitchcn
( l(l l l lili\
io
ntl
nr!
l:inal ,:
Irinal":0. r 202
[)irrul,r1,.;: 0.1203 g
l)rcrvcight: 0. I 155 g
Net 0.0048 g
Net ,{.8 mg
60.8932
19.9407
0. r 203 ()
5
t,
0.(n2l _q
60.893 r Iinaloyu: (r0.t1932 g
lnitialny6: 60.1t909 g
DaLc: 7l16l?021 l'inre :
Dur.,l7lr,nd2.l I inrc:
DaLc: 7ll(t12024 'l irttc: 8:00
D.r.",7iTM Iin,.,llJxt-
Date: 61712024 'l inrc:Dut.,?frilIEf tirrc:
l)ate: i 11612021 'l'irnc: tl:tX)
Datc:7lEilff I in'., -il,rttr
PM ( lnftrrnration ()nly )
l:inul^u,,: .19.9409 g
lnitial,rr,,;: +,f .rXra g
(iloss: 0.00,15 g
t3lanli: 0.0(X)0 g
Ncr __0.00a1_ 9
Net ,1.5 mg
Irinal,:
lrinalz:
Initial,:
lnitial.:
I:'inul,:
I;ina l.:
lnitiall:
I n itial,:
(r0.Iil909
(lloss:
Blank:
Nct
Net
60.tt90tl
0.0023 s
0.0000 g
2.3 mg
Ileakcr Nunrbcr:
49.9,1 l0
,19.9364
49.9363
Ilcakcl Nunrbcr:
BESUTIS I'M"r
lrilrcr (M | ) 4.8 mg
I)M1,, Wash tV.i 2.3 mg
Total_LL_ mg
( ritcria | ) \!crglrts ilrc | 0 5 rtrg ofcach other. or within l'!o ol thc nel \\ught
l)aLc: 1 I l5/21
Dlrtc: _ 7/16/24
40
-l( )
3.9
tt0
I
T
T
T
T
I
T
t
I
Facilirr,: [Jtelite Date: I1l,012024
flun: 2
Sanrplc []ox: t)
Stack Idcntilication:
Iriltcr Numhcr:
Kiln #3
488
Acctonc [Jlank Corrcction 0.(X)000 g/l00rnl Rinse Vol. Irilter & I)M,,,
:, pl\yl lr
ml
rnl
Blanks &
Rinses
Filter
t
c'onr1.rcr)ts:
(lR I l trltlr\
PM11y Wash I'inal,:
Ijinal.:
lnitial ,:
I n itia l.:
[]cakcl Nunrbcr:
'PM,n lrirral,:
Wash lrinal":
Initial,:
lnitiall:
Bcakcl Nr-rrnber:
6 | .9033
62.t971
0.r 194
0.1 194 e
b
c
g
I:inal,:
l'inal,:
Finalqy6: 0.1 194 g
Prcwcight: 0.1 144 g
Net 0.0050 g
Net 5.0 mg
lrinalny,l: 61 .90tt8 g
lnitialnr,',-?]EI-g
Cross: 0.005.1 I
tllank: 0.0000 g
Nct 0.0054 g:
Net
lrinalnu,,: 62.1971 S
Initial,ry,;: CrZ.trl:Z g
D.nrc: 711612024',Iirrrc:D,",1iTffif, rirnc:
l)atc 7 16,2024 I inrc: tJ:00
I)"t.,lrGDI]r Ii,r,c' ll:(x)
Dlttc: 61712024 -[ inrt:
Date: 7ll6l?(t24t-ti.",1iiffi
Dittc: 61712024
I)ot",?llDEf
PM (lnlirrmation Onlyl
PMr,, I().4 mt
.1,M,,, li.9 rrtg
'l'otal_LL1__ mg
t)ate: 7/l-512-l
l)atc: 7ll6121
6 L90ti9
61.9086
6 t .9034
62.1971
62.1932
(r2.193 I
Cross:
g lllank:
g Nct
Nel
Plvt r,)
0.0039 g
0.0000 g
0.0039 g
8l
I RESutrs
T
tiiltcr (M r )
PMr, Wrsh (Mr)
Total
5.0 mg
---11- nrg
----l!'4- *e
(-lt(eiln tlWcrglilinrc to5rnAol cachotlrcr.or r!rlhrr l9"of lhcnttwerght l) lherc5hnlltrcatlcail 6lrfst)el$ecrrrvctultrtrcs
Lah'lcchnician: MikcMcNamaraI
I
T
I
T
I
T
I-ab Icohnician. Dearr Kitchen
I Faciliry: Utelite I )ate:1il(\12024
Stack Idcnti lication:
l:iltcr Nurnbcr:
Kiln #3 I{ trn:
Sarnplc []ox:I 489
Blanks &
R.inses
Filter
Acctonc lJlank Corrcction 0.00(X)0 gi l00ml Rinse Vol. I:iltcr & PM,,,
> I)N1 1,1
l0 rnl
nrlI30
( l{l I i:ltlr\
l:inal,
I:irral.
0 t 1.59 g [--inaln1,r,: 0.I 159 g
l'rewciqht: 0. I 153 gt0.1 I 59
Nct 0.0006 u
Net 0.6 mgtPM,u Wash l'inal1:
Ii nal.:
Initial,:
In it ial.:
62.87 r5
g
ltinal,.r,,,: 62.ti715 g
Initial.ru,,: 62.ti66 I g
(iross: 0.(X)54 g
Blank: 0.0000 g
l)trrr::7/16l?024 l-inrt:: 8:0()
62.87 t5 Drrt"'.7lGili
T (r2.ll(16 I l)atc: 6t712024 '[ ir]lc
t)ut.,7,rlTD6il Iirnc62.8(160 Ncl 0.00i4 r
I Net 5.4 mg
Beakcr Nr.rntbcr:82
r PM,u
Wash
l:inal1:
l" ina l-:
Initial, :
ln itial":
60.6705 <t
s
liinalnyl;: 60.6705 g
Initialnu,,: 60.6680 -0.
Datc:7116120?1
ltrrtr,liitfizl
l'irne : t{:00
T
60.6705
(iross:
lllank:
Nct
Net
PM r,
0.6
0.0025 c
60.66'79 0.0000 g
().0()25 g
I)atc
l)atc
61712O24 I irnc:
6ln/2(lA 'l'inrc:t 60.6680
2.-5 rng
T
Bcaker Nuntbcr:
RESUTTS I'}lVl (lntirrnration Orrll )
t;illcr(Mr)
I)M,,, Wash (M1)
'I'otal
r11g
r1'lg
mg
l'lvl ,,,
,,M,,,
(i.0 nlg
T
5.1 2.5 lng
6.0 Totnl ll.5 mg
ll I lterc slrall I)cxt iur!t () hrs hctrvccn wcrrhlrlr( ortrrncnts:
T
T
l.ah'l'cchnicinn: Mikc: McNarnara l)atc: 7/l 5i2021
I)atc: 711612024[.ab'l'cchnician: [)ean Kitc,hcn
T
T
I
I
T
I
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\
(,
oEFoo
+'
o*(
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E=Td.
t)E't
:U(€
oo
a.
l
6t
=a.
l€r-
iN(\\o
=!
-
c.
l
\o
{'cl00F
tota.{=\o
-d
'6l
.a\o
=l00F-
c.
lcl
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Figure 1. Facility Schematic Representation
Raw Production and Control Equipment Data
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UTELITE DAILY KILN REPORT KILN 1
5:00 PM
6:00 PM
5:00 AM
4
END OF
END OF
DAY SHIFT TONNAGE
NIGHT SHIFT TONNAGE
FEED
TANK
RATE
TPH BH DP
GA5
SETTI NG
BH
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ID FAN
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KILN OPERATION KILN 1 (3 4 (circle one)
DAY SHIFT: Thurs thru Tues: (12 hr shifts)
Burner: t' ,',,,i{-,'
7am to 7pm; Wed: (6 hr shifts) 7am-Ipm & 1pm to 7pm
Utilitv Hand:
Gas on:Gas off:Reason:Aft:nf -.
KILN OPERATION
Gas on:Gas off:Reason:
Gas on:Gas off:Reason:
Feed in:Feed out:
Feed in:Feed out:
TANKS:
Silver 0 1-.t-jt;0,'1"
Orange 0 r I 0.+"{f' . -..)
Rusty
Coarse
Problems, Concerns or Events:
NIGHT SHIFT Thurs thru Tues: (12hr shifts) 7pm to 7am: Wed: (6 hr shifts) 7 pm-1am & lam to 7am
11 ,,Utility Hand: i
Gas on:Gas off:Reason:
Gas on:Gas off:Reason:
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i'. i?11 - {, r
TANKS 5'.* ";r,t4
Silver
Orange
Rusty
Coarse
Problems, Concerns or Events
Bin Vent:
I
I APPENDIX E
I Calibration of the console dry gas meter(s). pitot tubes. nozzles diameters. and temperature
sensors were carried out in accordance with the procedures outlined in the Quality Assurance
I Handbook. The appropriate calibration data are presented in the fbllowing pages. -fhe nozzler calibrations are recorded on the first page of the field data sheets.
t Figure 2 Schematic of Method 201A1202 Sampling Train
I [:Tl"i;i1;*'.J,:t?Ah,il:,:"1'Jl?l?:'i:'''Type S Pitot Tube lnspection Data
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Annual Balance Calibration Check
Dale 1123124
Denver lnstruments, ModelA-250, SN 8045284Balance
Weights Used Troemner Weight Set,
sN 98-115146
Technician
Certified Weight
orams
Measured Weight
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Difference
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0.1 000 0.1 000 0.0000
0.5000 0.5000 0.0000
1.0000 1.0000 0.0000
10.0000 10.0000 0.0000
50.0000 50.0001 -0.0001
100.0000 100.0000 0.0000
120.0000 '120.0001 -0.0001
150.0000 150.0000 0.0000
Michael McNamara
t
T APPENDIX F
I The testing protocol and other correspondence related to the tests are included here.
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B4acc C. Bitd
Diwator
June 28, 2024 DAQC-636-24
Site ID 10676 (84)
Dave Vernon
Holcim Utelite Plant
P.O. Box 387
Coalville, Utah 84017
DearMr. Vernon:
Re: Holcim SWR,luc. Utelite Plant *Kilns #l and #3 * Protocol Review and Test Date
Con{irmation * Summit Couaty
The testing protocol for the Holcim Kilns #l and #3 received June 6, 2024, has been reviewed and
found acceptable. The agreedupon test &te is the week of Juty 8,2024.
Acceptance of a protocol does not rclieve the owner/operator and the testing contrdctor from strict
adherence to all applicable EPA nnethods, Utah Division of Air Quality (DAQ) policies, Utah Air
Quality Rules (UAQR), and methods approved by the director. Any dcviation from EPA mcthods,
DAQ policies, UAQR, and methods approved by the director must be addressed separately and
express written consent given prior to commencement of testing.
The DAQ requires that all test re,ports include a statement signed by a responsible official
ce.rtifying &at:
A. Tcsting was conductcd white the source was opcmting at thc ran and/or conditions
specified in the appticable approval order, operating permig or federal regulation.
B. During testing, &e source combusted fuels, used raw matsrials, and maintained
process conditions reprcsentative of normal operations, and operated under such
other relevant conditions specified by the director.
C. Based on information and belief formed after reasonable inquiry, the statements
and information contained in the report are true, accurate, and complete.
195 Nor& l9i0 W;rr. S* Lrl$ City, UTllriling Addrcss: P.O. Box 144820, Sah Lr&c City, UT g4l l4,lg20
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COMPLIANCE PMIO EMISSION TESTING PROTOCOL
HOLCIM UTELITE, COALVILLE UTAH
KILN #I AND KILN #3
PRO.IECT ORGANTZATION AND RESPONSIBILITY
'fhc lbllowing personnel are presently anticipated to be involved in the testing prourarn. I'he
Utah l)ivision of n ir Quality (UDAQ) and EPA may have their own pcrsonnel to obscrve all
phases irrcluding the process.
Company
I-lolcinr IJtel ite Plant
P.0. Box 387
Cloalville. Utah 84017
TETCO
391 East 620 South
American Fork. tjtah 84003
Contacts
Dave Vcrnon
Alex Judd
(80 r ) 467-2800
(80 r ) 167-2800T
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Dean Kitchen 801-492-9106
During these tests only Holcirn personnel listed above or assigned personnel liorl the operating
department are authorized to answer or obtain answers to pertinent questions on the process
coiiditions or the test protocol.
PROJECT DESCRIPTION AND METHODS-APPLIED
l'he sources to be tested are the baghousc exhausts of Kiln # I and Kiln #3. at the I lolcirl lacility
krcated south of'Wanship, Utah. This test will be conducted to demorrstrate cornpliancc wil.h the
tacility's -l'itle V Operating Perrnit number.1300001004. Testing procedures will include
accurnulating process and production data as well as lesting lbr [,N4ro emissior-ts using LPA
Method 201A. Condcnsable particulate rnatter (CPM) will be measured accordirrg to Ill)A
Method 202 and is rrot for compliancc. but infbrmational purposcs only. Tcsting rvill consist ol
three test runs.
TEST SCHEDULE
It is planned to complete all testing the week of July 8,2021. 'fhe testing crew will arrivc and
set up and starl testing on July 9tl'and continue until all testing has been conrpletecl.
A pretest nieeting can be scheduled if reqLrested by Holcim or DAQ.
TEST PROCEDURES
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1.
5.
6.
7.
8.
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Three test runs rvill be conducted on each kiln I
Methods 201 A and 202 as specitied in 40 CFR
EPA Methods20lAl202.
for PMro emissions. Testing will tbllow EPA
5l Appendix M.
The following specific items rvill be followed for Methods 201A1202:
| . The Kiln # I stack inside diameter is 47 inches. There are two ports available lor testing
that rneet the upstream/downstream requirements of Method l. 'fhe ports are located 45
f'eet downstream and 33 feet upstream from any flow disturbance. A total of l2 points
will be sampled, six per port. Minimum target sampling tinre will be 60 minutes. The
stack flow will determine the dwell time at each point and actual test tirne.
The Kiln 3 stack inside diameter is 46.5 inches. There are two ports availahle that meet
the upstrearn/downstream requirernents of Method l. 'fhe porls arc located 45 l-eet
downstreamand35feetupstreamfromanyflowdisturbance. Atotal of l2poiritsrvill be
sampled, six per port. Minimum target sarnpling time will be 60 minutes. 'fhe stack flow
will deterrnirre the dwell time at each point and actual test
EPA Method 2 will be used to determine gas stream velocity. Calibration data fbr the
type "S" pitot tubes are included with this protocol. Dual inclined/vertical manometcrs
with graduations in 0.01 inches of water will be used. 'fhe absence ol'cyclonic florv lvill
be checked during the preliminary run.
A barometer will be used to measure the barometric pressure. lt is poriodically checkecl
against a mercury barometer. Prior to testing it will be checked to assure an accurate
barometric pressure.
An integrated sample of the flue gas will be taken fionr the exhaust line after the dr,"- gas
rneter orifice during each test run and analyzed at the test's completion by Fyrite to
determine the gas stream molecular weight.
1'he probe liners will be borosilicate glass or Teflon.
Preparation and clean-up by the contractor will be performed in the contractor's testing
trailer. Laboratory work and analysis will be done by the testing contractor as soon as
possibleafterall testshavebeencompletedat39l East620South.AmcricanFork.tJtalr.
Back half will be determined by EPA Method202. EPA Method202 analysis will be
followed as in the method.
If plant maintenance or operating problerns arise during the test. the test may be stopped.
This determination will be made by the Holcim Corporation representatives or operating
personnel in consultation with agency representatives
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9. Current calibration data is submitted in Appendix B of this protocol. Any equipment
calibration that fall past due prior to the test date will be recalibrated prior to use.
OPBRATIONAL DATA AND INSTRUMENTATION
Pertinent operating data will be made available by Holcirn upon request by agency personnel.
TE,ST AREA
The test area shall include the control room, stack and associated areas, and the area around the
contractor's testing trailer for preparation. and clean-up.
TEST SITE
A sketclr of the source is included with this protocol.
ACCESS TO SAMPLE SITE
The site is accessed via stairs and ladders.
POTENTIAL HAZARDS
Moving Equiprnent Yes
['lot Equiprnent Yes
Chemical No
Other No
ESTIMATES OF TESTING PARAMETERS
The volumetric flow rate. moisture and stack ternperatures are sinrilar for both stacks.
Volumetric Flow Rate 12,000 dcfnrMoisture l1%Temperature 325'F
OUALITY ASSURANCE
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All testing and analysis in these cornpliance tests will be conducted according to Methods 201 A
and202 and appropriate sections of the EPA Qualitlt A.t,rurunce Hantlltook./itr,lir Pollutiorr
Measurement Syslem.s Volume III.
REPORTING
The emissions test report will be prepared by the testing contractor according to EPA Quality
Assurance Guidelines. The contractor will furnish several copies of the test repoft to Holcim.
This report will be submitted within 30 days following the cornpletion o1'the tests.
EPA Method 202 will be included in the written repoft for informational purposes only.
Complete copies of raw data. calculations and summary of test will be included in reports. All
process and production data will be recorded and retained for inspection and copying by DAQ
and EPA.
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Appendix A
I Facility Schematics
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Type S Pitot Tube Inspection Data
Pitot -I'ubc ldenrillcation:
l'echn ician M. McNamara
D,= 0.-175 in. Is ['1 = Pe ?
Is 1.05.D, S P^&Pr1 S 150.D, 'l
Yes
Yes
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[ -trffi l- .. \, > r inchcs y = .] r/2 in
I'he pitot tubc nrcets the specilicalions lirr a calibration laclor ol'0.114? Ycs
'l r:mpcraturr; Scnsor Cal ibrationRel'erence: C)mega CL.l5 l2A
llmt Check 2:llt
BOIL WA'TER
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Tyrre S Pitot Tube Inspcction Data
l)itot fube Identillcation:5tc-2
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'Ihc pitot tubc rnccts the spccifications tbr a calibration factor ol'0.8.1? Yes
l'omporaturc Scnsor Cal ibrationIlelbrence: Omega Cl.35l2A
Continuiw Check
l lcat Chock 248
I('E WATER
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Sample Box Temperature Sensor Calibration
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t>arc I 12/24 ('alibraror Xuan N. Dang Rclbrcncc OrncgaCl,35l2A
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Location
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'femperature 'fcmperatu re
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Reference
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Scnsor
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A Oven (3)Waler 33 33 0
Watcr 203 20r a
Oven (4)water 3i 33
Water 203 20t 1
B
Oven (3)Water 33 33 0
Watcr 203 202 .l
Oven (4)waler -i -1 0
Watcr 203 20t _)
C
Ovcn (3)Waler J-1 0
Watcr 203 20 0
Ovcn (4)walcr 33 33
Watcr 203 203 0
D
Ovun (3)Water .,J J-)0
Watcr 20:l 203 0
Ovcn (4)watcr i3 -).)
Watcr 20:i 203 0
E
Oven (-j)Watcr ., 1 33 0
Watcr 203 203 0
Oven (4)water -) -l 33 0
Water 203 203 0
F Oven Water 33 33
Watcr 203 202 -I
G Oven Water 33 33 0
Water 203 ?02 -l
H Ovcn Water 33 33 0
Water 203 203 0
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lmpinger Out (i
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Annual Balance Calibration Check
Dale 1123124
Denver lnstruments, Model4-250, SN 8045284
Troemner Weight Set,
sN 98-'115146
I Technician Michaet McNamara
Certified Weight
qrams
Measured Weight
qrams
Difference
qrams
0.1 000 0.1 000 0.0000
0.5000 0.5000 0.0000
1.0000 1.0000 0.0000
10.0000 10.0000 0.0000
50.0000 50.0001 -0.0001
100.0000 100.0000 0.0000
120.0000 120.000'1 -0.0001
150.0000 150.0000 0.0000
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Source Information
Division of Air Quality
Compliance Demonstration
Referance Method 201 & 201A for PM10
Source Information
Company Name Holcim Utelite
Company Contact:Carsten Mortensen
Contact Phone No.801-467-2800
Stack Designation:Kiln #1
Test & Review Dates
Test Date: 7/10-11/24
Review Date: 9/23/2024
Observer: Robert Sirrine
Reviewer:Robert Sirrine
Particulate Emission Limits
lbs/MMBTU lbs/hr gr/dscf
0.000 3.340 0.024
Front Half Emission Rates
lbs/MMBTU lbs/hr gr/dscf
0.59 0.006
Total (Front & Back Half) Emission Rates
lbs/MMBTU lbs/hr gr/dscf
0.762335345 0.007462594
Test Information
Stack I.D. inches As ft^2 Y Dl H @ Cp Pbar Pq (static)Dn
Target
Time
47.00 12.048 0.9940 1.607 0.773 24.1 -0.22 0.235 60
Contractor Information
Contracting Company: TETCO
Contact: Dean Kitchen
Phone No.: 801-768-0973
Project No.:
Circular
10100
9780
9860
9190
8710
8710
8710
10540
10640
11950
320
10610
10200
10390
1970
1800
1910
1420
1040
1190
1250
F factor usedF factors for Coal, Oil, and Gas
Anthrocite 2
Lignite
Natural
Propane
Butane
COAL
OIL
GAS
Bituminous 2
Fd Fw Fc
scf/MMBtu scf/MMBtu scf/MMBtu
O2
CO2
lbs/MMBtu
Page 1
Summary
Division of Air Quality
Reference Methods 201 & 201A - TSP
Compliance Demonstration of
Holcim Utelite - Kiln #1
Testing Results Lab Data - grams collected
Test Date 7/10-11/24 7/10-11/24 7/10-11/24 7/10-11/24 Lab Data Cyclone Catch Filter Back
Run 1 Run 2 Run 3 Run 4 Run 1 0.0028 0.004900 0.00200
As ft^2 12.05 12.05 12.05 12.05 Run 2 0.0022 0.004200 0.00220
Pbar 24.10 24.10 24.10 24.10 Run 3 0.0069 0.000000 0.0021
Pq (static)-0.22 -0.22 -0.22 -0.22 Run 4
Ps 24.08 24.08 24.08 24.08
Avg. Ts F 288.20 293.60 296.00 Holcim Utelite Kiln #1
CO2 - FCO2 6.70 6.50 6.50 0.00 Front Half Emissions Summary
O2 13.20 13.10 12.80 0.00 Run 1 Run 2 Run 3 Run 4 Avg.
N2+C 80.10 80.40 80.70 100.00 gr./dscf 0.00622 0.00549 0.00551 0.00574
Md 29.60 29.56 29.55 28.00 lbs/hr 0.636 0.562 0.558 0.58533
Mw 28.03 27.92 27.92 lbs/MMbtu
Y 0.9940 0.9940 0.9940 0.9940
Cp 0.77 0.77 0.77 0.77 Particulate Emission Limits Front Half Emission Rates
Vm cf 25.264 23.277 25.426 0.000 lbs/MMBTU lbs/hr gr/dscf lbs/MMBTU lbs/hr gr/dscf
Vlc 63.700 63.600 67.800 0.000 3.340 0.024 0.59 0.005736922
AVG. Tm F 99.00 87.04 96.41
Vm cf 25.264 23.277 25.426 0 Holcim Utelite Kiln #1
Vm std 19.119 18.000 19.331 #VALUE!Total Emissions Summary w/back half condensable
Vw std 3.000 2.990 3.190 Run 1 Run 2 Run 3 Run 4 Avg.
Bws 13.50% 14.20% 14.10% #VALUE! gr./dscf 0.00783 0.0074 0.0072 0.0075
S Bws 99.90% 99.90% 99.90% #VALUE! lbs/hr 0.8024 0.7560 0.7286 0.7623
Avg. Sqrt Dlp 0.48 0.49 0.48 0.50 lbs/MMbtu
Vs 33.661 34.198 33.888
scfm wet 13820.29 13940.05 13769.73 #VALUE!Particulate Emission Limits Total Emission Rates
acfm 24333.53 24721.54 24497.26 lbs/MMBTU lbs/hr gr/dscf lbs/MMBTU lbs/hr gr/dscf
Qsd dscfh 717273 717634 709692 3.340 0.024 0.762335345 0.007462594
Qs ft3/min 0.646521 0.650992 0.653159 #VALUE!
% Isokinetic 106.18 104.23 107.17 Test Quality Parameters
Viscostiy 221.07 221.87 222.40 Run 1 Run 2 Run 3 Run 4
D50 9.99 9.99 9.99
Outlying Dlp's 0.00 0.00 0.00
% Isokinetic 106.17 104.23 107.16
D50 Outlying Dlp's % Isokinetic Status
Run 1 Passed Passed Passed Acceptable Run
Run 2 Passed Passed Passed Acceptable Run
Run 3 Passed Passed Passed Acceptable Run
Run 4
Page 1
Run 1
Holcim Utelite Test Date 7/10-11/24 Imp. Liquid Collected in grams
Run No. 1 - RM 201A - Pre-test velocity traverse:Wt. (Final)Wt. (Tare)lc
Port 1 Port 2 Port 3 Port 4 371.0 336.0 35.0
Point No.∆P'sqrt ∆P'∆P'sqrt ∆P'∆P'sqrt ∆P'∆P'sqrt ∆P'623.2 615.7 7.5
1 617.3 607.9 9.4
2 962.2 950.4 11.8
3 0.0
∆P1 Avg.
Sqrt ∆P
No. Sample
Points
t1
in min.
Ts avg
-50oF
Avg.
Ts oF
Ts avg
+50oF
0.25 0.49663265 12 5.05 Ts oF 238.20 288.20 338.20
∆H 0.55 0.51 0.48
∆ = delta, i.e., delta P would be ∆P
Stack I.D.
(inches)As ft^2 Pbar Pq (static) Ps CO2 % O2 % N2+C
Md
lb/lb mole
Mw
lb/lb mole
Stack
Saturation
47.00 12.05 24.10 -0.22 24.08 6.70 13.20 80.10 29.60 28.03 4.7907
Y ∆H@ Cp 201A Cp 2 Dn An Vm cf Vm std Vlc Vw std Bws S Bws
0.9940 1.607 0.77 0.235 3.01E-04 25.264 19.119 63.70 3.000 0.1350 0.9990
Avg. Sqrt
∆p
Vs
ft/sec Avg. ∆h Avg. Tm F scfm wet acfm Qsd dscfh
Qs (final)
ft3/min
µs
Viscosity
Run Time
(act)
Target
Time
0.4838 33.66 0.360 99.00 13,820 24,334 7.17E+05 0.646520678 221.07 60.25 60
Sample
Point No.Dn used
Sampling
End Time
(Min.Sec.)
Actual
Dwell Time
(Min.Sec.)
Desired
Dwell Time
(Min.Sec.)
Stack Temp.
Ts F
Velocity
Head ∆P ∆h D50
Dry Gas Meter Temp.
tm F (in) tm F (out)
Status
Pmin &
Pmax
1 - ∆P t1 0.235 5.15 5.15 5.15 295 0.25 0.36 9.990 88 86 Passed
2 - ∆P tn 0.235 10.15 5.00 5.15 294 0.25 0.36 9.990 87 89 Passed
3 - ∆P tn 0.235 15.15 5.00 5.00 295 0.24 0.36 9.990 88 96 Passed
4 - ∆P tn 0.235 20.00 4.45 4.30 296 0.20 0.36 9.990 89 101 Passed
5 - ∆P tn 0.235 24.45 4.45 4.30 296 0.20 0.36 9.990 91 105 Passed
6 - ∆P tn 0.235 29.15 4.30 4.30 295 0.19 0.36 9.990 92 103 Passed
7 - ∆P tn 0.235 34.30 5.15 5.15 267 0.26 0.36 9.990 95 106 Passed
8 - ∆P tn 0.235 40.00 5.30 5.30 263 0.28 0.36 9.990 96 112 Passed
9 - ∆P tn 0.235 45.30 5.30 5.30 288 0.28 0.36 9.990 97 110 Passed
10 - ∆P tn 0.235 50.30 5.00 5.00 290 0.24 0.36 9.990 99 114 Passed
11 - ∆P tn 0.235 55.30 5.00 4.45 290 0.22 0.36 9.990 99 116 Passed
12 - ∆P tn 0.235 60.15 4.45 4.45 290 0.21 0.36 9.990 100 117 Passed
12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00
Run Acceptance Results.
D50 9.9900 Passed
Sampling Points outside of Pmin & Pmax 0.00 Passed
% Isokinetic 106.2 Passed
The results are acceptabel if two conditions are met:
A. D50 is between 9.0 µm & 11.0 µm.
If D50 is less than 9.0 reject the results and repeat the test.
B. One of the following conditions must also be met:That no sampling points are outside Pmin and Pmax or
1. No sampling points are outside the Pmin and Pmax or
2. Isokinetics sampling is betwee 80 percent & 120 percent and no more than one sampling point is outside ∆Pmin and ∆Pmax.
Acceptable Run
Acceptable Run
Test Run Completed
Acceptable Run
Acceptable Run
Page 1
Run 2
Holcim Utelite Test Date 7/10-11/24 Imp. Liquid Collected in grams
Run No. 2 - RM 201A - Pre-test velocity traverse:Wt. (Final)Wt. (Tare)lc
Port 1 Port 2 Port 3 Port 4 414.3 363.8 50.5
Point No.∆P'sqrt ∆P'∆P'sqrt ∆P'∆P'sqrt ∆P'∆P'sqrt ∆P'619.8 616.2 3.6
1 607.5 604.6 2.9
2 963.6 957.0 6.6
3 0.0
∆P1 Avg.
Sqrt ∆P
No. Sample
Points
t1
in min.
Ts avg
-50oF
Avg.
Ts oF
Ts avg
+50oF
0.17 0.4804869 12 4.20 Ts oF 243.60 293.60 343.60
∆H 0.54 0.51 0.48
∆ = delta, i.e., delta P would be ∆P
Stack I.D.
(inches)As ft^2 Pbar Pq (static) Ps CO2 % O2 % N2+C
Md
lb/lb mole
Mw
lb/lb mole
Stack
Saturation
47.00 12.05 24.10 -0.22 24.08 6.50 13.10 80.40 29.56 27.92 5.2109
Y ∆H@ Cp 201A Cp 2 Dn An Vm cf Vm std Vlc Vw std Bws S Bws
0.9940 1.607 0.77 0.233 2.96E-04 23.277 18.000 63.60 2.990 0.1420 0.9990
Avg. Sqrt
∆p
Vs
ft/sec Avg. ∆h Avg. Tm F scfm wet acfm Qsd dscfh
Qs (final)
ft3/min
µs
Viscosity
Run Time
(act)
Target
Time
0.4913 34.20 0.360 87.04 13,940 24,722 7.18E+05 0.6509922 221.87 58.75 60
Sample
Point No.Dn used
Sampling
End Time
(Min.Sec.)
Actual
Dwell
Time
(Min.Sec.)
Desired
Dwell Time
(Min.Sec.)
Stack
Temp.
Ts F
Velocity
Head
∆P ∆h D50
Dry Gas Meter Temp.
tm F (in) tm F (out)
Status
Pmin &
Pmax
1 - ∆P t1 0.235 4.00 4.00 5.00 293 0.17 0.36 9.990 75 73 Passed
2 - ∆P tn 0.235 9.00 5.00 5.00 293 0.25 0.36 9.990 76 79 Passed3 - ∆P tn 0.235 14.15 5.15 5.15 292 0.28 0.36 9.990 73 86 Passed
4 - ∆P tn 0.235 19.15 5.00 5.15 293 0.27 0.36 9.990 74 86 Passed
5 - ∆P tn 0.235 24.00 4.45 4.45 295 0.22 0.36 9.990 78 93 Passed
6 - ∆P tn 0.235 28.45 4.45 4.45 295 0.23 0.36 9.990 79 97 Passed
7 - ∆P tn 0.235 33.30 4.45 4.45 292 0.22 0.36 9.990 83 93 Passed
8 - ∆P tn 0.235 38.30 5.00 5.00 290 0.24 0.36 9.990 83 97 Passed
9 - ∆P tn 0.235 43.45 5.15 5.15 297 0.28 0.36 9.990 85 102 Passed
10 - ∆P tn 0.235 49.00 5.15 5.15 297 0.28 0.36 9.990 86 103 Passed
11 - ∆P tn 0.235 54.00 5.00 5.00 294 0.25 0.36 9.990 88 105 Passed
12 - ∆P tn 0.235 58.45 4.45 4.45 293 0.22 0.36 9.990 88 107 Passed
12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00
Run Acceptance Results.
D50 9.9900 Passed
Sampling Points outside of Pmin & Pmax 0.00 Passed
% Isokinetic 104.2 Passed
The results are acceptabel if two conditions are met:
A. D50 is between 9.0 µm & 11.0 µm.
If D50 is less than 9.0 reject the results and repeat the test.
B. One of the following conditions must also be met:That no sampling points are outside Pmin and Pmax or
1. No sampling points are outside the Pmin and Pmax or
2. Isokinetics sampling is betwee 80 percent & 120 percent and no more than one sampling point is outside ∆Pmin and ∆Pmax.
Acceptable Run
Acceptable Run
Test Run Completed
Acceptable Run
Acceptable Run
Page 1
Run 3
Holcim Utelite Test Date 7/10-11/24 Imp. Liquid Collected in grams
Run No. 3 - RM 201A - Pre-test velocity traverse:Wt. (Final)Wt. (Tare)lc
Port 1 Port 2 Port 3 Port 4 416.5 373.5 43.0
Point No.∆P'sqrt ∆P'∆P'sqrt ∆P'∆P'sqrt ∆P'∆P'sqrt ∆P'610.7 605.5 5.2
1 596.2 586.0 10.2
2 974.2 964.8 9.4
3 0.0
∆P1 Avg.
Sqrt ∆P
No. Sample
Points t1
in min.
Ts avg
-50oF
Avg.
Ts oF
Ts avg
+50oF
0.17 0.4870254 12 4.30 Ts oF 246.00 296.00 346.00
∆H 0.55 0.51 0.48
∆ = delta, i.e., delta P would be ∆P
Stack I.D.
(inches)As ft^2 Pbar Pq (static) Ps CO2 % O2 % N2+C
Md
lb/lb mole
Mw
lb/lb mole
Stack
Saturation
47.00 12.05 24.10 -0.22 24.08 6.50 12.80 80.70 29.55 27.92 5.4070
Y ∆H@ Cp 201A Cp 2 Dn An Vm cf Vm std Vlc Vw std Bws S Bws
0.9940 1.607 0.77 0.235 3.01E-04 25.426 19.331 67.80 3.190 0.1410 0.9990
Avg. Sqrt
∆p
Vs
ft/sec Avg. ∆h Avg. Tm F scfm wet acfm Qsd dscfh
Qs (final)
ft3/min
µs
Viscosity
Run Time
(act)
Target
Time
0.4836 33.89 0.360 96.41 13,770 24,497 7.10E+05 0.6531595 222.40 61.00 60
Sample
Point No.Dn used
Sampling
End Time
(Min.Sec.)
Actual
Dwell
Time
(Min.Sec.)
Desired
Dwell Time
(Min.Sec.)
Stack
Temp.
Ts F
Velocity
Head
∆P ∆h D50
Dry Gas Meter Temp.
tm F (in) tm F (out)
Status
Pmin &
Pmax
1 - ∆P t1 0.235 4.15 4.15 5.15 288 0.17 0.36 9.990 86 87 Passed
2 - ∆P tn 0.235 9.45 5.30 5.15 288 0.27 0.36 9.990 85 88 Passed3 - ∆P tn 0.235 15.15 5.30 5.30 292 0.28 0.36 9.990 85 95 Passed
4 - ∆P tn 0.235 20.15 5.00 4.45 300 0.22 0.36 9.990 86 99 Passed
5 - ∆P tn 0.235 25.00 4.45 4.45 301 0.21 0.36 9.990 87 103 Passed
6 - ∆P tn 0.235 30.00 5.00 5.00 301 0.23 0.36 9.990 88 106 Passed
7 - ∆P tn 0.235 35.30 5.30 5.15 289 0.27 0.36 9.990 91 105 Passed
8 - ∆P tn 0.235 14.00 -21.70 5.15 299 0.27 0.36 9.990 91 107 Passed
9 - ∆P tn 0.235 46.15 32.15 5.15 299 0.25 0.36 9.990 92 110 Passed
10 - ∆P tn 0.235 51.15 5.00 5.00 298 0.23 0.36 9.990 93 112 Passed
11 - ∆P tn 0.235 56.15 5.00 4.45 300 0.22 0.36 9.990 94 114 Passed
12 - ∆P tn 0.235 61.00 4.45 4.30 298 0.20 0.36 9.990 95 115 Passed
12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00
Run Acceptance Results.
D50 9.9900 Passed
Sampling Points outside of Pmin & Pmax 0.00 Passed
% Isokinetic 107.2 Passed
The results are acceptabel if two conditions are met:
A. D50 is between 9.0 µm & 11.0 µm.
If D50 is less than 9.0 reject the results and repeat the test.
B. One of the following conditions must also be met:That no sampling points are outside Pmin and Pmax or
1. No sampling points are outside the Pmin and Pmax or
2. Isokinetics sampling is betwee 80 percent & 120 percent and no more than one sampling point is outside ∆Pmin and ∆Pmax.
Acceptable Run
Acceptable Run
Test Run Completed
Acceptable Run
Acceptable Run
Page 1
Source Information
Division of Air Quality
Compliance Demonstration
Referance Method 201 & 201A for PM10
Source Information
Company Name Holcim Utelite
Company Contact:Carsten Mortensen
Contact Phone No.801-467-2800
Stack Designation:Kiln #3
Test & Review Dates
Test Date: 7/10/2024
Review Date: 9/23/2024
Observer: Robert Sirrine
Reviewer:Robert Sirrine
Particulate Emission Limits
lbs/MMBTU lbs/hr gr/dscf
0.000 3.340 0.024
Front Half Emission Rates
lbs/MMBTU lbs/hr gr/dscf
0.74 0.006
Total (Front & Back Half) Emission Rates
lbs/MMBTU lbs/hr gr/dscf
1.084693486 0.00902737
Test Information
Stack I.D. inches As ft^2 Y Dl H @ Cp Pbar Pq (static)Dn
Target
Time
46.50 11.793 0.9940 1.607 0.769 24.1 -0.27 0.216 60
Contractor Information
Contracting Company: TETCO
Contact: Dean Kitchen
Phone No.: 801-768-0973
Project No.:
Circular
10100
9780
9860
9190
8710
8710
8710
10540
10640
11950
320
10610
10200
10390
1970
1800
1910
1420
1040
1190
1250
F factor usedF factors for Coal, Oil, and Gas
Anthrocite 2
Lignite
Natural
Propane
Butane
COAL
OIL
GAS
Bituminous 2
Fd Fw Fc
scf/MMBtu scf/MMBtu scf/MMBtu
O2
CO2
lbs/MMBtu
Page 1
Summary
Division of Air Quality
Reference Methods 201 & 201A - TSP
Compliance Demonstration of
Holcim Utelite - Kiln #3
Testing Results Lab Data - grams collected
Test Date 7/10/2024 7/10/2024 7/10/2024 7/10/2024 Lab Data Cyclone Catch Filter Back
Run 1 Run 2 Run 3 Run 4 Run 1 0.0023 0.004800 0.00450
As ft^2 11.79 11.79 11.79 11.79 Run 2 0.0054 0.005000 0.00390
Pbar 24.10 24.10 24.10 24.10 Run 3 0.0054 0.000600 0.0025
Pq (static)-0.27 -0.27 -0.27 -0.27 Run 4
Ps 24.08 24.08 24.08 24.08
Avg. Ts F 264.80 262.80 264.80 Holcim Utelite Kiln #3
CO2 - FCO2 4.20 4.20 4.00 0.00 Front Half Emissions Summary
O2 14.80 14.50 14.90 0.00 Run 1 Run 2 Run 3 Run 4 Avg.
N2+C 81.00 81.30 81.10 100.00 gr./dscf 0.00584 0.00802 0.00460 0.00615
Md 29.26 29.25 29.24 28.00 lbs/hr 0.71 0.96 0.54 0.738
Mw 28.07 27.98 28.05 lbs/MMbtu
Y 0.9940 0.9940 0.9940 0.9940
Cp 0.77 0.77 0.77 0.77 Particulate Emission Limits Front Half Emission Rates
Vm cf 24.288 26.272 26.642 0.000 lbs/MMBTU lbs/hr gr/dscf lbs/MMBTU lbs/hr gr/dscf
Vlc 47.400 54.400 50.300 0.000 3.340 0.024 0.74 0.006152463
AVG. Tm F 87.66 95.25 99.87
Vm cf 24.288 26.272 26.642 0 Holcim Utelite Kiln #3
Vm std 18.760 20.018 20.133 #VALUE!Total Emissions Summary w/back half condensable
Vw std 2.230 2.560 2.370 Run 1 Run 2 Run 3 Run 4 Avg.
Bws 10.60% 11.30% 10.50% #VALUE! gr./dscf 0.00954 0.0110 0.0065 0.0090
S Bws 99.90% 99.90% 99.90% #VALUE! lbs/hr 1.1625 1.3211 0.7705 1.0847
Avg. Sqrt Dlp 0.56 0.55 0.55 0.51 lbs/MMbtu
Vs 38.316 37.882 37.151
scfm wet 15895.78 15758.96 15412.29 #VALUE!Particulate Emission Limits Total Emission Rates
acfm 27112.54 26805.01 26287.87 lbs/MMBTU lbs/hr gr/dscf lbs/MMBTU lbs/hr gr/dscf
Qsd dscfh 852650 838692 827640 3.340 0.024 1.084693486 0.00902737
Qs ft3/min 0.631649 0.628286 0.632130 #VALUE!
% Isokinetic 103.70 108.14 112.74 Test Quality Parameters
Viscostiy 218.11 216.92 218.23 Run 1 Run 2 Run 3 Run 4
D50 9.99 9.99 9.99
Outlying Dlp's 0.00 0.00 0.00
% Isokinetic 103.69 108.14 112.73
D50 Outlying Dlp's % Isokinetic Status
Run 1 Passed Passed Passed Acceptable Run
Run 2 Passed Passed Passed Acceptable Run
Run 3 Passed Passed Passed Acceptable Run
Run 4
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Run 1
Holcim Utelite Test Date 7/10/2024 Imp. Liquid Collected in grams
Run No. 1 - RM 201A - Pre-test velocity traverse:Wt. (Final)Wt. (Tare)lc
Port 1 Port 2 Port 3 Port 4 383.9 353.2 30.7
Point No.∆P'sqrt ∆P'∆P'sqrt ∆P'∆P'sqrt ∆P'∆P'sqrt ∆P'616.2 613.4 2.8
1 607.9 601.2 6.7
2 950.4 943.2 7.2
3 0.0
∆P1 Avg.
Sqrt ∆P
No. Sample
Points
t1
in min.
Ts avg
-50oF
Avg.
Ts oF
Ts avg
+50oF
0.26 0.583614384 12 4.29 Ts oF 214.80 264.80 314.80
∆H 0.57 0.53 0.5
∆ = delta, i.e., delta P would be ∆P
Stack I.D.
(inches)As ft^2 Pbar Pq (static) Ps CO2 % O2 % N2+C
Md
lb/lb mole
Mw
lb/lb mole
Stack
Saturation
46.50 11.79 24.10 -0.27 24.08 4.20 14.80 81.00 29.26 28.07 3.2756
Y ∆H@ Cp 201A Cp 2 Dn An Vm cf Vm std Vlc Vw std Bws S Bws
0.9940 1.607 0.77 0.216 2.54E-04 24.288 18.760 47.40 2.230 0.1060 0.9990
Avg. Sqrt
∆p
Vs
ft/sec Avg. ∆h Avg. Tm F scfm wet acfm Qsd dscfh
Qs (final)
ft3/min
µs
Viscosity
Run Time
(act)
Target
Time
0.5628 38.32 0.350 87.66 15,896 27,113 8.53E+05 0.631649377 218.11 59.00 60
Sample
Point No.Dn used
Sampling
End Time
(Min.Sec.)
Actual
Dwell Time
(Min.Sec.)
Desired
Dwell Time
(Min.Sec.)
Stack Temp.
Ts F
Velocity
Head ∆P ∆h D50
Dry Gas Meter Temp.
tm F (in) tm F (out)
Status
Pmin &
Pmax
1 - ∆P t1 0.216 4.30 4.30 4.30 266 0.26 0.35 9.990 74 74 Passed
2 - ∆P tn 0.216 10.00 5.30 5.15 265 0.39 0.35 9.990 74 77 Passed
3 - ∆P tn 0.216 15.15 5.15 5.15 268 0.38 0.35 9.990 75 82 Passed
4 - ∆P tn 0.216 20.15 5.00 5.00 265 0.34 0.35 9.990 77 84 Passed
5 - ∆P tn 0.216 25.15 5.00 4.45 266 0.33 0.35 9.990 79 93 Passed
6 - ∆P tn 0.216 30.30 5.15 5.00 264 0.35 0.35 9.990 80 98 Passed
7 - ∆P tn 0.216 34.30 4.00 3.45 261 0.21 0.35 9.990 84 99 Passed
8 - ∆P tn 0.216 38.46 4.15 4.15 261 0.25 0.35 9.990 84 99 Passed
9 - ∆P tn 0.216 43.30 4.44 4.30 269 0.29 0.35 9.990 86 104 Passed
10 - ∆P tn 0.216 48.30 5.00 4.45 268 0.32 0.35 9.990 87 104 Passed
11 - ∆P tn 0.216 53.45 5.15 5.00 262 0.36 0.35 9.990 87 106 Passed
12 - ∆P tn 0.216 59.00 5.15 5.00 263 0.35 0.35 9.990 89 108 Passed
12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00
Run Acceptance Results.
D50 9.9900 Passed
Sampling Points outside of Pmin & Pmax 0.00 Passed
% Isokinetic 103.7 Passed
The results are acceptabel if two conditions are met:
A. D50 is between 9.0 µm & 11.0 µm.
If D50 is less than 9.0 reject the results and repeat the test.
B. One of the following conditions must also be met:That no sampling points are outside Pmin and Pmax or
1. No sampling points are outside the Pmin and Pmax or
2. Isokinetics sampling is betwee 80 percent & 120 percent and no more than one sampling point is outside ∆Pmin and ∆Pmax.
Acceptable Run
Acceptable Run
Test Run Completed
Acceptable Run
Acceptable Run
Page 1
Run 2
Holcim Utelite Test Date 7/10/2024 Imp. Liquid Collected in grams
Run No. 2 - RM 201A - Pre-test velocity traverse:Wt. (Final)Wt. (Tare)lc
Port 1 Port 2 Port 3 Port 4 406.0 360.8 45.2
Point No.∆P'sqrt ∆P'∆P'sqrt ∆P'∆P'sqrt ∆P'∆P'sqrt ∆P'598.1 595.2 2.9
1 604.6 604.0 0.6
2 957.0 951.3 5.7
3 0.0
∆P1 Avg.
Sqrt ∆P
No. Sample
Points
t1
in min.
Ts avg
-50oF
Avg.
Ts oF
Ts avg
+50oF
0.33 0.5914468 12 4.87 Ts oF 212.80 262.80 312.80
∆H 0.56 0.52 0.49
∆ = delta, i.e., delta P would be ∆P
Stack I.D.
(inches)As ft^2 Pbar Pq (static) Ps CO2 % O2 % N2+C
Md
lb/lb mole
Mw
lb/lb mole
Stack
Saturation
46.50 11.79 24.10 -0.27 24.08 4.20 14.50 81.30 29.25 27.98 3.1669
Y ∆H@ Cp 201A Cp 2 Dn An Vm cf Vm std Vlc Vw std Bws S Bws
0.9940 1.607 0.77 0.218 2.59E-04 26.272 20.018 54.40 2.560 0.1130 0.9990
Avg. Sqrt
∆p
Vs
ft/sec Avg. ∆h Avg. Tm F scfm wet acfm Qsd dscfh
Qs (final)
ft3/min
µs
Viscosity
Run Time
(act)
Target
Time
0.5542 37.88 0.390 95.25 15,759 26,805 8.39E+05 0.6282862 216.92 60.25 60
Sample
Point No.Dn used
Sampling
End Time
(Min.Sec.)
Actual
Dwell
Time
(Min.Sec.)
Desired
Dwell Time
(Min.Sec.)
Stack
Temp.
Ts F
Velocity
Head
∆P ∆h D50
Dry Gas Meter Temp.
tm F (in) tm F (out)
Status
Pmin &
Pmax
1 - ∆P t1 0.218 5.15 5.15 4.30 258 0.33 0.39 9.990 84 84 Passed
2 - ∆P tn 0.218 10.45 5.30 5.00 255 0.35 0.39 9.990 84 88 Passed3 - ∆P tn 0.218 16.15 5.30 5.15 262 0.37 0.39 9.990 84 93 Passed
4 - ∆P tn 0.218 21.45 5.30 5.00 265 0.36 0.39 9.990 85 99 Passed
5 - ∆P tn 0.218 27.00 5.15 5.00 260 0.34 0.39 9.990 87 104 Passed
6 - ∆P tn 0.218 32.00 5.00 4.45 266 0.31 0.39 9.990 88 106 Passed
7 - ∆P tn 0.218 39.00 7.00 3.45 268 0.20 0.39 9.990 91 100 Passed
8 - ∆P tn 0.218 40.00 1.00 3.45 268 0.20 0.39 9.990 91 105 Passed
9 - ∆P tn 0.218 44.30 4.30 4.15 264 0.26 0.39 9.990 91 108 Passed
10 - ∆P tn 0.218 49.30 5.00 4.45 264 0.31 0.39 9.990 92 110 Passed
11 - ∆P tn 0.218 54.45 5.15 5.00 264 0.34 0.39 9.990 93 112 Passed
12 - ∆P tn 0.218 60.15 5.30 5.00 260 0.35 0.39 9.990 94 113 Passed
12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00
Run Acceptance Results.
D50 9.9900 Passed
Sampling Points outside of Pmin & Pmax 0.00 Passed
% Isokinetic 108.1 Passed
The results are acceptabel if two conditions are met:
A. D50 is between 9.0 µm & 11.0 µm.
If D50 is less than 9.0 reject the results and repeat the test.
B. One of the following conditions must also be met:That no sampling points are outside Pmin and Pmax or
1. No sampling points are outside the Pmin and Pmax or
2. Isokinetics sampling is betwee 80 percent & 120 percent and no more than one sampling point is outside ∆Pmin and ∆Pmax.
Acceptable Run
Acceptable Run
Test Run Completed
Acceptable Run
Acceptable Run
Page 1
Run 3
Holcim Utelite Test Date 7/10/2024 Imp. Liquid Collected in grams
Run No. 3 - RM 201A - Pre-test velocity traverse:Wt. (Final)Wt. (Tare)lc
Port 1 Port 2 Port 3 Port 4 410.1 371.8 38.3
Point No.∆P'sqrt ∆P'∆P'sqrt ∆P'∆P'sqrt ∆P'∆P'sqrt ∆P'606.0 603.7 2.3
1 586.0 582.8 3.2
2 969.8 963.3 6.5
3 0.0
∆P1 Avg.
Sqrt ∆P
No. Sample
Points t1
in min.
Ts avg
-50oF
Avg.
Ts oF
Ts avg
+50oF
0.29 0.5592823 12 4.81 Ts oF 214.80 264.80 314.80
∆H 0.58 0.54 0.5
∆ = delta, i.e., delta P would be ∆P
Stack I.D.
(inches)As ft^2 Pbar Pq (static) Ps CO2 % O2 % N2+C
Md
lb/lb mole
Mw
lb/lb mole
Stack
Saturation
46.50 11.79 24.10 -0.27 24.08 4.00 14.90 81.10 29.24 28.05 3.2756
Y ∆H@ Cp 201A Cp 2 Dn An Vm cf Vm std Vlc Vw std Bws S Bws
0.9940 1.607 0.77 0.216 2.54E-04 26.642 20.133 50.30 2.370 0.1050 0.9990
Avg. Sqrt
∆p
Vs
ft/sec Avg. ∆h Avg. Tm F scfm wet acfm Qsd dscfh
Qs (final)
ft3/min
µs
Viscosity
Run Time
(act)
Target
Time
0.5455 37.15 0.400 99.87 15,412 26,288 8.28E+05 0.6321298 218.23 60.00 60
Sample
Point No.Dn used
Sampling
End Time
(Min.Sec.)
Actual
Dwell
Time
(Min.Sec.)
Desired
Dwell Time
(Min.Sec.)
Stack
Temp.
Ts F
Velocity
Head
∆P ∆h D50
Dry Gas Meter Temp.
tm F (in) tm F (out)
Status
Pmin &
Pmax
1 - ∆P t1 0.216 4.45 4.45 4.45 265 0.29 0.40 9.990 89 88 Passed
2 - ∆P tn 0.216 10.00 5.15 4.45 260 0.30 0.40 9.990 89 91 Passed3 - ∆P tn 0.216 15.15 5.15 5.15 263 0.35 0.40 9.990 89 98 Passed
4 - ∆P tn 0.216 20.30 5.15 5.00 267 0.34 0.40 9.990 91 106 Passed
5 - ∆P tn 0.216 25.30 5.00 5.00 266 0.32 0.40 9.990 91 108 Passed
6 - ∆P tn 0.26 30.30 5.00 4.45 264 0.30 0.40 9.990 93 111 Passed
7 - ∆P tn 0.216 34.30 4.00 3.45 262 0.19 0.40 9.990 96 104 Passed
8 - ∆P tn 0.216 40.15 5.45 4.30 261 0.28 0.40 9.990 96 107 Passed
9 - ∆P tn 0.216 45.00 4.45 4.30 269 0.27 0.40 9.990 96 110 Passed
10 - ∆P tn 0.216 49.45 4.45 4.45 272 0.29 0.40 9.990 97 114 Passed
11 - ∆P tn 0.216 55.00 5.15 5.00 264 0.34 0.40 9.990 99 117 Passed
12 - ∆P tn 0.216 60.00 5.00 5.00 265 0.32 0.40 9.990 99 118 Passed
12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00 12.00
Run Acceptance Results.
D50 9.9900 Passed
Sampling Points outside of Pmin & Pmax 0.00 Passed
% Isokinetic 112.7 Passed
The results are acceptabel if two conditions are met:
A. D50 is between 9.0 µm & 11.0 µm.
If D50 is less than 9.0 reject the results and repeat the test.
B. One of the following conditions must also be met:That no sampling points are outside Pmin and Pmax or
1. No sampling points are outside the Pmin and Pmax or
2. Isokinetics sampling is betwee 80 percent & 120 percent and no more than one sampling point is outside ∆Pmin and ∆Pmax.
Acceptable Run
Acceptable Run
Test Run Completed
Acceptable Run
Acceptable Run
Page 1