HomeMy WebLinkAboutDRC-2012-001086 - 0901a068802a7faaC- 20 12-00 108 6
January 30 2012
VIA E MAIL AND OVERNIGHT DELIVERY
Mr Rusty Lundberg
Department of Environmental Quality
195 North 1950 West
PO Box 144850
Salt Lake City UT 84114 4850
Denison Mines (USA) Corp
105017th street Suite 950
Denver CO 80265
USA
Tel 303 628 7798
Fax 303 389 4125
www denisonmines com
Re State of Utah Groundwater Discharge Permit ( GWDP ) No UGW370004
Transmittal of Revised Discharge Minimization Technology Monitonng ( DMT ) Revision 11 4
dated January 2012
Dear Mr Lundberg
Reference is made to the Division of Radiation Control ( DRC ) letters dated September 13 2011
December 14 2011 and December 22 2011 regarding the White Mesa Mill Tailings Management
System and Discharge Minimization Technology ( DMT ) Monitonng Plans dated June 2011 (Revision
11 2) and July 2011 (Revision 11 3)
This letter transmits Denison Mines (USA) Corp s ( Denison s ) proposed revisions to the White Mesa
Mill DMT Plan These revisions include changes made to
1 Respond to the Request for Information ( RFI )/Confirmatory Action Letter dated September 13
2011
2 Respond to the comments provided in the December 22 2011 DRC letter and
3 Correct additional errors and inconsistencies in the June 2011 and July 2011 Revisions of the
DMT Plan
For ease of review we have provided both redline and clean versions of each document
The attached DMT Plan Revision 11 4 has accepted all the redline changes proposed in Denison s June
23 2011 and July 11 2011 submittals as the base version in black type Changes resulting from the
above referenced DRC comment letters are provided in redline/stnkeout format
We have also provided below specific responses to each request in DRCs September 13 2011 and
December 22 2011 letters The sections and numbenng of the remainder of this letter follow the DRC
September 13 2011 and December 22 2011 letters Each DRC request is shown in italics below
followed by Denison s response
Letter to Mr Rusty Lundberg
January 30 2012
Page 2
Responses to Comments Provided to DUSA in the September 13 2011 DRC RFI/Confirmatory
Action Letter (as re transmitted in a DRC letter dated December 14 2011)
DRC Comment
1 DUSA will provide the DRC the appropriate Mine Safety and Health Administration (MSHA) rule
quotation(s) and citing(s) that require the use of walkways with handrails when egressing active tailings
cells According to our discussion these requirements precluded DUSA from making water level elevation
measurements in Cell 4B
Denison Response
The requested MSHA citations are as follows
1 30 CFR 56 11001 - Safe Access - Safe means of access shall be provided and maintained
to all working places
2 30 CFR 56 11002-Handrails and toeboards- Crossovers elevated walkways elevated
ramps and stairways shall be of substantial construction provided with handrails and
maintained in good condition Where necessary toeboards shall be provided
3 Statutory Miners Rights - Right to refuse to work under conditions or practices believed to
be unsafe unhealthy or illegal
4 Statutory Miners Rights - Right to protection from discnmination for exercising statutory
rights
Under the requirements of MSHA if there is no MSHA regulation specific to a given issue but there is
one under OSHA the OSHA rule does apply That being the case Denison is also required to comply
OSHAs policies for nng buoys lifesaving skiffs and other requirements as prescnbed in 1910 and 1926
(General Industry and Construction) under OSHA s policies if a walkway with handrails is not avaialble
DRC Comment
2 DUSA will commit to a penod of time to construct walkways for new tailings cells after receiving
authorization for use of any new tailings cell from the Executive Secretary This time period must be
submitted for approval in a revised DMT Plan
Denison Response
It IS Denison s understanding that DRC s request for a time commitment to construct walkways in new
cells IS based on the assumption that the initiation of solution level measurements in future cells will
require a walkway That is Denison understands that DRC actually seeks a time commitment for
initiating solution level measurement Tailmgs cell wastewater pool elevations will be monitored within 30
days of authonzation for use in accordance with the existing survey procedures specified in the DMT Plan
and in accordance with Mill health and safety requirements The DMT Plan has been revised to reflect
this requirement Health and safety requirements will dictate the methods such as floating walkways for
providing worker access to the new cells are not discussed in the DMT Plan
DRC Comment
3 DUSA will acquire a steel surveyors tape(s) of adequate length or develop other approved means to
accurately measure water level elevations prior to construction of the walkway discussed in the two
numbered items immediately above The procedures for this method to measure the water level
elevation will be submitted by DUSA for approval in a revised DMT Plan
Denison Response
A steel surveyors tape will not be used to measure tailings wastewater pool elevations Consistent with
the remainder of Comment 3 Denison has developed other means to accurately measure cell solution
level elevations prior to construction of any walkways Therefore a descnption of procedure for use of a
surveyor s tape is not necessary No changes to the text have been made
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Letter to Mr Rusty Lundberg
January 30 2012
Page 3
DRC Comment
4 DUSA will revise the DMT Plan reference (c) so the point designated for the water level measurement
in Cell 4B will be the southeast corner rather than the current required location
Denison Response
The text has been changed as requested
DRC Comment
5 DUSA must acquire a longer survey elevation rod eg a 45 rod) in order to survey the water level in
the subject cell at lowest depths DUSA will revise the DMT Plan to include procedures for use of this
longer survey rod
Denison Response
Denison has purchased a longer survey elevation rod 45 feet in length The procedures for use of the
longer survey elevation rod are the same as those currently descnbed in the DMT plan The longer
survey elevation rod does not require any procedural changes therefore no changes were made in the
DMT Plan
DRC Comment
6 A revised DMT Plan proposed in reference (e) contains a new paragraph on page 10 As discussed
this specific proposed new verbiage is not acceptable The DMT Plan must be revised in accordance with
the above commitments and requirements
Denison Response
The paragraph in question has been modified to specify that tailings wastewater pool elevations in new
cells will be measured within 30 days of authonzation for use of the new cell
DRC Comment
7 A new revised DMT Plan containing all the necessary verbiage changes from the items above will be
submitted for approval
Denison Response
The revised DMT Plan Revision 11 4 dated January 2012 is attached
Responses to Comments Provided to Denison in the DRC letter dated December 22 2011
DMT Plan Changes Required, from the Groundwater Discharge Permit Part I H 7
DRC Comment
1 Permit Part ID 3(b) paragraphs ii and in now that the slimes dram access pipe has been extended
the correspondmg measurements in the DMT Plan need to be corrected
Denison Response
The Cell 2 shmes dram access pipe measurements have been changed in the DMT Plan and the
appropnate forms in the appendices to the Plan As a result of the changes in Cell 2 and the corrected
measurements descnbed below the new depth of the Cell 2 shmes dram access pipe is 37 97 feet This
modification has been made in the DMP Plan Revision 11 4 The changes to the Cell 2 slimes dram
access pipe are described in more detail below
Two sets of measurements are routinely collected from the Cell 2 slimes dram access pipe for compliance
with the GWDP and the RML The first measurement is the quarterly recovery test which is conducted to
determine the compliance with the GWDP Part I D 3 (b)2 The second set of measurements are the
weekly pre and post pump head measurements required by the License Changes to Cell 2 were
completed dunng the second and third quarter 2011 which affect both sets of measurements collected
from the Cell 2 shmes access dram Where these changes affect the DMT Plan or inspections forms the
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Letter to Mr Rusty Lundberg
January 30 2012
Page 4
Plan or forms have been revised A descnption of the changes and the effects on the measurements are
as follows
Summary of Changes to Cell 2
As detailed in letters to DRC dated May 27 June 17 and August 1 2011 Denison re graded the interim
fill on Cell 2 in order to reduce the potential for the accumulation of stormwater on the surface of Cell 2
which could potentially infiltrate into Cell 2 This re grading required 62 000 cubic yards of cut and fill
and was completed on July 30 2011 As a result of the re grading of the intenm cover and the
placement of additional fill the Cell 2 slimes dram access pipe was extended to bnng it above grade
relative to the new cell surface elevation The extension pipe which is the same diameter as the existing
access pipe was placed on top of the previous Cell 2 slimes dram access location and was mechanically
attached using metal braces and plates The seam between the existing pipe and the extension were
sealed with caulking and an external covenng to prevent infiltration by dirt and debns The measunng
point for the extension of the slimes dram access pipe is directly above the previous measunng point
The distance from the old measunng point to the new extended measunng point was measured to an
accuracy of 0 01 feet The extension to the Cell 2 shmes dram access pipe measures 6 97 feet The
extension was placed July 20 2011
Quarterly Recovery Test Data
As noted above the quarterly recovery test is completed in accordance with the GWDP dated July 14
2011 Part I D 3 (b)(2) The recovery test data are collected by measunng the fluid level in the shmes
dram over an extended penod of time (greater than 90 hours) The measurements for the recovery test
are taken by measunng the distance from the measunng point to the top of the fluid present in the Cell 2
shmes dram access pipe The total depth of the Cell 2 shmes dram access pipe is not used in any of the
calculations for determination of compliance with the GWDP Compliance determinations rely on
elevation data generated by subtracting depth of the fluid levels measured from the top of the Cell 2
shmes dram access pipe from the elevation of the slimes dram access pipe There will be no change in
the shmes dram elevation numbers generated because both the measurements used in the subtraction
are adjusted by the same factor In order to make the data collected pnor to July 20 2011 comparable to
the current data for use in the graphical representations 6 97 feet was added to all of the previous
recovery data to adjust for the height added with the extension to the Cell 2 shmes dram access pipe
Weekly Pre and Post Pump Head Measurements
As noted above weekly pre and post pump head measurements are collected as required by the RML
The weekly pre and post pump head measurements are taken by measunng the distance from the
measunng point to the top of the fluid present in the Cell 2 shmes access pipe Two measurements are
taken the first measurement is taken before the pump is started and the second is taken after the pump
has run for 15 minutes The pre and post pump head is calculated by subtracting the liquid level from
the total depth of the Cell 2 slimes dram
Dunng the measurements of the extension to the Cell 2 shmes dram access pipe it was noted by the field
personnel that the new length of the Cell 2 shmes dram access pipe is now approximately 38 feet The
previous measurement used for the pre and post pumping head measurements was also 38 feet and the
discrepancy was noted An investigation into the discrepancy between the previous total depth of the Cell
2 slimes dram and the current depth of the Cell 2 slimes dram was conducted The investigation included
a review of the as built drawings for Cell 2 previous pre and post pump measurements and a review of
the Cell 2 shmes drain access pipe procedures The as built drawings and the results of the investigation
indicate that the previous total depth of the Cell 2 slimes dram was actually 31 feet With the extension of
6 79 feet to the previous total depth of 31 feet the current depth is now approximately 38 feet Pnor to
the second quarter of 2011 the pre and post pump data was not reported to DRC The pre and post
pump data were reported to DRC only in the second and third quarter 2011 DMT Reports The corrected
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Letter to Mr Rusty Lundberg
January 30 2012
Page 5
second and third quarter data will be included in the next quarterly DMT Report submitted on or before
March 1 2012
DRC Comment
2 Part IE 7(b) paragraph (2) a professional survey of the new measurement point needs to be made
Denison Response
The Cell 2 slimes dram access pipe has been surveyed by a Utah certified Land Surveyor
DRC Comment
3 Now that the Cell 2 slimes dram access pipe has been extended in height DUSA must state in the
DMT Plan how the measurements to the water surface will be taken now and how DUSA will correlate
these measurements correctly to earlier measurements
Denison Response
The weekly measurement procedure was not changed as a result of the extension of the Cell 2 shmes
dram access pipe The head values are calculated in the same manner using the same procedures as
those used prior to the extension of the Cell 2 slimes dram access pipe however the total depth to the
bottom of the pipe has changed to 37 97 feet as noted to the response to DRC comment number 1
above The new total depth is now used to calculate the pre and post pumping head The new
measurement is noted on the Weekly Tailings Inspection form in Attachment A of the DMT Plan
Correlation and/or adjustment for the height of the Cell 2 slimes dram access pipe for the calculation of
the pre and post pumping head values is not necessary The pre and post head values are calculated
by subtracting the liquid level measured pre and post pumping from the total depth of the Cell 2 shmes
dram access pipe The pre and post pumping head value is a calculated difference that uses the total
height of the Cell 2 shmes dram access pipe As can be seen in the following example the pre and post
head values are the same regardless of the height of the Cell 2 shmes dram access pipe
The pre and post pumping values are stored in hardcopy at the Mill site on the Weekly Inspection forms
A note to the file will be stored with all of the hardcopy forms that show the incorrect total depth of 38 feet
If recalculation were necessary the correct height measurement to complete the calculation will be used
Other Comments on the DMT Plan (reference (B)
DRC Comment
4 On page 4 in the first sentence the items Cell 3 Cell 4A spillway should be reversed in their order in
the sentence to be clearer in meaning
Denison Response
The text was changed as requested
DRC Comment
5 In paragraph 6 35 there are several references to Cell 4A that apparently should refer to Cell 4B
instead This occurs in paragraphs (c) iv vi vii and paragraph (d)iii In Appendix F of the DMT Plan this
misreference appears to occur on page 56 in the second and fifth bullet line Please correct
Denison Response
The text corrections have been made as requested
DRC Comment
6 Paragraph 6 2 needs to be revised due to the construction of Cell 4B It needs to be corrected to refer
to the current exterior dikes required to have movement monitoring
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Letter to Mr Rusty Lundberg
January 30 2012
Pages
Denison Response
The text corrections have been made as requested
DRC Comment
7 Page 29 Table III Column under Dike 3 If there is visible embankment on the south dike of Cell 3
please adjust the form as appropriate
Denison Response
There is no visible embankment on the south dike of Cell 3 and no changes to the text were required
DRC Comment
8 On page 36 paragraph 7 refers to a Contaminated Waste Dump awaiting DRC approval We are
uncertain as to what this is Please clarify
Denison Response
The name Contaminated Waste Dump is an incorrect designation for the Designated Disposal Area for
Non Tailmgs Mill waste discussed in SOP PBL 7 The form has been modified to refer to the area
correctly The notation awaiting DRC approval on the form refers to an amendment request submitted
to DRC by Denison in 2008 to revise the SOP to permit disposal of non tailings Mill waste in more than
one cell To date DRC has not provided any response to that amendment request
DRC Comment
9 Due to the installation of additional platform fill on Cell 2 slimes dram recovery elevation measurement
related items in the DMT Plan need to be changed On the DMT Plan inspection form p 34 paragraph 2
the 38 foot figure appears to need adjustment
Denison Response
The form was changed as required
Please contact me if you have any questions or require any further information
Yours very truly
DENISON MINES (USA) CORP
4)o Ann Tischler
Director Compliance and Permitting
cc David C Frydenlund
Ron F Hochstein
Harold R Roberts
David Rupp
David E Turk
K Weinel
Attachments
White Mesa Mill - Standard Operating Procedures 01/12 Revision Denisonl 1 4
Book 11 Environmental Protection Manual Section 3 1 Page 1 of 53
WHITE MESA MILL TAILINGS MANAGEMENT SYSTEM
AND
DISCHARGE MINIMIZATION TECHNOLOGY (DMT)
MONITOMNG PLAN
TABLE OF CONTENTS
Contents
1 INTRODUCTION 3
2 DAILY TAILINGS INSPECTIONS 3
2 1 Daily Comprehensive Tailmgs Inspection 3
2 2 Daily Operations Inspection 6
2 3 Daily Operations Patrol 6
2 4 Training 6
2 5 Tailings Emergencies 6
3 WEEKLY TAILINGS AND DMT INSPECTION 7
3 1 Weekly Tailings Inspections 7
Northing 12
Easting 12
3 2 Weekly Inspection of Solution Levels in Roberts Pond 14
3 3 Weekly Feedstock Storage Area Inspections 15
4 MONTHLY TAILINGS INSPECTION 15
5 QUARTERLY TAILEsfGS INSPECTION 16
6 ANNUAL EVALUATIONS 17
6 1 Annual Technical Eveiluation 17
6 2 Movement Monitors 18
6 3 Freeboard Linuts 18
6 3 1 Cell 1 19
6 3 2 Cell 2 19
6 3 3 Cell 3 19
6 3 4 Cell 4A 19
6 3 5 Cell 4B 19
6 3 6 Roberts Pond 22
6 4 Annual Leak Detection Fluid Samples 22
6 5 Annual Inspection of the Decontamination Pads 23
7 OTHER INSPECTIONS 23
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White Mesa Mill - Standard Operating Procedures
Book 11 Envu-onmental Protection Manual Section 3 1
01/12 Revision Denisonll 4
Page 2 of 53
8 REPORTING REQUIREMENTS
8 1 Monthly Tailings Reports
8 2 DMT Reports
8 3 TAILINGS INSPECTOR TRAEsFING
23
23
24
40
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Book 11 Envu:onmental Protection Manual Section 3 1 Page 3 of 53
1 INTRODUCTION
This Tailings Management System and Discharge Minimization Technology Monitonng Plan (the
Plan ) for the White Mesa Mill (the Mill ) provides procedures for monitoring of the tailings cell
system as required under State of Utah Radioactive Matenals License No UT1900479 (the
Radioactive Materials License ) as well as procedures for operating and maintenance of monitonng
equipment and reporting procedures that are adequate to demonstrate DMT compliance under State
of Utah Ground Water Discharge Permit No 370004 for the Mill (the GWDP )
This Plan is designed as a systematic program for constant surveillance and documentation of the
integrity of the tailings impoundment system including dike stability liner integrity and transport
systems as well as monitoring of water levels m Roberts Pond and feedstock storage areas at the
Mill The Plan requires daily weekly quarterly monthly and annual inspections and evaluations and
monthly reporting to Mill management
2 DAILY TAILINGS INSPECTIONS
The following daily tailings inspections shall be performed
2 1 Dailv Comprehensive Tailings Inspection
On a daily basis including weekends all areas connected with the evaporation cell (Cell 1) and
thefour tailings cells (Cells 2 3 4A and 4B) will be inspected Observations will be made of the
current condition of each cell noting any corrective action that needs to be taken
The Radiation Safety Officer (RSO) or his designee is responsible for performing the daily tailings
inspections The RSO may designate other individuals with trainmg as described in Section 2 4
below to perform the daily tailings inspection
Observations made by the inspector will be recorded on the Daily Inspection Data form (a copy of
which IS attached in Appendix A) The Daily Inspection Data form contains an inspection checklist
which mcludes a tailings cells map and spaces to record observations especially those of immediate
concem and those requiring corrective action The inspector will place a check by all inspection
items that appear to be operating properly Those items where conditions of potential concem are
observed should be marked with an X A note should accompany the X specifying what the
concem is and what conective measures will resolve the problem This observation of concem
should be noted on the form until the problem has been remedied The date that conective action
was taken should be noted as well
Areas to be inspected include the following Cell 1 2 3 4A and 4B Dikes 4A S 4A E and 4B
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Book 11 Environmental Protection Manual Section 3 1 Page 4 of 53
S wind movement of tailings effectiveness of dust minimization methods spray evaporation Cell 2
spillway Cell 3 spillway Cell 4A spillway Cell 3 Cell 4A and 4B liquid pools and associated liquid
retum equipment and cell leak detection systems
Operational features of the tailings area are checked for conditions of potential concem The
following Items require visual inspection during the daily tailings inspection
a) Tailmgs slurry and SX raffinate transport systems from the Mill to the active
disposal cell(s) and pool retum pipeline and pumps
Daily inspections of the tailings lines are required to be performed when the Mill
IS operating The lines to be inspected include the tailings slurry lines from CCD
to the active tailmgs cell SX raffinate lines that can discharge into Cell 1 Cell
4A or Cell 4B the pond retum line from the tailings area to the Mill and lines
transporting pond solutions from one cell to another
b) Cell 1
c) Cell 2
d) Cell 3
e) Cell 4A
f) Cell 4B
g) Dike stmctures including dikes 4A S 4A E and 4B S
h) The Cell 2 spillway Cell 3 spillway Cell 4A spillway Cell 3 Cell 4A and Cell
4B liquid pools and associated liquid retum equipment
i) Presence of wildlife and/or domesticated animals in the tailings area including
waterfowl and bunowing animal habitations
j) Spray evaporation pumps and lines
k) Wind movement of tailings and dust rmniimzation
Wind movement of tailings will be evaluated for conditions which may require
initiation of preventative dust minimization measures for cells containing tailmgs
sand During tailmgs inspection general surface conditions will be evaluated for
the following 1) areas of tailings subject to blowing and/or wind movement 2)
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Book 11 Environmental Protection Manual Section 3 1 Page 5 of 53
liquid pool size 3) areas not subject to blowing and/or wind movement
expressed as a percentage of the total cell area The evaluations will be reviewed
on a weekly basis or more frequently if wananted and will be used to direct dust
nunimization activities
1) Observation of flow and operational status of the dust control/spray evaporation
system(s)
m) Observations of any abnormal variations in tailings pond elevations in Cells 1 3
4A and4B
n) Locations of slurry and SX discharge within the active cells Slurry and SX
discharge points need to be indicated on the tailings cells map included m the
Daily Inspection Data form
o) An estimate of flow for active tailings slurry and SX line(s)
p) An estimate of flow in the solution retum line(s)
q) Daily measurements m the leak detection system sumps of the tailmgs cells will
be made when warranted by changes in the solution level of the respective leak
detection system
The trigger for further action when evaluating the measurements in the Cell 1 and
Cell 3 leak detection systems is a gain of more than 12 inches in 24 hours The
solution level m Cell 4A or 4B leak detection system is not allowed to be more
than 1 0 foot above the lowest point on the bottom flexible membrane liner
(FML) (Cell 4A FML elevation is 5555 14 amsl and with the addition of the 1 0
foot of solution the solution elevation is 5556 14 feet amsl For Cell 4B the FML
elevation is 5557 50 amsl and with the addition of the 1 0 foot of solution the
solution elevation is 5558 50 feet amsl) If any of these observations are made
the Mill Manager should be notified immediately and the leak detection system
pump started In addition the requirement to notify the Executive Secretary in
accordance with Parts ID 6 and IG 3 of the Groundwater Discharge Permit must
be adhered to when the solution level trigger for Cell 4A or 4B has been
exceeded
Whenever the leak detection system pump is operating and the flow meter
totalizer is recording a notation of the date and the time will be recorded on the
Daily Inspection Data form This data will be used in accordance with License
Condition 11 3 B through 11 3 E of the Mill s Radioactive Materials License to
determine whether or not the flow rate into the leak detection system is in excess
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Book 11 Environmental Protection Manual Section 3 1 Page 6 of 53
of the License Conditions
Items (a) (m) (n) and (o) are to be done only when the Mill is operating When the Mill is down
these Items cannot be performed
2 2 Dailv Operations Inspection
Dunng Mill operation the Shift Foreman or other person with the training specified in Section 2 4
below designated by the Radiation Safety Officer will perform an inspection of the tailings line and
tailings area at least once per shift paying close attention for potentisd leaks and to the discharges
from the pipelines Observations by the Inspector will be recorded on the appropriate line on the
Operating Foreman s Daily Inspection form
2 3 Dailv Operations Patrol
In addition to the inspections described in Sections 2 1 and 2 2 above a Mill employee will patrol
the tailings area at least twice per shift during Mill operations to ensure that there are no obvious
safety or operational issues such as leaking pipes or unusual wildlife activity or incidences
No record of these patrols need be made but the inspectors will notify the RSO and/or Mill
management in the event that during their inspection they discover that an abnormal condition or
tailings emergency has occuned
2 4 Training
All individuals performing inspections described in Sections 2 1 and 2 2 above must have Tailings
Management System training as set out m the Tailings Inspection Training procedure which is
attached as Appendix B This training will include a training pack explaining the procedure for
performing the inspection and addressing inspection items to be observed In addition each
individual after reviewing the training pack will sign a certification form indicating that training
has been received relative to his/her duties as an inspector
2 5 Tailings Emergencies
Inspectors will notify the RSO and/or Mill management immediately if dunng their inspection they
discover that an abnormal condition exists or an event has occuned that could cause a tailings
emergency Until relieved by the Environmental or Technician or RSO inspectors will have the
authority to direct resources during tailings emergencies
Any major catastrophic events or conditions pertaining to the tailmgs area should be reported
immediately to the Mill Manager or the RSO one of whom will notify Corporate Management If
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Book 11 Environmental Protection Manual Section 3 1 Page 7 of 53
dam failure occurs notify your supervisor and the Mill Manager immediately The Mill Manager
will then notify Corporate Management MSHA (303 231 5465) and the State of Utah Division of
Dam Safety (801 538 7200)
3 WEEKLY TAILINGS AND DMT INSPECTION
3 1 Weeklv Tailings Inspections
Weekly tailings inspections are to be conducted by the Radiation Safety Department and include the
following
a) Leak Detection Systems
Each tailings cell s leak detection system shall be checked weekly (as well as
daily) to determine whether it is wet or dry If marked wet the liquid levels need
to be measured and reported In Cell 1 and Cell 3 the leak detection system is
measured by use of a dual probe system that senses the presence of solutions in
the LDS system (comparable to the systems m Cells 4A and 4B) and indicates the
presence of solution with a warning light The Cell 4A and 4B leak detection
systems are monitored on a continuous basis by use of a pressure transducer that
feeds water level information to an electronic data collector The pressure
transducer is calibrated for fluid with a specific gravity of 1 0 The water levels
are measured every hour and the information is stored for later retrieval The
water levels are measured to the nearest 0 10 inch The data collector is cunently
programmed to store 7 days of water level information The number of days of
stored data can be increased beyond 7 days if needed For Cells 1 and 3 the
water level data is recorded on the Daily Tailings Inspection Form For Cells 4A
and 4B the water level data is downloaded to a laptop computer periodically and
incorporated into the Mill s environmental monitoring data storage and into the
files for weekly inspection reports of the tailings cell leak detection systems
If sufficient fluid is present in the leak detection system of any cell the fluid shall
be pumped from the LDS to the extent reasonably possible and record the
volume of fluid recovered Any fluid pumped from an LDS shall be retumed to a
disposal cell
For Cells 1 and 3 if fluid is pumped from an LDS the flow rate shall be
calculated by dividing the recorded volume of fluid recovered by the elapsed time
since fluid was last pumped or increases in the LDS fluid levels were recorded
whichever is the more recent This calculation shall be documented as part of the
weekly inspection
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Book 11 Envu-onmental Protection Manual SecUon 3 1 Page 8 of 53
For Cells 1 and 3 upon the initial pumping of fluid from an LDS a fluid sample
shall be collected and analyzed m accordance with paragraph 11 3 C of the
Radioactive Matenals License
For Cell 4A and 4B under no circumstance shall fluid head in the leak
detection system sump exceed a 1 foot level above the lowest point in the
lower flexible membrane liner To determine the Maximum Allowable Daily
LDS Flow Rates in the Cell 4A and 4B leak detection systems the total
volume of all fluids pumped from the LDS on a weekly basis shall be
recovered from the data collector and that information will be used to
calculate an average volume pumped per day Under no circumstances shall
the daily LDS flow volume exceed 24 160 gallons/day for Cell 4A or 26 145
gallons/day for Cell 4B The maximum daily LDS flow volume will be
compared against the measured cell solution levels detailed on Table 1A and
IB (for Cells 4A and 4B respectively) m Appendix E to determine the
maximum daily allowable LDS flow volume for varying head conditions in
Cell 4A and 4B
b) Slimes Drain Water Level Monitoring
(i) Cell 3 IS nearly full and will commence closure when filled Cell 2 is partially
reclaimed with the surface covered by platform fill Each cell has a shmes drain
system which aids in dewatering the shmes and sands placed m the cell
(ll) Denison re graded the interim fill on Cell 2 in order to reduce the potential for the
accumulation of stormwater on the surface of Cell 2 As a result of the re grading of
the interim cover and the placement of an additional 62 000 cubic yards of fill
material on Cell 2 the shmes drain access pipe was extended 6 97 feet The
extension pipe is 6 97 feet in length and therefore the new measuring point is 37 97
feet from the bottom of the shmes dram The measuring point on the extension pipe
was surveyed by a Utah Certified Land Surveyor For the quarterly recovery test
descnbed in section vi below this extension has no effect on the data measurement
procedures
Cell 2 has a pump placed inside of the shmes dram access pipe at the bottom of the
shmes dram As taken from actual measurements the bottom of the shmes drain is
37 97 feet below a water level measunng point which is a notch on the side of the
Cell 2 shmes drain access pipe This means that the bottom of the slimes drain pool
and the location of the pump are one foot above the lowest point of the FML in Cell
2 which based on constmction reports is at a depth of 38 97 feet below the water
level measuring point on the slimes drain access pipe for Cell 2
(ill) The shmes drain pump in Cell 2 is activated and deactivated by a float
mechanism and water level probe system When the water level reaches the level of
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the float mechanism the pump is activated Pumping then occurs until the water level
reaches the lower probe which tums the pump off The lower probe is located one
foot above the bottom of the slimes drain standpipe and the float valve is located at
three feet above the bottom of the slimes drain standpipe The average wastewater
head in the Cell 2 shmes drain is therefore less than 3 feet and is below the phreatic
surface of tailmgs Cell 2 about 27 feet below the water level measuring point on the
shmes drain access pipe As a result there is a continuous flow of wastewater from
Cell 2 mto the shmes drain collection system Mill management considers that the
average allowable wastewater head in the Cell 2 shmes drain resulting from pumping
in this manner is satisfactory and is as low as reasonably achievable
(iv) The Cell 2 shmes drain pump is checked weekly to observe that it is operating and
that the water level probe and float mechanism are working properly which is noted
on the Weekly Tailmgs Inspection Form If at any time the pump is observed to be
not working properly it will be fixed or replaced withm 15 days
(v) Depth to wastewater in the Cell 2 shmes drain access pipe shall be monitored and
recorded weekly to determine maximum and nunimum fluid head before and after a
pumping cycle respectively The extension of the Cell 2 shmes drain access pipe did
not require any changes to the measurement procedure The surveyed measuring
point on the extended pipe is used as required The head measurements are
calculated in the same manner using the same procedures as those used prior to the
extension of the Cell 2 slimes dram access pipe however the total depth to the
bottom ofthe pipe is now 37 97 feet as noted on the conected form in Attachment A
All head measurements must be made from the same measuring point (the notch at
the north side of the access pipe) and made to the nearest 0 01 foot The results will
be recorded as depth in pipe measurements on the Weekly Tailings Inspection Form
The extension of the Cell 2 shmes access pipe has not changed the method of
calculation of the pre and post pump head calculations only the constant (Cell 2
shmes drain access pipe height) used in the calculation has changed The head is
calculated by subtracting the depth to liquid fi"om 37 97 feet rather than from the
previous measurement of 38 feet The weekly Tailings Inspection form included in
Attachment A has been changed to reflect the extension height
(vi) Effective July 11 2011 on a quarterly basis the shmes drain pump will be tumed off
and the wastewater in the shmes drain access pipe will be allowed to stabilize for at
least 90 hours Once the water level has stabilized (based on no change in water level
for three (3) successive readings taken no less than one (1) hour apart) the water level
ofthe wastewater will be measured and recorded as a depth in pipe measurement on
Quarterly Data form by measuring the depth to water below the water level
measuring point on the slimes drain access pipe
(vn) No process liquids shall be allowed to be discharged into Cell 2
(vill) If at any time the most recent average annual head in the Cell 2 shmes drain is
found to have increased above the average head for the previous calendar year the
Licensee will comply with the requirements of Part IG 3 of the GWDP including the
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requirement to provide notification to the Executive Secretary orally within 24 hours
followed by written notification
(ix)Because Cell 3 and Cell 4A are cunently active no pumping from the Cell 3 or Cell
4A shmes drain is authorized No pumping from the Cell 4B slimes drain will be
authorized once it is put into service and while it is active Prior to initiation of
tailings dewatering operations for Cell 3 Cell 4A or Cell 4B a similar procedure
will be developed for ensuring that average head elevations in the Cell 3 and Cell 4A
slimes drains are kept as low as reasonably achievable and that the Cell 3 Cell 4A
and Cell 4 slimes drains are inspected and the results reported in accordance with the
requirements of the permit
c) Wind Movement of Tailings
An evaluation of wind movement of tailings or dusting and control measures
shall be taken if needed
d) Tailings Wastewater Pool Elevation Monitoring
Solution elevation measurements m Cells 1 4A and 4B and Roberts Pond are to be taken
by survey on a weekly basis The beach area in Cell 4B with the maximum elevation is to
be taken by survey on a monthly basis when beaches are first observed as follows
(i) The survey will be performed by the Mill s Radiation Safety Officer or designee
(the Surveyor ) with the assistance of another Mill worker (the Assistant )
(ll) The survey will be perfonned using a survey instmment (the Survey Instmment )
accurate to 0 01 feet such as a Sokkai No B21 or equivalent together with a
survey rod (the Survey Rod ) having a visible scale in 0 01 foot increments
(iii)The Reference Points for Cells 1 Cell 4A and 4B and Roberts Pond are known
points established by professional survey For Cell 1 and Roberts Pond the
Reference Point is a wooden stake with a metal disk on it located on the southeast
comer of Cell 1 The elevation of the metal disk (the Reference Point
Elevation ) for Cell 1 and Roberts Pond is at 5 623 14 feet above mean sea level
( FMSL ) For Cell 4A and 4B the Reference Point is a piece of stamped metal
monument located next to the transformer on the south side of Cell 4A and 4B
The elevation at the top of this piece of rebar (the Reference Point Elevation for
Cell 4A and 4B) is 5600 49 fmsl The Surveyor will set up the Survey Instmment
in a location where both the applicable Reference Point and pond surface are
visible For Cell 1 and Roberts Pond this is typically on the road on the Cell 1
south dike between Cell 1 and Roberts Pond approximately 100 feet east of the
Cell 1/Roberts Pond Reference Point For Cell 4A and Cell 4B this is typically
on the south side of Cell 4A and 4B
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(iv) Once in location the Surveyor will ensure that the Survey Instmment is level by
centering the bubble in the level gauge on the Survey Instmment
(v) The Assistant will place the Survey Rod vertically on the Reference Point (on the
metal disk on the Cell 1/Roberts Pond Reference Point on the top of the rebar on
the Cell 4A and 4B Reference Point The Assistant will ensure that the Survey
Rod IS vertical by gently rocking the rod back and forth until the Surveyor has
established a level reading
(vi) The Surveyor will focus the cross hairs of the Survey Instmment on the scale on
the Survey Rod and record the number (the Reference Point Reading ) which
represents the number of feet the Survey Instmment is reading above the
Reference Point
(vii) The Assistant will then move to a designated location where the Survey Rod can
be placed on the surface of the main solution pond in the Cell 1 Cell 4A Cell
4B or Roberts Pond or the area of the beach in Cell 4B with the highest
elevation as the case may be These designated locations and the methods to be
used by the Assistant to consistently use the same locations are as follows
For a newly constmcted cell when the cell is first placed into operation the solution level is
typically zero feet above the FML or a nunimal elevation above the FML due to natural
precipitation For newly constmcted cells measurement of solution level will commence within
30 days of authorization for use Measurements will be conducted consistent with the procedures
in this DMT Plan and consistent with cunent Mill health and safety procedures The
measurements will be completed using survey equipment and the appropriate length survey rod
(either 25 or 45 )
A Pond Surface Measurements
I Cell 4A
The Assistant will walk down the slope in the northeast comer of Cell 4A and
place the Survey Rod at the liquid level
n Cell 4B
The Assistant will walk down the slope in the southeast comer of Cell 4B and
place the Survey Rod at the liquid level
m Cell 1
A mark has been painted on the north side of the ramp going to the pump
platform in Cell 1 The Assistant will place the Survey Rod against that mark
and hold the rod vertically with one end just touching the liquid surface and
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IV Roberts Pond
A mark has been painted on the railing of the pump stand in Roberts Pond The
Assistant will place the Survey Rod against that mark and hold the rod
vertically with one end just touching the liquid surface
Based on the foregoing methods the approximate coordinate locations for the
measuring points for Roberts Pond and the Cells are
Northing Easting
Roberts Pond 323 041 2 579 697
Cell 1 322 196 2 579 277
Cell 4A 320 300 2 579 360
Cell 4B 320 690 2 576 200
These coordinate locations may vary somewhat depending on solution elevations
in the Pond and Cells
B Cell 4B Beach Elevation
Beach elevations in Cell 4B will commence when beaches are first observed The
Assistant will place the Survey Rod at the point on the beach area of Cell 4B that
has the highest elevation If it is not clear which area of the beach has the highest
elevation then multiple points on the beach area will be surveyed until the
Surveyor is satisfied that the point on the Cell 4B beach area with the highest
elevation has been surveyed If it is clear that all points on the Cell 4B beach area
are below 5 593 FMSL then the Surveyor may rely on one survey point
(vill) The Assistant will hold the Survey Rod vertically with one end of the Survey
Rod just touching the pond surface The Assistant will ensure that the Survey
Rod IS vertical by gently rocking the rod back and forth until the Surveyor has
established a level reading
(ix)The Surveyor will focus the cross hairs of the Survey Instmment on the scale on
the Survey Rod and record the number (the Pond Surface Reading ) which
represents the number of feet the Survey Instmment is reading above the pond
surface level
The Surveyor will calculate the elevation of the pond surface as FSML by adding the
Reference Point Reading for the Cell or Roberts Pond as the case may be to the Reference
Point Elevation for the Cell or Roberts Pond and subtracting the Pond Surface Reading for
the Cell or Roberts Pond and will record the number accurate to 0 01 feet
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e) Decontamination Pads
(i) New Decontamination Pad
The New Decontamination Pad is located m the southeast comer of the ore
pad near the Mill s scale house
A In order to ensure that the primary containment of the New
Decontamination Pad water collection system has not been
compronused and to provide an inspection capability to detect
leakage from the pnmary containment vertical inspection portals
have been installed between the pnmary and secondary containments
B These portals will be visually observed on a weekly basis as a means
of detecting any leakage from the primary containment into the void
between the pnmary and secondary containment The depth to water
in each portal will be measured weekly by physically measunng the
depth to water with an electrical sounding tape/device All
measurements must be made from the same measuring point and be
made to the nearest 0 01 foot
C These inspections will be recorded on the Weekly Tailings Inspection
form
D The water level shall not exceed 0 10 foot above the concrete floor in
any standpipe at any time This will be determined by subtracting the
weekly depth to water measurement from the distance from the
measuring point in the standpipe to the dry concrete floor The depth
to water from the top (elevation 5589 8 feet amsl) of any of the three
(3) observation ports to the standing water shall be no less than 6 2
feet Depths less than 6 2 feet shall indicate more that 0 1 foot of
standing water above the concrete floor (elev 5583 5 feet amsl) and
shall indicate a leak in the primary containment
E Any observation of fluid between the primary and secondary
containments will be reported to the Radiation Safety Officer (RSO)
F In addition to inspection of the water levels in the standpipes the
New Decontamination Pad including the concrete integrity of the
exposed surfaces of the pad will be inspected on a weekly basis Any
soil and debris will be removed from the New Decontaimnation Pad
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immediately prior to inspection of the concrete wash pad for cracking
Observations will be made of the cunent condition of the New
Decontamination Pad Any abnormalities relating to the pad and any
damage to the concrete wash surface of the pad will be noted on the
Weekly Tailings Inspection form If there are any cracks greater than
1/8 inch separation (width) the RSO must be contacted The RSO
will have the responsibility to cease activities and have the cracks
repaired
(ll) Existing Decontamination Pad
The Existing Decontamination Pad is located between the northwest comer of the
Mill s maintenance shop and the ore feeding grizzly
A The Existing Decontaimnation Pad will be inspected on a weekly
basis Any soil and debris will be removed from the Existing
Decontanunation Pad immediately prior to inspection of the concrete
wash pad for cracking Observations will be made of the cunent
condition of the Existing Decontamination Pad including the
concrete integrity of the exposed surfaces of the pad Any
abnormalities relating to the pad and any damage or cracks on the
concrete wash surface of the pad will be noted on the Weekly
Tailmgs Inspection form If there are any cracks greater than 1/8 inch
separation (width) the RSO must be contacted The RSO will have
the responsibility to cease activities and have the cracks repaired
/) Summary
In addition the weekly inspection should summarize all activities conceming the
tailings area for that particular week
Results ofthe weekly tailmgs inspection are recorded on the Weekly Tailings and DMT Inspection
form An example of the Weekly Tailings and DMT Inspection form is provided in Appendix A
3 2 Weeklv Inspection of Solution Levels m Roberts Pond
On a weekly basis solution elevations are taken on Roberts Pond in accordance with the procedures
set out in Section 3 1 d) above The Weekly solution level in Roberts Pond is recorded on the
Weekly Tailings and DMT Inspection form Based on historical observations the FML at the Pond
Surface Reading area for Roberts Pond is approximately six inches above the lowest point on the
pond s FML If the pond solution elevation at the Pond Surface Reading area is at or below the FML
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for that area the pond will be recorded as being dry
3 3 Weeklv Feedstock Storage Area Inspections
Weekly feedstock storage area inspections will be performed by the Radiation Safety Department to
confirm that
a) the bulk feedstock materials are stored and maintained within the defined area descnbed in
the GWDP as indicated on the map attached hereto as Appendix D
b) a 4 ft buffer is mainteuned at the periphery of the storage area which is absent bulk material
in order to assure that the materials do not encroach upon the boundary of the storage area
and
c) all altemate feedstock located outside the defined Feedstock Area are maintained within
water tight containers
The results of this inspection will be recorded on the Ore Storage/Sample Plant Weekly Inspection
Report a copy of which is contained in Appendix A Any variance in stored matenals from this
requirement or observed leaking altemate feedstock dmms or other containers will be brought to the
attention of Mill Management and rectified within 15 days
4 MONTHLY TAILINGS INSPECTION
Monthly tailings inspections will be performed by the Radiation Safety Officer or his designee from
the Radiation Safety Department and recorded on the Monthly Inspection Data form an example of
which IS contained in Appendix A Monthly inspections are to be performed no sooner than 14 days
since the last monthly tailings inspection and can be conducted concunently with the quarterly
tailmgs inspection when applicable The following items are to be inspected
a) Tailings Slurry Pipeline
When the Mill is operating the slurry pipeline will be visually inspected at key
locations to determine pipe wear The cntical points of the pipe include bends slope
changes valves and junctions which are cntical to dike stability These locations to
be monitored will be detemuned by the Radiation Safety Officer or his designee from
the Radiation Safety Department during the Mill mn
b) Diversion Ditches
Diversion ditches 1 2 and 3 shall be monitored monthly for sloughing erosion
undesirable vegetation and obstmction of flow Diversion berm 2 should be checked
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for stability and signs of distress
c) Sedimentation Pond
Activities around the Mill and facilities area sedimentation pond shall be summanzed
for the month
d) Overspray Dust Minimization
The inspection shall mclude an evaluation of overspray minimization if applicable
This entails ensuring that the overspray system is functioning properly In the event
that overspray is earned more than 50 feet from the cell the overspray system should
be immediately shut off
e) Remarks
A section is included on the Monthly Inspection Data form for remarks in which
recommendations can be made or observations of concem can be documented
f) Summary of Daily Weekly and Quarterly Inspections
The monthly inspection will also summanze the daily weekly and if applicable
quarterly tailings inspections for the specific month
In addition settlement monitors are typically surveyed monthly and the results reported on the
Monthly Inspection Data form
5 QUARTERLY TAILINGS INSPECTION
The quarterly tailings inspection is performed by the Radiation Safety Officer or his designee from
the Radiation Safety Department having the training specified m Section 2 4 above once per
calendar quarter A quarterly inspection should be performed no sooner than 45 days since the
previous quarterly inspection was performed
Each quarterly inspection shall include an Embankment Inspection an Operations/Maintenance
Review a Constmction Review and a Summary as follows
a) Embankment Inspection
The Embankment inspection involves a visual inspection of the crest slope and toe
of each dike for movement seepage severe erosion subsidence shrinkage cracks
and exposed Imer
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b) Operations/Maintenance Review
The Operations/Maintenance Review consists of reviewing Operations and
Maintenance activities pertaining to the tailmgs area on a quarterly basis
c) Construction Review
The Constmction Review consists of reviewing any constmction changes or
modifications made to the tailings area on a quarterly basis
d) An estimate of the percentage of the tailmgs beach surface area and solution pool
area is made including estimates of solutions cover areas and tailmgs sands for
Cells 3 4Aand4B
e) Summary
The summary will include all major activities or observations noted around the
tailmgs area on a quarterly basis
If any of these conditions are noted the conditions and conective measures taken should be
documented m the Quarterly Inspection Data form An example of the Quarterly Inspection Data
form IS provided in Appendix A
6 ANNUAL EVALUATIONS
The following annual evaluations shall be performed
6 1 Annual Technical Evaluation
An annual technical evaluation of the tailings management system is performed by a registered
professional engineer (PE) who has experience and training m the area of geotechnical aspects of
retention stmctures The technical evaluation includes an on site inspection of the tailings
management system and a thorough review of all tailings records for the past year The Technical
Evaluation also includes a review and summary of the annual movement monitor survey (see Section
5 2 below)
All tailings cells and conesponding dikes will be inspected for signs of erosion subsidence
shnnkage and seepage The drainage ditches will be inspected to evaluate surface water control
stmctures
In the event tailings capacity evaluations (as per SOP PBL 3) were performed for the receipt of
altemate feed material during the year the capacity evaluation forms and associated calculation
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sheets will be reviewed to ensure that the maximum tailings capacity estimate is accurate The
amount of tailings added to the system since the last evaluation will also be calculated to determine
the estimated capacity at the time of the evaluation
Tailings inspection records will consist of daily weekly monthly and quarterly tailings inspections
These inspection records will be evaluated to determine if any freeboard limits are being
approached Records will also be reviewed to summarize observations of potential concern The
evaluation also involves discussion with the Environmental and/or Radiation Technician and the
Radiation Safety Officer regarding activities around the tailings area for the past year During the
annual inspection photographs of the tailings area will be taken The training of individuals will be
reviewed as a part of the Annual Technical Evaluation
The registered engineer will obtain copies of selected tailings inspections along with the monthly
and quarterly summaries of observations of concem and the conective actions taken These copies
will then be included in the Annual Technical Evaluation Report
The Annual Technical Evaluation Report must be submitted by November 15'** of every year to the
Executive Secretary
6 2 Movement Monitors
A movement monitor survey is to be conducted by a licensed surveyor annually during the second
quarter of each year The movement monitor survey consists of surveying momtors along dikes 3 S
4A W and 4A S to detect any possible settlement or movement of the dikes The data generated
from this survey is reviewed and incorporated into the Annual Technical Evaluation Report of the
tailings management system
6 3 Freeboard Limits
The freeboard limits set out in this Section are intended to capture the Local 6 hour Probable
Maximum Precipitation (PMP) event which was detemuned in the January 10 1990 Drainage
Report (the Drainage Report ) for the White Mesa site to be 10 inches
The flood volume from the PMP event over the Cell 1 pond area plus the adjacent drainage areas
was calculated in the Drainage Report to be 103 acre feet of water with a wave mn up factor of
0 90 feet
The flood volume from the PMP event over the Cell 2 and Cell 3 pond areas plus the adjacent
drainage areas was calculated in the Drainage Report to be 123 4 acre feet of water
The flood volume from the PMP event over the Cell 4A area was calculated in the Drainage
Report to be 36 acre feet of water (40 acres plus the adjacent drainage area of 3 25 acres) times
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the PMP of 10 inches) with a wave mn up factor of 0 77 feet
The flood volume from the PMP event over the Cell 4B area has been calculated to be 38 1 acre
feet of water (40 acres plus the adjacent drainage area of 5 72 acres) times the PMP of 10
inches with a wave mn up factor of 0 77 feet
The total pool surface area in Cell 1 is 52 9 acres in Cell 4A is 40 acres and in Cell 4B is 40
acres The top of the flexible membrane liner ( FML ) for Cell 1 is 5 618 2 FMSL for Cell 4A
is 5 598 5 FMSL and for Cell 4B is 5600 4 FMSL
Based on the foregoing the freeboard Imuts for the Mill s tailings cells will be set as follows
63 1 Cell 1
The freeboard limit for Cell 1 will be set at 5 615 4 FMSL This will allow Cell 1 to capture all of
the PMP volume associated with Cell 1 The total volume requirement for Cell 1 is 103 acre feet
divided by 52 9 acres equals 1 95 feet plus the wave mn up factor of0 90 feet equals 2 85 feet The
freeboard linut is then 5 618 2 FMSL minus 2 85 feet equals 5 615 4 FMSL Under Radioactive
Matenals License condition 10 3 this freeboard limit is set and is not recalculated annually
632 Cell 2
The freeboard Imut for Cell 2 is inapplicable since Cell 2 is filled with solids All of the PMP
volume associated with Cell 2 will be attributed to Cell 4A (and/or any future tailings cells)
63 3 Cell 3
The freeboard limit for Cell 3 is inapplicable since Cell 3 is close to being filled with solids and all
of the PMP flood volume associated with Cell 3 will be attributed to Cell 4B (and/or any future
tailings cells)
634 Cell 4A
The freeboard limit for Cell 4A is inapplicable since all of the PMP flood volume associated with
Cell 4A will be attributed to Cell 4B A spillway has been added to Cell 4A to allow overflow into
Cell 4B
635 Cell 4B
The freeboard limit for Cell 4B will be set assuming that the total PMP volume for Cells 2 3 4A
and 4B of 159 4 acre feet will be accommodated in Cell 4B The procedure for calculating the
freeboard limit for Cell 4B is as follows
(a) When the Pool Surface Area is 40 Acres
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When the pool surface area in Cell 4B is 40 acres (i e when there are no beaches) the freeboard
linut for Cell 4B will be 5 594 6FMSL which is 5 7 feet below the FML This freeboard value was
developed as follows
PMP Flood Volume 38 1 acre feet
Overflow from Cell 4A assuming no storage m Cell 3 or 4A 159 4 acre feet
Sum of PMP volume and overflow volume 197 5 acre feet
Depth to store PMP an overflow volume
= 197 5 acre feet/40 acres 4 9 feet
Wave mn up factor 0 77 feet
Total required freeboard 5 7 feet
(all values in the above calculation have been rounded to the nearest one tenth of afoot)
(b) When the Maximum Elevation ofthe Beach Area is 5 594 FMSL or Less
When the maximum elevation of the beach area in Cell 4B is 5594 FMSL or less then the freeboard
limit will be 5 594 6 FMSL which is the same as m (a) above This allows for the situation where
there may be beaches but these beaches are at a lower elevation than the freeboard limit established
in (a) above and there is therefore ample freeboard above the beaches to hold the maximum PMP
volume The maximum elevation of the beach area will be determined by monthly surveys
performed by Mill personnel in accordance with the Mill s DMT Plan
(c) When the Maximum Elevation of the Beach Area First Exceeds 5 594 FMSL
When the maximum elevation of the beach area in Cell 4B first exceeds 5 594 FMSL then the
freeboard limit for the remainder of the ensuing year (period t=0) (until the next November 1) will be
calculated when that elevation is first exceeded (the Initial Calculation Date ) as follows
i) The total number of dry tons of tailings that have historically been deposited into Cell
4B pnor to the Initial Calculation Date ( To ) will be determined
II) The expected number of dry tons to be deposited into Cell 4B for the remainder of the
ensuing year (up to the next November 1) based on production estimates for that
period ( Ao* ) will be detemuned
III) Ao* will be grossed up by a safety factor of 150% to allow for a potential
underestimation of the number of tons that will be deposited m the cell during the
remainder of the ensuing year This grossed up number can be refened to as the
modeled tonnage for the period
IV) The total design tailings solid storage capacity of Cell 4B will be accepted as
2 094 000 dry tons of tailings
v) The available remaining space in Cell 4B for solids as at the Initial Calculation Date
will be calculated as 2 094 000 dry tons minus To
VI) The reduction in the pool surface area for the remainder of the ensuing year will be
assumed to be directly proportional to the reduction in the available space in Cell 4B
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for solids That is the reduced pool surface area for period t=0 ( RPAo ) after the
reduction will be calculated to be
(1 - (Ao* X 1 5) / (2 094 000 To)) x 40 acres = RPAo
vn) The required freeboard for Cell 4B for the remainder of the period t=0 can be
calculated in feet to be the wave mn up factor for Cell 4B of 0 77 feet plus the
quotient of 197 5 acre feet divided by the RPAo The freeboard Imut for Cell 4B for
the remainder of period t=0 would then be the elevation of the FML for Cell 4B of
5594 0 FMSL less this required freeboard amount rounded to the nearest one tenth of
afoot and
VIII) The foregoing calculations will be performed at the Initial Calculation Date and the
resulting freeboard linut will persist until the next November 1
An example of this calculation is set out m Appendix F
(d) Annual Freeboard Calculation When the Maximum Elevation ofthe Beach Area Exceeds
5 594 FMSL
On November 1 of each year (the Annual Calculation Date ) the reduction in pool area for the
ensuing year (refened to as period t) will be calculated by
i) First calculating the Adjusted Reduced Pool Area for the previous period (ARPAt i)
to reflect actual tonnages deposited in Cell 4B for the previous period (period t 1)
The RPAt 1 used for the previous period was based on expected tonnages for penod t
1 grossed up by a safety factor The ARP At i is merely the RPA that would have
been used for period t 1 had the actual tonnages for year t 1 been known at the outset
of period t 1 and had the RPA been calculated based on the actual tonnages for penod
t 1 This allows the freeboard calculations to be conected each year to take into
account actual tonnages deposited m the cell as of the date of the calculation The
ARP At 1 can be calculated using the following formula
(1 - At 1 / (2 094 000 - Tt i)) X ARPAt 2 = ARPAt 1
Where
• At 1 IS the actual number of dry tons of tailings solids deposited in Cell 4B
dunng period t 1
• Tt 1 IS the actual number of dry tons of tailings solids historically deposited in
Cell 4B pnor to the beginning of penod t 1 and
• ARPAt 2 IS the Adjusted Reduced Pool Area for penod t 2 If period t 2
started at the Initial Calculation Date then ARPAt 2 is 40 acres
11) Once the ARPAt 1 for the previous penod (period t 1) has been calculated the RPA
for the subject period (period t) can be calculated as follows
(1 - (At* X 1 5) / (2 094 000 Tt)) x ARPAt 1 = RPAt
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Where
• At* IS the expected number of dry tons of tailings to be deposited into Cell 4B
for the ensuing year (period t) based on production estimates for the year (as
can be seen from the foregoing formula this expected number is grossed up
by a safety factor of 1 5)
• Tt is the actual number of dry tons of tailings solids historically deposited in
Cell 4B prior to the beginning of penod t and
• ARPAt 1 IS the Adjusted Reduced Pool Area for period t 1 which is the pool
surface area for the previous period (penod t 1) that should have applied
during that penod had modeled tonnages (i e expected tonnages grossed up
by the 150% safety factor) equaled actual tonnages for the period
III) The required freeboard for penod t can be calculated in feet to be the wave mn up
factor for Cell 4B of 0 77 feet plus the quotient of 197 5 acre feet divided by the RPAt
The freeboard limit for Cell 4B for period t would then be the elevation of the FML
for Cell 4B of 5594 0 FMSL less this required freeboard amount rounded to the
nearest one tenth of a foot and
iv) The foregoing calculations will be performed at the Annual Calculation Date for
period t and the resulting freeboard linut will persist until the next Annual Calculation
Date for period t+1
An example of this calculation is set out in Appendix F
(e) When a Spillway is Added to Cell 4B that Allows Overflow Into a New Tailings Cell
When a spillway is added between Cell 4B and a new tailings cell then if an approved freeboard
limit calculation method for the new cell is set to cover the entire PMP event for Cells 2 3 4A 4B
and the new tailings cell the freeboard linut for Cell 4B will be inapplicable except for approved
provisions to prevent storm water mnoff from overtopping dikes
6 3 6 Roberts Pond
The freeboard limit for Roberts Pond is a liquid maximum elevation of 5 624 0 feet above mean sea
level as specified m the GWDP
6 4 Annual Leak Detection Fluid Samples
In the event solution has been detected in a leak detection system a sample will be collected on an
annual basis This sample will be analyzed according to the conditions set forth in License
Condition 11 3 C The results of the analysis will be reviewed to detemune the origin of the
solution
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6 5 Annual Inspection of the Decontamination Pads
a) New Decontamination Pad
During the second quarter of each year the New Decontamination Pad will be taken out of service
and inspected to ensure the integrity of the wash pad s exposed concrete surface If any
abnormalities are identified i e cracks in the concrete with greater than 1/8 inch separation (width)
or any significant deterioration or damage of the pad surface repairs will be made pnor to resunung
the use of the facility All inspection findings and any repairs required shall be documented on the
Annual Decontanunation Pad Inspection form The inspection findings any repairs required and
repairs completed shall be sununanzed in the 2"^ Quarter DMT Monitoring Report due September 1
of each calendar year
b) Existing Decontanunation Pad
During the second quarter of each year the Existing Decontanunation Pad will be taken out of
service and inspected to ensure the integrity of the steel tank Once the water and any sediment
present is removed from the steel tank containment the walls and bottom of the tank will be
visually inspected for any areas of damage cracks or bubbling indicating conosion that may
have occuned since the last mspection If any abnormalities are identified defects or damage
will be reported to Mill management and repairs will be made prior to resunung the use of the
facility All inspection findings and any repairs required shall be documented on the Annual
Decontamination Pad Inspection form A record of the repairs will be maintained as a part of the
Annual Inspection records at the Mill site The inspection findings any repairs required and
repairs completed shall be summarized in the 2nd Quarter DMT Monitonng Report due
September 1 of each calendar year
7 OTHER INSPECTIONS
All daily weekly monthly quarterly and annual inspections and evaluations should be performed as
specified m Sections 2 3 4 5 and 6 above However additional inspections should be conducted
after any significant storm or significant natural or man made event occurs
8 REPORTING REQUIREMENTS
In addition to the Daily Inspection Data Weekly Tailings Inspection Monthly Inspection Data and
Quarterly Inspection Data forms included as Appendix A and described in Sections 2 3 4 and 5
respectively and the Operating Foreman s Daily Inspection and Weekly Mill Inspection forms
described m Sections 2 and 3 respectively the following additional reports shall also be prepared
8 1 Monthlv Tailings Reports
Monthly tailings reports are prepared every month and summarize the previous month s activities
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around the tailings area If not prepared by the Radiation Safety Officer the report shall be
submitted to the Radiation Safety Officer for review The Mill Manager will review the report as
well before the report is filed m the Mill Central File The report will contain a summary of
observations of concern noted on the daily and weekly tailings inspections Conective measures
taken during the month will be documented along with the observations where appropriate All daily
and weekly tailings inspection forms will be attached to the report A monthly inspection form will
also be attached Quarterly inspection forms will accompany the report when applicable The report
will be signed and dated by the preparer m addition to the Radiation Safety Officer and the Mill
Manager
82 DMT Reports
Quarterly reports of DMT monitonng activities which will include the following information will
be provided to the Executive Secretary on the schedule provided in Table 5 of the GWDP
a) On a quarterly basis all required information required by Part 1 F 2 of the GWDP
relating to the inspections described in Section 3 1(b) (Shmes Dram Water Level
Monitonng) 3 1(d) (Tailings Wastewater Pool and Beach Area Elevation
Monitoring) 3 2 (Weekly Inspection of Solution Levels in Roberts Pond) and 3 3
(Weekly Feedstock Storage Area Inspections)
b) On a quarterly basis a summary of the weekly water level (depth) inspections for
the quarter for the presence of fluid in all three vertical inspection portals for each
of the three chambers in the concrete settling tank system for the New
Decontanunation Pad which will include a table indicating the water level
measurements in each portal dunng the quarter
c) With respect to the annual inspection of the New Decontamination Pad descnbed
m Section 6 5(a) the inspection findings any repairs required and repairs
completed shall be summarized in the 2"^ Quarter report due September 1 of
each calendar year
d) With respect to the annual inspection of the Existing Decontanunation Pad
described in Section 6 5(b) the inspection findings any repairs required and
repairs completed shall be summarized in the 2"** Quarter report due September 1
of each calendar year and
e) An annual summary and graph for each calendar year of the depth to wastewater
in the Cell 2 shmes dram must be included in the fourth quarter report After the
first year and beginning in 2008 quarterly reports shall include both the cunent
year monthly values and a graphic comparison to the previous year
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APPENDIX A
FORMS
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Page 27 of 53
APPENDIX A (CONT)
DAILY INSPECTION DATA
Inspector
Date
Accompanied by
Time
Any Item not OK must be documented A check mark = OK X = Action Required
I TAILINGS SLURRY TRANSPORT SYSTEM
Inspection Items Conditions of Potential Concem Cell 1 Cell 2 Cell 3 Cell 4A Cell 4B
Slurry Pipehne Leaks Damage Blockage Sharp Bends
Pipeline Joints Leaks Loose Connections
Pipebne Supports Damage Loss of Support
Valves Leaks Blocked Closed
Point(s) of Discharge Improper Location or Onentation
II OPERATIONAL SYSTEMS
Inspection Items Conditions of Potential Concem Cell 1 Cell 2 Cell 3 Cell 4A Cell 4B
Water Level Greater Than Operating Level Large Change
Since Previous Inspection
Beach Cracks Severe Erosion Subsidence
Liner and Cover Erosion of cover Exposure of Liner
Lmer Observable Liner Damage
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Page 28 of 53
III DIKES AND EMBANKMENTS
Inspection Items Conditions of Potential Dike 1 I Dike 1 Dike 2 Dike 3 Dike Dike Dike
Concem lA 4AS 4AE 4B S
Slopes Sloughs or Sliding Cracks No No No No
Bulges Subsidence Severe visible visible visible visible
Erosion Moist Areas Areas slope or slope or slope or slope or
of Seepage Outbreak dike to dike to dike to dike to
inspect inspect inspect inspect
Crest Cracks Subsidence Severe No No No No
Erosion visible visible visible visible
slope or slope or slope or slope or
dike to dike to dike to dike to
inspect inspect inspect inspect
IV FLOW RATES
Slurry Line(s) Pond Retum S X Tails Sprav Svstem
GPM
V PHYSICAL INSPECTION OF SLURRY LINES(S)
Walked to Discharge Point
Observed Entire Discharge Line
Yes
Yes
_No
No
VI DUST CONTROL
Cell 2 Cell 3 Cell 4A Cell 4B
Dusting
Wind Movement of Tailings
Precipitation inches liquid
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Page 29 of 53
General Meteorological conditions
Vn DAILY LEAK DETECTION CHECK
Celll Cell 2 Cell 3 Cell 4A Cell 4B
Leak
Detection
System
Checked
Checked Checked Checked Checked Checked Leak
Detection
System
Checked
Wet Drv Wet Drv Wet Drv Wet Drv Wet Drv
Leak
Detection
System
Checked
Initial level Initial level Initial level Initial level Initial level
Leak
Detection
System
Checked
Final
level
Final
level
Final
level
Final
level
Final
level
Leak
Detection
System
Checked
Gal pumped Gal pumped Gal pumped Gal pumped Gal pumped
Vni OBSERVATIONS OF POTENTIAL CONCERN Action Required
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Tailings Daily Inspection Repoit
Tailmgs Sluny Dischaige Location
7-H (4-1
C O
S o
O 03
CELL NO 1
Dike 11
MILL SITE
>
ts
t f
c
c« 2
O 1
2 2
^3
c
B
D
^ PQ
CELL NO 2
Filled
CELL NO 4B
CELL NO 4A /
Date
Inspectoi / .0^
N
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Book 11 Envu-onmental Protection Manual Section 3 1 Page 31 of 53
APPENDIX A (CONT)
DENISON MINES (USA) CORP
WEEKLY TAILINGS INSPECTION
Date Inspectors
1 Pond and Beach Cell 1 (a) Pond Solution Elevation
elevations (msl ft)
(b) FML Bottom Elevation 5597.
(c) Depth of Water above FML ((a) (b))
Cell4A (a)Pond Solution Elevation
(b) FML Bottom Elevation 5555 14_
(c) Depth of Water above FML ((a) (b))
Cell 4B (a)Pond Solution Elevation
(b) FML Bottom Elevation 5557 50
(c) Depth of Water above FML ((a) (b))
(d) Elevation of Beach Area with Highest Elevation
(monthly)
Roberts
Pond (a)Pond Solution Elevation
(b) FML Bottom Elevation 5612 3.
(c) Depth of Water above FML ((a) (b))
2 Shmes Dram Liquid Levels Cell 2 Pump functioning properly
_Depth to Liquid pre pump
_Depth to Liquid Post pump
(all measurements are depth m pipe)
Pre pump head is 37 97 Depth to Liquid Pre
pump =
Post pump head is 37 97 -Depth to Liquid Post
pump =
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3 Leak Detection Systems
(Same data as Daily Inspection Form Record data on daily form)
Observation
New Decon Pad.
Portal 1
New Decon Pad,
Portal 2
New Decon Pad
Portal 3
Is LDS (Portal)
wet or dry*^
.wet dry .wet ^dry .wet dry
If wet Record
liquid level Liquid
Ft to
Liquid
Ft to
Liquid
Ft to
If wet Report to
RSO
4 Taihngs Area Inspection (Note dispersal of blowing tailings)
5 Control Methods Implemented
6 Remarks
7 Designated Disposal Area for Non Tailings Mill Waste (awaiting DRC approval)
* Does Level exceed 12 inches above the lowest point on the bottom flexible membrane hner (solution
elevation of 5556 14 amsl for Cell 4A and 5558 50 for Cell 4B)'? no yes
If Cell 4A leak detection system level exceeds 12 inches above the lowest point on the bottom flexible
membrane liner (elevation 5556 14 amsl) notify supervisor or Mill manager immediately
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Page 33 of 53
APPENDIX A (CONT)
MONTHLY INSPECTION DATA
Inspector
Date
1 Slurry Pipehne
2 Diversion Ditches and Diversion Berm
Observation
Diversion Ditch 1 Diversion Ditch 2 Diversion Ditch 3 Diversion Berm 2
Diversion Ditches
Sloughing
Erosion
Undesirable
Vegetation
Obstruction of Flow
Diversion Berm
Stability Issues
Signs of Distress
^es_
_yes_
^es_
_yes.
.no
.no
no
no
_yes_
^es_
_yes_
_yes_
.no
.no
.no
no
_yes.
_yes_
_yes.
_yes_
.no
.no
.no
no
_yes.
_yes_
_no
no
Comments
3 Summary of Activities Around Sedimentation Pond
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4 Overspray Dust Mimmization
Overspray system functioning properly _yes.
Overspray earned more than 50 feet from the cell
If yes was system immediately shut off^
Comments
no
0^es_
_yes.
no
no
5 Remarks
6 Settlement Monitors
Cell 2 Wl
Cell 2 W2
Cell 2 W3
Cell 2 W4
Cell 2W7 C
Cell 2 W7N
Cell2W6C
Cell 4A Toe
Cell 3 2C
Cell 3 3S
Cell 3 4N
Cell 3 7C
Cell 3 SC
Cell 2W3 S
Cell 2E1 N
Cell 2E1 IS
Cell 2E1 2S
Cell 2 East
Cell 2 W7S
Cell 2 W6S
Cell 2 W4S
Cell 3 2S _
Cell 3 3C _
Cell 3 6N _
Cell 3 7N _
Cell 3 8N
Cell 3 IN _
Cell 3 IC _
Cell 3 IS _
Cell 3 2N _
Cell 2W5 N
Cell 2 W6N
Cell 2 W4N
Cell 2 W5C
Cell 2 W5S
Cell3 3N _
Cell 3 7S _
Cell 3 8S
7 Movement Monitors
surfaces)''
(Is there visible damage to any movement momtor or to adjacent
8 Summary of Daily, Weekly and Quarterly Inspections
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Page 35 of 53
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Page 36 of 53
APPENDIX A (CONT)
WHITE MESA MILL
TAILINGS MANAGEMENT SYSTEM
QUARTERLY INSPECTION DATA
Inspector
Date
1 Embankment Inspection
2 Operations/Mamtenance Review
3 Construction Activities
4 Estimated Areas
Cell 3 Cell 4A Cell 4B
Estimated percent of beach surface area
Estimated percent of solution pool area
Estimated percent of cover area
Comments
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APPENDIX A (CONT)
ORE STORAGE/SAMPLE PLANT WEEKLY INSPECTION REPORT
Week of through Date of Inspection
Inspector
Weather conditions for the week
Blowing dust conditions for the week
Corrective actions needed or taken for the week
Are all bulk feedstock matenals stored in the area indicated on the attached diagram
yes no
comments
Are all altemate feedstock matenals located outside the area indicated on the attached diagram maintained
within water tight containers
yes no
comments (e g conditions of containers)
Are all sumps and low lying areas free of standing solutions'^
Yes No
If No how was the situation corrected supervisor contacted and correction date*^
Is there free standing water or water running off of the feedstock stockpiles'^
Yes No
Comments
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Other comments
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APPENDIX A (CONT)
ANNUAL DECONTAMINATION PAD INSPECTION
Date of Inspection
Inspector
New Decontamination Pad
Are there any cracks on the wash pad surface greater than 1/8 inch of separation'? Yes ^No
Is there any significant detenoration or damage of the pad surface*? Yes No
Findings
Repair Work Required
Existing Decontamination Pad
Were there any observed problems with the steel tank? Yes ^No
Findings
Repair Work Required
Note For the annual inspection of the both the Existing and New Decontanunation Pads the
annual inspection findings any repairs required and repairs completed along with a summary of
the weekly inspections shall be discussed in the 2"^ Quarter report due September 1 of each
calendar year
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Book 11 Environmental Protection Manual Section 3 1 Page 40 of 53
APPENDIX B
8 3 TAILINGS INSPECTOR TRAINING
This document provides the traimng necessary for qualifying management designated individuals for
conducting daily tailings inspections Training information is presented by the Radiation Safety
Officer or designee from the Environmental Department Daily tailings inspections are conducted in
accordance with the White Mesa Mill Tailings Management System and Discharge Minimization
Technology (DMT) Monitoring Plan The Radiation Safety Officer or designee from the Radiation
Safety Department is responsible for perfomung monthly and quarterly tailings inspections Tailings
inspection forms will be included in the monthly tailings inspection reports which summarize the
conditions activities and areas of concern regarding the tailmgs areas
Notifications
The inspector is required to record whether all inspection items are normal (satisfactory requinng no
action) or that conditions of potential concem exist (requinng action) A check mark indicates no
action required If conditions of potential concem exist the inspector should mark an X in the area
the condition pertains to note the condition and specify the conective action to be taken If an
observable concem is made it should be noted on the tailings report until the conective action is
taken and the concem is remedied The dates of all conective actions should be noted on the reports
as well
Any major catastrophic events or conditions pertaining to the tailings area should be reported
immediately to the Mill Manager or the Radiation Safety Officer one of whom will notify Corporate
Management If dam failure occurs notify your supervisor and the Mill Manager immediately The
Mill Manager will then notify Corporate Management MSHA (303 231 5465) and the State of
Utah Division of Dam Safety (801 538 7200)
Inspections
All areas of the tailings disposal system are routinely patrolled and visible observations are to be
noted on a daily tailings inspection form Refer to Appendix A for an example of the daily tailings
inspection form The inspection form consists of three pages and is summarized as follows
1 Tailings Slurry Transport System
The slurry pipeline IS to be inspected for leaks damage and sharp bends The pipeline joints
are to be monitored for leaks and loose connections The pipeline supports are to be
inspected for damage and loss of support Valves are also to be inspected particularly for
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leaks blocked valves and closed valves Points of discharge need to be inspected for
improper location and orientation
Operational Systems
Operating systems including water levels beach liners and covered areas are items to be
inspected and noted on the daily inspection forms Sudden changes in water levels
previously observed or water levels exceeding the operating level of a pond are potential
areas of concem and should be noted Beach areas that are observed as having cracks severe
erosion or cavities are also items that require investigation and notation on daily forms
Exposed liner or absence of cover from erosion are potential items of concern for ponds and
covered areas These should also be noted on the daily inspection form
Cells 1 3 4A and 4B solution levels are to be monitored closely for conditions nearing
maximum operating level and for large changes m the water level since the last inspection
All pumping activities affecting the water level will be documented In Cells 1 and 3 the
PVC liner needs to be monitored closely for exposed liner especially after storm events It is
important to cover exposed liner immediately as exposure to sunlight will cause degradation
of the PVC liner Small areas of exposed lmer should be covered by hand Large sections of
exposed lmer will require the use of heavy equipment
These conditions are considered senous and require immediate action After these conditions
have been noted to the Radiation Safety Officer a work order will be written by the
Radiation Safety Officer and tumed into the Maintenance Department All such repairs
should be noted in the report and should contain the start and finish date of the repairs
Dikes and Embankments
Inspection items include the slopes and the crests of each dike For slopes areas of concem
are sloughs or sliding cracks bulges subsidence severe erosion moist areas and areas of
seepage outbreak For crests areas of concem are cracks subsidence and severe erosion
When any of these conditions are noted an X mark should be placed in the section marked
for that dike
In addition the dikes m particular dikes 4A S 4A E and 4B S should be inspected closely
for mice holes and more importantly for prairie dog holes as the praine dogs are likely to
bunow in deep possibly to the lmer If any of these conditions exist the inspection report
should be marked accordingly
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4 Flow Rates
Presence of all flows in and out of the cells should be noted Flow rates are to be estimated
in gallons per nunute (GPM) Rates need to be detemuned for slurry lines pond retum SX
tails and the spray system During non operational modes the flow rate column should be
marked as 0 The same holds tme when the spray system is not utilized
5 Physical Inspection of Slurry Line(s)
A physical inspection of all slurry lines has to be made every 4 hours during operation of the
null If possible the inspection should include observation of the entire discharge line and
discharge spill point into the cell If fill to elevation flags are m place the tailings and
build up IS to be monitored and controlled so as to not cover the flags
6 Dust Control
Dusting and wind movement of tailings should be noted for Cells 2 3 4A and 4B Other
observations to be noted include a brief description of present weather conditions and a
record of any precipitation received Any dusting or wind movement of tailings should be
documented In addition an estimate should be made for wind speed at the time of the
observed dusting or wind movement of tailings
The Radiation Safety Department measures precipitation on a daily basis Daily
measurements should be made as near to 8 00 a m as possible every day Weekend
measurements will be taken by Environmental Health and Safety personnel as close to 8 00
a m as possible All snow or ice should be melted before a reading is taken
7 Observations of Potential Concern
All observations of concem during the inspection should be noted in this section Conective
action should follow each area of concem noted All work orders issued contacts or
notifications made should be noted in this section as well It is important to document all
these Items in order to assure that the tailings management system records are complete and
accurate
8 Map of Tailmgs Cells
The last section of the inspection involves drawing as accurately as possible the following
Items where applicable
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1 Cover area
2 Beach/tailing sands area
3 Solution as it exists
4 Pump lines
5 Activities around tailings cell (i e hauling trash to the dump lmer repairs etc )
6 Slurry discharge when operating
7 Over spray system when operating
9 Safety Rules
All safety mles applicable to the mill are applicable when m the tailings area These mles
meet the required MSHA regulations for the tailmgs area Please pay particular notice to the
following mles
1 The posted speed Imut on Cell 4A and 4B dike is 5 mph and the posted speed limit for
the tailings area (other than the Cell 4 A and 4B dike) is 15 mph These limits should not
be exceeded
2 No food or drink is penmtted in the area
3 All personnel entering the tailmgs area must have access to a two way radio
4 Horseplay is not pemutted at any time
5 Only those specifically authorized may operate motor vehicles m the restricted area
6 When road conditions are muddy or slick a four wheel drive vehicle is required in the
area
7 Any work performed in which there is a danger of falling or slipping in the cell will
require the use of a safety belt or hamess with attended life line and an approved life
jacket A portable eyewash must be present on site as well
8 Anytime the boat is used to perform any work an approved life jacket and goggles must
be wom at all times There must also be an approved safety watch with a two way hand
held radio on shore A portable eyewash must be present on site as well
10 Preservation of Wildlife
Every effort should be made to prevent wildlife and domesticated animals from entering the
tailings area All wildlife observed should be reported on the Wildlife Report Worksheet
during each shift Waterfowl seen near the tailings cells should be discouraged from landing
by the use of noisemakers
11 Certification
Following the review of this document and on site instmction on the tailings system
inspection program designated individuals will be certified to perform daily tailings
inspections The Radiation Safety Officer authorizes certification Refer to the Certification
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Book 11 Environmental Protection Manual Section 3 1 Page 44 of 53
Form Appendix C This form should be signed and dated only after a thorough review of the
tailings information previously presented The form will then be signed by the Radiation
Safety Officer and filed
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Book 11 Environmental Protection Manual Section 3 1 Page 45 of 53
APPENDIX C
CERTIFICATION FORM
Date .
Name
I have read the document titled Tailings Management System White Mesa Mill Tailings
Inspector Training and have received on site instmction at the tailings system This instmction
included documentation of daily tailings inspections analysis of potential problems (dike
failures unusual flows) notification procedures and safety
Signature
I certify that the above named person is qualified to perform the daily inspection of the tailings
system at the White Mesa Mill
Radiation Safety Personnel/ Tailings System
Supervisor
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01/12 Revision Denisonll 4
Page 46 of 53
APPENDIX D
FEEDSTOCK STORAGE AREA
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Page 47 of 53
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Book 11 Envu-onmental Protection Manual Section 3 1 Page 48 of 53
APPENDIX E
TABLES
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Page 49 of 53
Table lA
Calculated Action leakage Rates
for Vanous head Conditions
Cell 4A White mesa Mill
Blanding Utah
Head above Liner System (feet) Calculated Action leakage Rate
( gallons / acre / day)
5 222 04
10 31401
15 384 58
20 444 08
25 496 50
30 543 88
35 587 46
37 604 01
Table IB
Calculated Action leakage Rates
for Various head Conditions
Cell 4B White mesa Mill
Blanding Utah
Head above Liner System (feet) Calculated Action leakage Rate
( gallons / acre / day)
5 21140
10 317 00
15 369 90
20 422 70
25 475 60
30 528 40
35 570 00
37 581 20
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Page 50 of 53
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Page 51 of 53
APPENDIX F
Example of Freeboard Calculations
For Cell 4B
Assumptions and Factors
o Total PMP volume to be stored in Cell 4A - 159 4 acre feet
o Wave mnup factor for Cell 4B - 0 77 feet
o Total capacity of Cell 4B - 2 094 000 dry tons
o Elevation of FML of Cell 4B - 5 600 35 FMSL
o Maximum pool surface area of Cell 4B - 40 acres
o Total tailings solids deposited mto Cell 4B at time beach area first exceeds 5 594
FMSL - 1 000 000 dry tons*
o Date beach area first exceeds 5 594 FMSL - March 1 2012*
o Expected and actual production is as set forth in the following table
Time Period Expected
Tailings Solids
Disposition into
Cell 4B
Determined at
the beginnmg of
the period (dry
tons)*
Expected
Tailmgs
Solids
Dispositio
n into Cell
4B at the
beginning
of the
period,
multiplied
by 150%
Safety
Factor
(dry tons)
Actual Tailings
Solids
Disposition mto
Cell 4B
determined at
end of the
period (dry
tons)*
March 1 2012
to November 1
2012
150 000 225 000 225 000
November 1
2012 to
November 1
2013
300 000 450 000 275 000
November 1
2013 to
November 1
2014
200 000 300 000 250 000
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Book 11 Environmental Protection Manual Section 3 1 Page 52 of 53
*These expected and actual tailings and production numbers and dates are fictional and have
been assumed for illustrative purposes only
Based on these assumptions and factors the freeboard liimts for Cell 4B would be calculated
as follows
1 Prior to March L 2012
Prior to March 1 2012 the maximum elevation of the beach area in Cell 4B is less than or
equal to 5 594 FMSL therefore the freeboard linut is set at 5 594 6 FMSL
2 March 1. 2012 to November 1. 2012
The pool surface area would be reduced to the following amount
(1-225 000/ (2 094 000 - 1 000 000)) x 40 acres = 31 77 acres
Based on this reduced pool area the amount of freeboard would be 197 5 acre feet divided by 31 77
acres equals 6 22 feet When the wave mn up factor for Cell 4B of0 77 feet is added to this the total
freeboard required is 6 99 feet This means that the freeboard limit for Cell 4B would be reduced
from 5594 6 FMSL to 5592 2 FMSL (5594 6 FMSL minus 6 22 feet rounded to the nearest one
tenth of a foot) This calculation would be performed at March 1 2012 and this freeboard limit
would persist until November 1 2012
3 November 1, 2012 to November 1. 2013
The pool surface area would be reduced to the following amount
First recalculate the pool surface area that should have applied during the previous period
had modeled tonnages (i e expected tonnages grossed up by the 150% safety factor) equaled
actual tonnages for the period Since the actual tonnage of 225 000 dry tons was the same as
the modeled tonnage of 225 000 dry tons the recalculated pool surface area is the same as
the modeled pool surface area for the previous penod which is 31 77 acres
Then calculate the modeled pool surface area to be used for the period
(1-450 000/ (2 094 000 - 1 000 000 225 000)) x 31 77 acres = 15 32 acres
Based on this reduced pool area the amount of freeboard would be 197 5 acre feet divided by
15 32 acres equals 12 89 feet When the wave mn up factor for Cell 4B of0 77 feet is added
to this the total freeboard required is 13 66 feet This means that the freeboard limit for Cell
4B would be reduced from 5592 2 FMSL to 5586 7 FMSL (5600 35 FMSL minus 13 66
feet rounded to the nearest one tenth of a foot) This calculation would be performed at
November 1 2012 and this freeboard Imut would persist until November 1 2013
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Book 11 Environmental Protection Manual Section 3 1 Page 53 of 53
4 November 1. 2013 to November L 2014
The pool surface area would be reduced to the following amount
First recalculate the pool surface area that should have applied during the previous period
had modeled tonnages (i e expected tonnages grossed up by the 150% safety factor) equaled
actual tonnages for the period Since modeled tonnages exceeded actual tonnages the pool
area was reduced too much during the previous penod and must be adjusted The
recalculated pool area for the previous period is
(1 - 275 000/ (2 094 000 - 1 000 000 225 000) x 31 77 acres = 21 72 acres
This recalculated pool surface area will be used as the starting point for the freeboard
calculation to be performed at November 1 2013
Then calculate the modeled pool surface area to be used for the penod
(1-300 000/ (2 094 000 - 1 000 000 225 000 - 275 000)) x 21 72 acres
10 75 acres
Based on this reduced pool area the amount of freeboard would be 197 5 acre feet divided by
10 75 acres equals 18 37 feet When the wave mn up factor for Cell 4B of0 77 feet is added
to this the total freeboard required is 19 14 feet This means that the freeboard limit for Cell
4B would be reduced from 5586 7 FMSL to 5581 2 FMSL (5600 4 FMSL minus 18 4 feet
rounded to the nearest one tenth of a foot) This calculation would be performed at
November 1 2013 and this freeboard limit would persist until November 1 2014
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REDLINE
i' f
I White Mesa Mill - Standard Operating Procedures 07/1101/12 Revision Denison 11 4^
Book 11 Envu-onmental Protection Manual Section 3 1 Page 1 of 53
WHITE MESA MILL TAILINGS MANAGEMENT SYSTEM
AND
DISCHARGE MINIMIZATION TECHNOLOGY (DMT)
MONITORING PLAN
TABLE OF CONTENTS
Contents
1 INTRODUCTION 3
2 DAILY TAILINGS INSPECTIONS 3
2 1 Dailv Comprehensive Tailings Inspection 3
2 2 Dailv Operations Inspection 6
2 3 Dailv Operations Patrol 6
2 4 Trainmg 6
2 5 Tailmes Emergencies 6
3 WEEKLY TAILINGS AND DMT INSPECTION 7
3 1 Weeklv Tailings Inspections 7
Northing 12
Easting 12
3 2 Weeklv Inspection of Solution Levels in Roberts Pond 15
3 3 Weeklv Feedstock Storage Area Inspections 15
4 MONTHLY TAILINGS INSPECTION 15
5 QUARTERLY TAILINGS INSPECTION 16
6 ANNUAL EVALUATIONS 18
6 1 Annual Technical Evaluation 18
6 2 Movement Monitors 19
6 3 Freeboard Limits 19
6 3 1 Cell 1 20
6 3 2 Cell 2 20
6 3 3 Cell 3 20
6 3 4 Cell 4A 20
6 3 5 Cell 43 20
6 3 6 Roberts Pond 23
6 4 Annual Leak Detection Fluid Samples 23
6 5 Annual Inspection of the Decontanunation Pads 23
7 OTHER INSPECTIONS 24
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Book 11 Environmental Protection Manual SecUon 3 1 Page 2 of 53
8 REPORTING REQUIREMENTS 24
8 1 Monthlv Tailings Reports 24
8 2 DMT Reports 25
8 3 TAILINGS INSPECTOR TRAINING 40
1 INTRODUCTION ^
3—DAILY TAILINGS INSPECTIONS ^
3-4-—Daily Comprehensive Tailings Inspectioa-
Dailv Operations Inspection
3-^—Daily Operations Pa&el-
34-—Traming
3-^—Tailings Emorgencies-
3—WEEKLY TAILINGS AND DMT INSPECTION
3-1-—Wookly Tailings Inspections 7
3 1 2 Northfflg 13
3^-^—Easting 13
3-3-—Weekly Inspection of Solution Levels in Roberts Pond 14
3-3-—Weekly Focdstock Storage Area Inspoctiens 14
4-MONTHLY TAILINGS INSPECTION
OTTARTFRI Y TATI TMn9 TNI<?PFPTTnN
i&
6-ANNUAL EVALUATIONS i%
—Annual Technical Evaluation i%
6-3r—Movomcnt Momtors i9
6-3-—Frooboard Limits 19
6-34-
1
Coll 1
Pnll '»
30
''n '1 CcW '-'0
fi d Prll /I A
TXf
'-*n
fi '1 5 PPII IIR %J ^ mJ
6^-6-Roberts Pond 33
6-4-—Annual Leak Detoction Ruid Samples 33
6-§-—Annual Inspection of the Decontamination Pads 33
7 OTHER INSPECTIONS 34
^—REPORTING REQUIREMENTS 34
—Monthlv Tailings Reports 34
«-3-—DMT Reports 3§
—TAILINGS INSPECTOR TRAINING 45
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Book 11 Environmental ProtecUon Manual SecUon 3 1 Page 3 of 53
1 INTRODUCTION
This Tailings Management System and Discharge Minmuzation Technology Monitoring Plan (the
Plan ) for the White Mesa Mill (the Mill ) provides procedures for monitonng of the tailings cell
system as required under State of Utah Radioactive Matenals License No UT 1900479 (the
Radioactive Matenals License ) as well as procedures for operating and maintenance of monitonng
equipment and reporting procedures that are adequate to demonstrate DMT compliance under State
of Utah Ground Water Discharge Penrnt No 370004 for the Mill (the GWDP )
This Plan is designed as a systematic program for constant surveillance and documentation of the
integnty of the tailings impoundment system including dike stability liner integnty and transport
systems as well as monitonng of water levels in Roberts Pond and feedstock storage areas at the
Mill The Plan requires daily weekly quarterly monthly and annual inspections and evaluations and
monthly reporting to Mill management
2 DAILY TAILINGS INSPECTIONS
The following daily tailings inspections shall be performed
2 1 Daily Comprehensive Tailings Inspection
Qn a daily basis including weekends all areas connected with the evaporation cell (Cell 1) and
thefive-four tailings cells (Cells 2.3.4A. and 4B) will be inspected Observations will be made of
the current condition of each cell noting any corrective action that needs to be taken
The Environmental or Radiation TochmcianRadiation Safety Officer (RSO) or his designee is
responsible for performing the daily tailings inspections The Radiation Safety OfficorRSO may
designate other individuals with training as descnbed in Section 2 4 below to perform the daily
tailings inspection
Observations made by the inspector will be recorded on the Daily Inspection Data form (a copy of
which IS attached m Appendix A) The Daily Inspection Data form contains an inspection checklist
which includes a tailings cells map and spaces to record observations especially those of immediate
concem and those requinng corrective action The inspector will place a check by all inspection
Items that appear to be operating properly Those items where conditions of potential concem are
observed should be marked with an X A note should accompany the X speciiymg what the
concem is and what corrective measures will resolve the problem This observation of concem
should be noted on the form until the problem has been remedied The date that conective action
was taken should be noted as well
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Book 11 Environmental Protection Manual Section 3 1 Page 4 of 53
Areas to be inspected include the following Cell 1 2 3 4A and 4B Dikes 4A S 4A E and 4B
S wind movement of tailmgs effectiveness of dust nunimization methods spray evaporation Cell 2
spillway Cell 3 spillway Cell 4A spillway,Cell 3 Cell 4A spillway Cell 4A and 4B hquid pools and
associated liquid return equipment and cell leak detection systems
Operational features of the tailings area are checked for conditions of potential concem The
following Items require visual inspection dunng the daily tailings inspection
a) Tailings slurry and SX raffinate transport systems from the Mill to the active
disposal cell(s) and pool retum pipeline and pumps
Daily inspections of the tailmgs lines are required to be performed when the Mill
is operating The lines to be inspected include the taihngs slurry hues from CCD
to the active tailings cell SX raffinate lines that can discharge mto Cell 1 Cell
4AorCell4B the pond retum line from the tailings area to the Mill and lines
transporting pond solutions from one cell to another
b) Cell 1
c) Cell 2
d) Cell 3
e) Cell 4A
f) Cell 4B
g) Dike stmctures including dikes 4A S 4A E and 4B S
h) The Cell 2 spillway Cell 3 spillway Cell 4A spiUway Cell 3 Cell 4A and Cell
4B liquid pools and associated liquid return equipment
i) Presence of wildlife and/or domesticated ammals in the tailings area including
waterfowl and burrowing animal habitations
j) Spray evaporation pumps and lines
k) Wind movement of tailings and dust minmuzation
Wind movement of tailings will be evaluated for conditions which may require
initiation of preventative dust minimization measures for cells containing taihngs
sand Durmg tailmgs inspection general surface conditions will be evaluated for
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Book 11 Environmental Protection Manual Section 3 1 Page 5 of 53
the following 1) areas of tailings subject to blowing and/or wind movement 2)
liquid pool size 3) areas not subject to blowing and/or wind movement
expressed as a percentage of the total cell area The evaluations will be reviewed
on a weekly basis or more frequently if warranted and will be used to direct dust
minimization activities
1) Observation of flow and operational status of the dust control/spray evaporation
system(s)
m) Observations of any abnormal vanations in tailings pond elevations in Cells 1 3
4A and4B
n) Locations of slurry and SX discharge within the active cells Slurry and SX
discharge pomts need to be indicated on the tailings cells map included in the
Daily Inspection Data form.
o) An estimate of flow for active tailings slurry and SX line(s)
p) An estimate of flow m the solution retum line(s)
q) Daily measurements in the leak detection system (LDS) sumps of the tailings
cells will be made when warranted by changes in the solution level of the
respective leak detection system
The tngger for further action when evaluating the measurements m the Cell 1 and
Cell 3 leak detection systems is a gain of more than 12 inches in 24 hours The
solution level in Cell 4A or 4B leak detection system is not allowed to be more
than 1 0 foot above the lowest point on the bottom flexible membrane liner
(FML) (Cell 4A FML elevation is 5555 14 amsl and with the addition of the 1 0
foot of solution the solution elevation is 5556 14 feet amsl For Cell 4B the FML
elevation is 5557 50 amsl and with the addition of the 1 0 foot of solution the
solution elevation is 5558 50 feet amsl) If any of these observations are made
the Mill Manager should be notified immediately and the leak detection system
pump started In addition the requirement to notify the Executive Secretary in
accordance with Parts ID 6 and IG 3 of the Groundwater Discharge Permit must
be adhered to when the solution level tngger for Cell 4A or 4B has been
exceeded
Whenever the leak detection system pump is operating and the flow meter
totalizer is recording a notation of the date and the time will be recorded on the
Daily Inspection Data form This data will be used in accordance with License
Condition 11 3 B through 11 3 E of the Mill s Radioactive Matenals License to
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Book 11 Environmental Protection Manual SecUon 3 1 Page 6 of 53
detemune whether or not the flow rate into the leak detection system is in excess
of the License Conditions
Items (a) (m) (n) and (o) are to be done only when the Mill is operating When the Mill is down
these Items cannot be performed
2 2 Daily Operations Inspection
Dunng Mill operation the Shift Foreman or other person with the training specified in Section 2 4
below designated by the Radiation Safety Officer will perform an mspection of the tailmgs line and
tailings area at least once per shift paying close attention for potential leaks and to the discharges
from the pipelines Observations by the Inspector will be recorded on the appropnate line on the
Operating Foreman s Daily Inspection form
2 3 Daily Operations Patrol
In addition to the inspections descnbed in Sections 2 1 and 2 2 above a Mill employee will patiol
the tailings area at least twice per shift dunng Mill operations to ensure that there are no obvious
safety or operational issues such as leaking pipes or unusual wildlife activity or incidences
No record of these patrols need be made but the inspectors will notify the Radiation Safety Officer
^RSQ-) and/or Mill management m die event that dunng their inspection they discover that an
abnormal condition or tailmgs emergency has occuned
2 4 Training
All individuals perfomung inspections descnbed in Sections 2 1 and 2 2 above must have Tailings
Management System training as set out in the Tailmgs Inspection Training procedure which is
attached as Appendix B This training will include a training pack explaining the procedure for
performing the inspection and addressing inspection items to be observed In addition each
individual after reviewing the training pack will sign a certification form mdicating that tiaimng
has been received relative to his/her duties as an inspector
2 5 Tailings Emergencies
Inspectors will notify the Radiation Safety OfficerRSO and/or Mill management immediately if
dunng their inspection they discover that an abnormal condition exists or an event has occurred that
could cause a tailings emergency Until relieved by the Environmental or Radiation Technician or
Radiation Safety OfficorRSO inspectors will have the authonty to direct resources dunng tailings
emergencies
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Book 11 Environmental Protection Manual Section 3 1 Page 7 of 53
Any major catasti-ophic events or conditions pertaining to the tailmgs area should be reported
I immediately to the Mill Manager or the Radiation Safety OfficorRSO one of whom will notify
Corporate Management If dam failure occurs notify your supervisor and the Mill Manager
immediately The Mill Manager will then notify Corporate Management MSHA (303 231 5465)
and the State of Utah Division of Dam Safety (801 538 7200)
3 WEEKLY TAILINGS AND DMT INSPECTION
3 1 Weeklv Tailings Inspections
Weekly tailings inspections are to be conducted by the Radiation Safety Department and include the
following
a) Leak Detection Systems
Each tailings cell s leak detection system shall be checked weekly (as well as
daily) to determine whether it is wet or dry If marked wet the liquid levels need
to be measured and reported In Cell 1 and Cell 3 the leak detection system is
measured by use of a dual probe system that senses the presence of solutions in
the LDS system (comparable to the systems in Cells 4A and 4B) and indicates the
presence of solution with a waming light The Cell 4A and 4B leak detection
systems are momtored on a continuous basis by use of a pressure tiansducer that
feeds water level information to an electronic data collector The pressure
transducer is calibrated for fluid with a specific gravity of 1 0 The water levels
are measured every hour and the information is stored for later retneval The
water levels are measured to the nearest 0 10 inch The data collector is currentiy
programmed to store 7 days of water level information The number of days of
stored data can be increased beyond 7 days if needed For Cells 1 and 3 the
water level data is recorded on the Daily Tailings Inspection Form For Cells 4 A
I and 4B the water level data is downloaded to a laptop computer ea-penodically
and incorporated into the Mill s environmental monitonng data storage and into
the files for weekly inspection reports of the tailmgs cell leak detection systems
K sufficient fluid is present in the leak detection system of any cell the fluid shall
be pumped from the LDS to the extent reasonably possible and record the
volume of fluid recovered Any fluid pumped from an LDS shall be retumed to a
disposal cell
For Cells 1 and 3 if fluid is pumped from an LDS the flow rate shall be
calculated by dividing the recorded volume of fluid recovered by the elapsed time
since fluid was last pumped or increases m the LDS fluid levels were recorded
whichever is the more recent This calculation shall be documented as part of the
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07/U01/12 Revision Denisonl 1 43
Page 8 of 53
weekly inspection
For Cells 1 and 3 upon the initial pumping of fluid from an LDS a fluid sample
shall be collected and analyzed in accordance with paragraph 11 3 C of the
Radioactive Matenals License
For Cell 4A and 4B under no circumstance shall fluid head in the leak
detection system sump exceed a 1 foot level above the lowest point in the
lower flexible membrane liner To determine the Maximum Allowable Daily
LDS How Rates in the Cell 4A and 4B leak detection systems the total
volume of all fluids pumped from the LDS on a weekly basis shall be
recovered from the data collector and that information will be used to
calculate an average volume pumped per day Under no circumstances shall
the daily LDS flow volume exceed 24 160 gallons/day for Cell 4A or 26 145
gallons/day for Cell 4B The maximum daily LDS flow volume will be
compared against the measured cell solution levels detailed on Table 1A and
IB (for Cells 4A and 4B respectively) in Appendix E to detemune the
maximum daily allowable LDS flow volume for varying head conditions m
Cell 4A and 4B
b) Slimes Drain Water Level Monitoring
(i) Cell 3 IS nearly full and will commence closure when filled Cell 2 is partially
reclaimed with the surface covered by platform fill Each cell has a shmes drain
system which aids in dewatenng the shmes and sands placed m the cell
(ll) Denison re graded the intenm fill on Cell 2 in order to reduce the potential for the
accumulation of stormwater on the surface of Cell 2 As a result of the re grading of
the intenm cover and the placement of an additional 62.000 cubic yards of fill
matenal on Cell 2. the slimes dram access pipe was extended 6 97 feet The
extension pipe is 6 97 feet in length, and therefore the new measunng point is 37 97
feet from the t)ottom of the slimes drain The measunng point on the extension pipe
was surveyed bv a Utah Certified Land Surveyor For the quarterly recoverv test
descnt>ed in section vi below, this extension has no effect on the data measurement
procedures
^ Cell 2 has a pump placed inside of the shmes drain access pipe at the bottom*
of the shmes drain As taken from actual measurements the bottom of the shmes
drain is 38-37 97 feet below a water level measunng point which is a notch on the
side ofthe Cell 2 shmes drain access pipe at the centerline of the shmes drain access
pipe at the ground surface level This means that the bottom of the slimes dram pool
and the location of the pump are one foot above the lowest point of the FML in Cell
Formatted Indent Left 1 No bullets or
numbering
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07/1401/12 Revision Demsonll43
Page 9 of 53
2 which based on constmction reports is at a depth of39-^897.feet below the water
level measunng point on the slimes drain access pipe for Cell 2
(iii) The shmes drain pump m Cell 2 is activated and deactivated by a float mechamsm
and water level probe system When the water level reaches the level of the float
mechamsm the pump is activated Pumping then occurs until the water level reaches
the lower probe which tums the pump off The lower probe is located one foot above
the bottom of the shmes drain standpipe and the float valve is located at five-three
feet above the bottom of the slimes drain standpipe The average wastewater head
m the Cell 2 shmes dram is therefore less than 5-3_feet and is below the phreatic
surface of tailings Cell 2 about 30-27 feet below the water level measunng point on
the slimes drain access pipe As a result there is a continuous flow of wastewater
from Cell 2 into the slimes dram collection system Mill management considers that
the average allowable wastewater head in the Cell 2 shmes drain resulting from
pumping in this manner is satisfactory and is as low as reasonably achievable
(iv) The Cell 2 shmes dram pump is checked weekly to observe that it is operating and
that the water level probe and float mechanism are working properly which is noted
on the Weekly Tailings Inspection Form If at any time the pump is observed to be
not working properly it will be fixed or replaced within 15 days
(v) Depth to wastewater m the Cell 2 shmes drain access pipe shall be monitored and
recorded weekly to determine maximum and mimmum fluid head before and after a
pumping cycle respectively The extension of the Cell 2 slimes dram access pipe did
not require any changes to the measurement procedure The surveyed measunng
point on the extended pipe is used as required The head measurements are
calculated m the same manner, using the same procedures as those used pnor to the
extension of the Cell 2 shmes drain access pipe, however, the total depth to the
bottom of the pipe is now 37 97 feet as noted on the corrected form in Attachment A
-All head measurements must be made from the same measunng point (the*
notch at the north side of the access pipe) and made to the nearest 0 01 foot The
results will be recorded as depth in pipe measurements on the Weekly Tailings
Inspection Form The extension of the Cell 2 slimes access pipe has not changed the
method of calculation of the pre and post pump head calculations, only the constant
(Cell 2 shmes drain access pipe height) used m the calculation has changed The
head is calculated bv subtracting the depth to liquid from 37 97 feet rather than from
the previous measurement of 38 feet The weekly Tailings Inspection form included
m Attachment A has been changed to reflect the extension height.
•4-
(vi) Effective July 11 2011 on a quarterly basis the shmes drain pump will be tumed off
and the wastewater m the shmes drain access pipe will be allowed to stabilize for at
least 90 hours Once the water level has stabilized (based on no change in water level
for three (3) successive readings taken no less than one (1) hour apart) the water level
of the wastewater will be measured and recorded as a depth in pipe measurement on
-( Formatted Not H ghlight
Formatted Indent Left
numbering
1 No bullets or
Formatted Indent Left 1 Hanging 0 5
No bullets or numbering
Formatted Indent Left 0 75
number ng
No bullets or
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Book 11 Environmental Protection Manual Section 3 1 Page 10 of 53
Quarterly Data form by measunng the depth to water below the water level
measunng point on the shmes drain access pipe
(vu) No process hquids shall be allowed to be discharged mto Cell 2
(vill) If at any time the most recent average annual head in the Cell 2 shmes drain is
found to have increased above the average head for the previous calendar year the
Licensee will comply with the requirements of Part IG 3 of the GWDP mcluding the
requirement to provide notification to the Executive Secretary orally within 24 hours
followed by wntten notification
(ix) Because Cell 3 and Cell 4A are cunently active no pumping from the Cell 3 or Cell
4A shmes drain is authonzed No pumping from the Cell 4B shmes drain will be
authonzed once it is put mto service and while it is active Pnor to initiation of
tailmgs dewatenng operations for Cell 3 Cell 4A or Cell 4B a similar procedure
will be developed for ensunng that average head elevations in the Cell 3 and Cell 4A
shmes drains are kept as low as reasonably achievable and that the Cell 3 Cell 4A
and Cell 4 shmes drains are inspected and the results reported in accordance with the
requirements of the permit
c) Wind Movement of Tailings
An evaluation of wind movement of tailings or dusting and control measures
shall be taken if needed
d) Tailings Wastewater Pool Elevation Monitoring
Solution elevation measurements in Cells 1^4A and 4B and Roberts Pond are to be taken
by survey on a weekly basis _ aad-tThe beach area in Cell 4B with the maximum elevation
is to be taken by survey on a monthly basis when beaches are first observed as follows
(i) The survey will be performed by the Mill s Radiation Safety Officer or designee
(the Surveyor ) with the assistance of another Mill worker (the Assistant )
(u) The survey will be performed using a survey mstmment (the Survey Instrument )
accurate to 0 01 feet such as a Sokkai No B21 or equivalent together with a
survey rod (the Survey Rod ) having a visible scale m 0 01 foot increments
(iii)The Reference Points for Cells 1. Cell 4A. and 4B and Roberts Pond are known
points established by professional survey For Cell 1 and Roberts Pond the
Reference Point is a wooden stake with a metal disk on it located on the southeast
comer of Cell 1 The elevation of the metal disk (the Reference Point
Elevation ) for Cell 1 and Roberts Pond is at 5 623 14 feet above mean sea level
( FMSL ) For Coll 3 tho Rcforenco Point is a piece of metal rebar located on the
south dike of Cell 3 Tho elevation at the top of this pieco of rebar (tho Reference
Point Elevation for Coll 3) la at 5 607 83 FMSL For Cell 4A and 4B the
Reference Point is a piece of stamped metal monument located next to the
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Book 11 Environmental Protection Manual SecUon 3 1 Page 11 of 53
transformer on the south side of Cell 4A and 4B The elevation at the top of this
piece of rebar (the Reference Point Elevation for Cell 4A and 4B) is 5600 49 fmsl
The Surveyor will set up the Survey Instmment m a location where both the
applicable Reference Point and pond surface are visible For Cell 1 and Roberts
Pond this is typically on the road on the Cell 1 south dike between Cell 1 and
Roberts Pond approximately 100 feet east of the Cell 1/Roberts Pond Reference
Point For Cell 4A and Cell 4B this is typically on the south side of Cell 4A and
4B
(iv) Qnce m location the Surveyor will ensure that the Survey Instmment is level by
centenng the bubble m the level gauge on the Survey Instmment
(v) The Assistant will place the Survey Rod vertically on the Reference Point (on the
metal disk on the Cell 1/Roberts Pond Reference Point on the top of the rebar on
the Cell 4A and 4B Reference Point The Assistant will ensure that the Survey
Rod IS vertical by gentiy rocking the rod back and forth until the Surveyor has
established a level reading
(vi) The Surveyor will focus the cross hairs of the Survey Instmment on the scale on
the Survey Rod and record the number (the Reference Point Reading ) which
represents the number of feet the Survey Instmment is reading above the
Reference Point
(vii) The Assistant will then move to a designated location where the Survey Rod can
be placed on the surface of the main solution pond in the Cell 1 Cell 4A Cell
4B or Roberts Pond or the area of the beach in Cell 4B with the highest
elevation as the case may be These designated locations and the methods to be
used by the Assistant to consistendy use the same locations are as follows
For a newly constmcted cell when the cell is first placed into operation the solution level is
typically zero feet above the FML or a minimal elevation above the FML due to natural
precipitation For newly constmcted cells solution level measurement of solution level will
commence within 30 days of authonzation for use Measurements will be conducted consistent
with the procedures in this DMT Plan and consistent with current Mill health and safety
procedures The measurements will be completed using survey equipment and the appropnate
length survey rod (either 25 or 45 ) not be required until tho solution level is high enough that it
can be reached safely by personnel with a measurmg tape along the sido of the FML Solutions
lovols will bo measured by this method beginning when tho solution level is high enough to be
reached safely as detemuned by tho RSO Surveying of solution lovols will not bo required until
solution levels aro high enough that they can offoctivoly ho measured by survey instmment from
the appropnate surveying point
A Pond Surface Measurements
I Cell 4A
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Book 11 Environmental ProtecUon Manual SecUon 3 1
07/4401/12 Revision Denisonl 143
Page 12 of 53
The Assistant will walk down the slope in the northeast comer of Cell 4A and
place the Survey Rod at the liquid level
n Cell 4B
The Assistant will walk down the slope in the northwest southeast comer of Cell
4B and place the Survey Rod at the liquid level
m Cell 1
A mark has been painted on the north side of the ramp going to the pump
platform m Cell 1 The Assistant will place the Survey Rod against that mark
and hold the rod vertically with one end just touching the liquid surface and
IV Roberts Pond
A mark has been painted on the railing of the pump stand in Roberts Pond The
Assistant will place the Survey Rod against that mark and hold the rod
vertically with one end just touching the liquid surface
Based on the foregoing methods the approximate coordinate locations for the
measunng points for Roberts Pond and the Cells are
3-1-^ Northing 3-1^ Easting
Roberts Pond 323 041 2 579 697
CeU 1 322 196 2 579 277
Cell 4A 320 300 2 579 360
Cell 4B 320 690 2 576 200
-( Formatted No bullets or numbering
These coordinate locations may vary somewhat depending on solution elevations
m the Pond and Cells
Cell 4B Beach Elevation
Beach elevations m Cell 4B will commence when beaches are first observed The
Assistant will place the Survey Rod at the point on the beach area of Cell 4B that
has the highest elevation If it is not clear which area of the beach has the highest
elevation then multiple points on the beach area will be surveyed until the
Surveyor is satisfied that the point on the Cell 4B beach area with the highest
elevation has been surveyed If it is clear that all points on the Cell 4B beach area
are below 5 593 FMSL then the Surveyor may rely on one survey point
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Book 11 Envu-onmental Protection Manual Section 3 1 Page 13 of 5 3
(vm) The Assistant will hold the Survey Rod vertically with one end of the Survey
Rod just touching the pond surface The Assistant will ensure that the Survey
Rod IS vertical by gently rocking the rod back and forth until the Surveyor has
established a level reading
(ix)The Surveyor will focus the cross hairs of the Survey Instmment on the scale on
the Survey Rod and record the number (the Pond Surface Reading ) which
represents the number of feet the Survey Instmment is reading above the pond
surface level
The Surveyor will calculate the elevation of the pond surface as FSML by adding the
Reference Point Reading for the Cell or Roberts Pond as the case may be to the Reference
Point Elevation for the Cell or Roberts Pond and subtracting die Pond Surface Reading for
the Cell or Roberts Pond and will record the number accurate to 0 01 feet
^e} Decontamination Pads
(i) New Decontamination Pad
The New Decontamination Pad is located in the southeast comer of the ore
pad near the Mill s scale house
A In order to ensure that the pnmary containment of the New
Decontamination Pad water collection system has not been
compromised and to provide an inspection capability to detect
leakage from the pnmary containment vertical inspection portals
have been installed between the pnmary and secondary containments
B These portals will be visually observed on a weekly basis as a means
of detecting any leakage from the pnmary containment into the void
between the pnmary and secondary containment The depth to water
m each portal will be measured weekly by physically measunng the
depth to water with an electncal sounding tape/device All
measurements must be made from the same measunng point and be
made to the nearest 0 01 foot
C These inspections will be recorded on the Weekly Tailmgs Inspection
form
D The water level shall not exceed 0 10 foot above the concrete floor in
any standpipe at any time This will be determmed by subtracting the
weekly depth to water measurement from the distance from the
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Book 11 Environmental Protection Manual Secuon 3 1 Page 14 of 53
measunng point in the standpipe to the dry concrete floor The depth
to water from the top (elevation 5589 8 feet amsl) of any of the three
(3) observation ports to the standing water shall be no less than 6 2
feet Depths less than 6 2 feet shall indicate more that 0 1 foot of
standing water above the concrete floor (elev 5583 5 feet amsl) and
shall indicate a leak in the pnmary containment
E Any observation of fluid between the pnmary and secondary
containments will be reported to the Radiation Safety Officer (RSO)
F In addition to inspection of the water levels in the standpipes the
New Decontamination Pad including the concrete integnty of the
exposed surfaces of the pad will be inspected on a weekly basis Any
soil and debns will be removed from the New Decontamination Pad
immediately pnor to inspection of the concrete wash pad for cracking
Observations will be made of the current condition of the New
Decontamination Pad Any abnormahties relating to the pad and any
damage to the concrete wash surface of the pad will be noted on the
Weekly Tailings Inspection form If there are any cracks greater than
1/8 inch separation (width) the RSO must be contacted The RSO
will have the responsibility to cease activities and have the cracks
repaired
(ll) Existing Decontamination Pad
The Existing Decontamination Pad is located between the northwest comer of the
Mill s maintenance shop and the ore feeding gnzzly
A The Existing Decontamination Pad will be inspected on a weekly
basis Any soil and debns will be removed from the Existing
Decontamination Pad immediately pnor to inspection of the concrete
wash pad for cracking Observations will be made of the current
condition of the Existing Decontanunation Pad including the
concrete integnty of the exposed surfaces of the pad Any
abnormahties relating to the pad and any damage or cracks on the
concrete wash surface of the pad will be noted on the Weekly
Tailings Inspection form If there are any cracks greater than 1/8 inch
separation (width) the RSO must be contacted The RSO will have
the responsibility to cease activities and have the cracks repaired
Summary
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Book 11 Environmental Protection Manual Section 3 1 Page 15 of 53
In addition the weekly inspection should summanze all activities conceming the
tailings area for that particular week
Results ofthe weekly tailings inspection are recorded on the Weekly Tailings and DMT Inspection
form An example of the Weekly Tailings and DMT Inspection form is provided in Appendix A
3 2 Weekly Inspection of Solution Levels m Roberts Pond
On a weekly basis solution elevations are taken on Roberts Pond in accordance with the procedures
set out in Section 3 1 d) above The Weekly solution level m Roberts Pond is recorded on the
Weekly Tailings and DMT Inspection form Based on histoncal observations the FML at the Pond
Surface Reading area for Roberts Pond is approximately six inches above the lowest point on the
pond s FML If the pond solution elevation at the Pond Surface Reading area is at or below the FML
for that area the pond will be recorded as being dry
3 3 Weeklv Feedstock Storage Area Inspections
Weekly feedstock storage area inspections will be performed by the Radiation Safety Department to
confirm that
a) the bulk feedstock matenals are stored and maintained within the defined area descnbed m
the GWDP as indicated on the map attached hereto as Appendix D
b) a 4 ft buffer is maintained at the penphery of the storage area which is absent bulk matenal
in order to assure that the matenals do not encroach upon the boundary of the storage area
and
c) all altemate feedstock located outside the defined Feedstock Area are maintained within
water tight contmners
The results of this inspection will be recorded on the Ore Storage/Sample Plant Weekly Inspection
Report a copy of which is contamed m Appendix A Any vanance in stored matenals from this
requirement or observed leaking altemate feedstock dmms or other containers will be brought to the
attention of Mill Management and rectified within 15 days
4 MONTHLY TAILINGS INSPECTION
Monthly tailings inspections will be performed by the Radiation Safety Officer or his designee from
the Radiation Safety Department and recorded on the Monthly Inspection Data form an example of
which IS contained in Appendix A Monthly inspections are to be performed no sooner than 14 days
since the last monthly tailmgs inspection and can be conducted concurrentiy with the quarterly
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tailings inspection when applicable The following items are to be inspected
a) Tailings Slurry Pipeline
When the Mill is operating the slurry pipeline will be visually inspected at key
locations to determine pipe wear The cntical points of the pipe include bends slope
changes valves and junctions which are cntical to dike stability These locations to
be monitored will be determined by the Radiation Safety Officer or his designee from
the Radiation Safety Department dunng the Mill mn
b) Diversion Ditches
Diversion ditches 1 2 and 3 shall be monitored monthly for sloughing erosion
undesirable vegetation and obstmction of flow Diversion berm 2 should be checked
for stability and signs of distress
c) Sedimentation Pond
Activities around the Mill and facihties area sedimentation pond shall be summanzed
for the month
d) Overspray Dust Minimization
The inspection shall include an evaluation of overspray minmuzation if applicable
This entails ensunng that the overspray system is functioning properly In the event
that overspray is earned more than 50 feet from the cell the overspray system should
be immediately shut off
e) Remarks
A section is included on the Monthly Inspection Data form for remarks in which
recommendations can be made or observations of concem can be documented
f) Summary of Daily Weekly and Quarterly Inspections
The monthly inspection will also summanze the daily weekly and if applicable
quarterly tailings inspections for the specific month
In addition settlement monitors are typically surveyed monthly and the results reported on the
Monthly Inspection Data form
5 QUARTERLY TAILINGS INSPECTION
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Book 11 Envnonmental Protection Manual Section 3 1 Page 17 of 53
The quarterly tailings inspection is performed by the Radiation Safety Officer or his designee from
the Radiation Safety Department having the trainmg specified in Section 2 4 above once per
calendar quarter A quarterly inspection should be performed no sooner than 45 days since the
previous quarterly inspection was performed
Each quarterly inspection shall include an Embankment Inspection an Operations/Maintenance
Review a Constmction Review and a Summary as follows
a) Embankment Inspection
The Embankment mspection involves a visual inspection of the crest slope and toe
of each dike for movement seepage severe erosion subsidence shnnkage cracks
and exposed liner
b) Operations/Maintenance Review
The Operations/Maintenance Review consists of reviewing Operations and
Maintenance activities pertaimng to the tailings area on a quarterly basis
c) Construction Review
The Constmction Review consists of reviewing any constmction changes or
modifications made to the tailings area on a quarterly basis
d) An estimate of the percentage of the tailings beach surface area and solution pool
area is made including estimates of solutions cover areas and tailings sands for
Cells 3 4A and 4B
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Book 11 Environmental Protection Manual Section 3 1 Page 18 of 53
e) Summary
The summary will include all major activities or observations noted around the
tailings area on a quarterly basis
If any of these conditions are noted the conditions and conective measures taken should be
documented in the Quarterly Inspection Data form An example of the Quarterly Inspection Data
form IS provided in Appendix A
6 ANNUAL EVALUATIONS
The following annual evaluations shall be performed
6 1 Annual Technical Evaluation
An annual technical evaluation of the tailings management system is performed by a registered
professional engineer (PE) who has expenence and traimng m the area of geotechnical aspects of
retention stmcmres The technical evaluation includes an on site inspection of the tailings
management system and a thorough review of all tailmgs records for the past year The Technical
Evaluation also includes a review and summary of the annual movement monitor survey (see Section
5 2 below)
All tailings cells and corresponding dikes will be inspected for signs of erosion subsidence
shnnkage and seepage The drainage ditches wdl be inspected to evaluate surface water control
stmctures
In the event tailings capacity evaluations (as per SOP PBL 3) were performed for the receipt of
altemate feed matenal dunng the year the capacity evaluation forms and associated calculation
sheets will be reviewed to ensure that the maximum tailings capacity estimate is accurate The
amount of tailings added to the system since the last evaluation will also be calculated to detemune
the estimated capacity at the time of the evaluation
Tailings inspection records will consist of daily weekly monthly and quarterly tailmgs inspections
These inspection records will be evaluated to determine if any freeboard limits are being
approached Records will also be reviewed to summanze observations of potential concem The
evaluation also involves discussion with the Environmental and/or Radiation Technician and the
Radiation Safety Officer regarding activities around the tailings area for the past year Dunng the
aimual inspection photographs of the tailings area will be taken The training of individuals will be
reviewed as a part of the Annual Technical Evaluation
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Book 11 Environmental Protection Manual Section 3 1 Page 19 of 53
The registered engineer will obtain copies of selected tailings inspections along with the monthly
and quarterly summanes of observations of concem and the corrective actions taken These copies
will then be included in the Annual Technical Evaluation Report
The Annual Techmcal Evaluation Report must be submitted by November 15* of every yearteto the
Executive Secretary
Directing Dam Safety Engineer
State of Utah Namral Resources
1636 West North Temple Suito 220
Salt Lolto City Utah 84116 3156
6 2 Movement Monitors
A movement momtor survey is to be conducted by a licensed surveyor annually dunng the second
quarter of each year The movement monitor survey consists of surveying momtors along dikes 3 S
4A W and 4A S to detect any possible settiement or movement of the dikes The data generated
from this survey is reviewed and incorporated mto the Annual Technical Evaluation Report of the
tailmgs management system
6 3 Freeboard Lmuts
The freeboard limits set out in this Section are intended to capmre the Local 6 hour Probable
Maximum Precipitation (PMP) event which was detemuned in the January 10 1990 Drainage
Report (the Drainage Report ) for the White Mesa site to be 10 inches
The flood volume from the PMP event over the Cell 1 pond area plus the adjacent drainage areas
was calculated m the Drainage Report to be 103 acre feet of water with a wave mn up factor of
0 90 feet
The flood volume from the PMP event over the Cell 2 and Cell 3 pond areas plus the adjacent
drainage areas was calculated in the Drainage Report to be 123 4 acre feet of water
The flood volume from the PMP event over the Cell 4A area was calculated m the Drainage
Report to be 36 acre feet of water (40 acres plus the adjacent drainage area of 3 25 acres) times
the PMP of 10 inches) with a wave mn up factor of 0 77 feet
The flood volume from the PMP event over the Cell 4B area has been calculated to be 38 1 acre
feet of water (40 acres plus the adjacent drainage area of 5 72 acres) times the PMP of 10
inches with a wave mn up factor of 0 77 feet
The total pool surface area in Cell 1 is 52 9 acres in Cell 4A is 40 acres and m Cell 4B is 40
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Book 11 Envnonmental Protection Manual Section 3 1 Page 20 of 53
acres The top of the flexible membrane liner ( FML ) for Cell 1 is 5 618 2 FMSL for Cell 4A
IS 5 598 5 FMSL and for Cell 4B is 5600 4 FMSL
Based on the foregoing the freeboard limits for the Mill s tailings cells will be set as follows
63 1 Cell 1
The freeboard limit for Cell 1 will be set at 5 615 4 FMSL This will allow Cell 1 to capmre all of
the PMP volume associated with Cell 1 The total volume requirement for Cell 1 is 103 acre feet
divided by 52 9 acres equals 1 95 feet plus the wave mn up factor of0 90 feet equals 2 85 feet The
freeboard linut is dien 5 618 2 FMSL minus 2 85 feet equals 5 615 4 FMSL Under Radioactive
Matenals License condition 10 3 this freeboard limit is set and is not recalculated annually
632 Cell 2
The freeboard limit for Cell 2 is inapplicable since Cell 2 is filled with solids All of the PMP
volume associated with Cell 2 will be attnbuted to Cell 4A (and/or any future tailings cells)
633 Cell 3
The freeboard limit for Cell 3 is inapplicable since Cell 3 is close to being filled with solids and all
of the PMP flood volume associated with Cell 3 will be attnbuted to Cell 4B (and/or any fumre
tailings cells)
634 Cell 4A
The freeboard limit for Cell 4A is inapplicable since all of the PMP flood volume associated with
Cell 4A will be attnbuted to Cell 4B A spillway has been added to Cell 4A to allow overflow into
CeU 4B
635 Cell 4B
The freeboard limit for Cell 4B will be set assurmng that the total PMP volume for Cells 2 3 4A
and 4B of 159 4 acre feet will be accommodated in Cell 4B The procedure for calculating the
freeboard limit for Cell 4B is as follows
(a) When the Pool Surface Area is 40 Acres
When the pool surface area in Cell 4B is 40 acres (i e when there are no beaches) the freeboard
limit for Cell 4B will be 5 594 6FMSL which is 5 7 feet below die FML This freeboard value was
developed as follows
PMP Flood Volume 38 1 acre feet
Overflow from Cell 4A assuming no storage in Cell 3 or 4A 159 4 acre feet
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Book 11 Envu-onmental Protection Manual Section 3 1 Page 2 lof 53
Sum of PMP volume and overflow volume 197 5 acre feet
Depth to store PMP an overflow volume
= 197 5 acre feet/40 acres 4 9 feet
Wave mn up factor 0 77 feet
Total required freeboard 5 7 feet
(all values in the above calculation have been rounded to the nearest one tenth of afoot)
(b) When the Maximum Elevation ofthe Beach Area is 5 594 FMSL or Less
When the maximum elevation of the beach area in Cell 4B is 5594 FMSL or less then the freeboard
lirmt will be 5 594 6 FMSL which is the same as m (a) above This allows for the simation where
there may be beaches but these beaches are at a lower elevation than the freeboard limit estabhshed
in (a) above and there is therefore ample freeboard above the beaches to hold the maximum PMP
volume The maximum elevation of the beach area will be detemuned by monthly surveys
performed by Mill personnel in accordance with the Mill s DMT Plan
(c) When the Maximum Elevation ofthe Beach Area First Exceeds 5 594 FMSL
When the maximum elevation of the beach area m Cell 4B first exceeds 5 594 FMSL then the
freeboard limit for the remainder of the ensuing year (penod t=0) (untU the next November 1) wiU be
calculated when that elevation is first exceeded (the Initial C^culation Date ) as follows
i) The total number of dry tons of tailings that have hi stoncally been deposited into CeU
4B pnor to the Initial Calculation Date ( To ) will be detenmned
u) The expected number of dry tons to be deposited into Cell 4B for the remainder of the
ensuing year (up to the next November 1) based on production estimates for that
penod ( Ao* ) will be detemuned
111) Ao* will be grossed up by a safety factor of 150% to allow for a potential
underestimation of the number of tons that wdl be deposited in the cell dunng the
remainder of the ensuing year This grossed up number can be referred to as the
modeled tonnage for the penod
iv) The total design tailings solid storage capacity of Cell 4AB will be accepted as
2 094 000 dry tons of ladings
v) The available remaining space in Cell 4B for solids as at the Initial Calculation Date
will be calculated as 2 094 000 dry tons minus To
vi) The reduction in the pool surface area for the remainder of the ensuing year will be
assumed to be direcdy proportional to the reduction in the available space in Cell 4A
4B for solids That is the reduced pool surface area for penod t=0( RPAo ) afterthe
reduction will be calculated to be
(1 - (Ao* X 1 5) / (2 094 000 To)) x 40 acres = RPAQ
vu) The required freeboard for Cell 4A-4B for the remainder of the penod t=0 can be
calculated in feet to be the wave mn up factor for Cell 4B of 0 77 feet plus the
quotient of 197 5 acre feet divided by the RPAo The freeboard Imut for Cell 4B for
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Book 11 Environmental Protection Manual Section 3 1 Page 22 of 53
the remainder of penod t=0 would then be the elevation of the FML for Cell 4B of
5594 0 FMSL less this required freeboard amount rounded to the nearest one tenth of
afoot and
Vlll) The foregoing calculations will be performed at the Imtial Calculation Date and the
resulting freeboard limit will persist until the next November 1
An example of this calculation is set out in Appendix F
(d) Annual Freeboard Calculation When the Maximum Elevation ofthe Beach Area Exceeds
5 594 FMSL
On November 1 of each year (the Annual Calculation Date ) the reduction in pool area for the
ensuing year (refened to as penod t) will be calculated by
i) First calculating the Adjusted Reduced Pool Area for the previous penod (ARPAt 0
to reflect actual tonnages deposited in Cell 4B for the previous penod (penod t 1)
The RPAt 1 used for the previous penod was based on expected tonnages for penod t
1 grossed up by a safety factor The ARPAt i is merely the RPA that would have
been used for penod t 1 had the actual tonnages for year t I been known at die outset
of penod t 1 and had the RPA been calculated based on the acmal tonnages for penod
t 1 This allows the freeboard calculations to be corrected each year to take into
account acmal tonnages deposited in the cell as of the date of the calculation The
ARPAt 1 can be calculated using the following formula
(1 - At 1 / (2 094 000 - Tt 0) x ARPAt 2 = ARPAt 1
Where
• A, 1 IS the acmal number of dry tons of tailings solids deposited in Cell 4B
dunng penod t 1
• Tt 1 IS the actual number of dry tons of tailings solids histoncally deposited in
Cell 4B pnor to the beginmng of penod t 1 and
• ARPAt 2 IS the Adjusted Reduced Pool Area for penod t 2 If penod t 2
started at the Imtial Calculation Date then ARPAt 2 is 40 acres
11) Once the ARPA, 1 for the previous penod (penod t 1) has been calculated the RPA
for the subject penod (penod t) can be calculated as follows
(1 - (At* X 1 5) / (2 094 000 Tt)) x ARPAt 1 = RPAt
Where
• A,* IS the expected number of dry tons of tailings to be deposited mto Cell 4B
for the ensuing year (penod t) based on production estimates for the year (as
can be seen from the foregoing formula this expected number is grossed up
by a safety factor of 1 5)
• Tt IS the acmal number of dry tons of tailings solids histoncally deposited in
Cell 4B pnor to the beginmng of penod t and
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Book 11 Environmental ProtecUon Manual SecUon 3 1 Page 23 of 53
• ARPAt 1 IS the Adjusted Reduced Pool Area for penod t 1 which is the pool
surface area for the previous penod (penod t 1) that should have applied
dunng that penod had modeled tonnages (i e expected tonnages grossed up
by the 150% safety factor) equaled acmal tonnages for the penod
111) The required freeboard for penod t can be calculated m feet to be the wave mn up
factor for Cell 4B of 0 77 feet plus the quotient of 197 5 acre feet divided by die RPA,
The freeboard limit for Cell 4A-4B for penod t would then be the elevation of the
FML for Cell 4B of 5594 0 FMSL less this required freeboard amount rounded to the
nearest one tenth of a foot and
iv) The foregoing calculations will be performed at the Annual Calculation Date for
penod t and the resulting freeboard limit will persist until the next Aimual Calculation
Date for penod t-i-1
An example of this calculation is set out in Appendix F
(e) When a Spillway is Added to Cell 4B that Allows Overflow Into a New Tailings Cell
When a spillway is added between Cell 4B and a new taihngs cell then if an approved freeboard
limit calculation method for the new cell is set to cover the entire PMP event for Cells 2 3 4A 4B
and the new tailings cell the freeboard limit for Cell 4B will be inapphcable except for approved
provisions to prevent storm water mnoff from overtopping dikes
6 3 6 Roberts Pond
The freeboard linut for Roberts Pond is a liquid maximum elevation of 5 624 0 feet above mean sea
level as specified in the GWDP
6 4 Annual Leak Detection Fluid Samples
In the event solution has been detected m a leak detection system a sample will be collected on an
annual basis This sample will be analyzed according to the conditions set forth m License
Condition 11 3 C The results of the analysis will be reviewed to determine die ongm of the
solution
6 5 Annual Inspection of the Decontamination Pads
a) New Decontanunation Pad
Dunng the second quarter of each year die New Decontanunation Pad will be taken out of service
and inspected to ensure the integnty of the wash pad s exposed concrete surface If any
abnormalities are identified i e cracks in the concrete with greater than 1/8 inch separation (width)
or any significant detenoration or damage of the pad surface repairs will be made pnor to resuming
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Book 11 Envu-onmental Protection Manual SecUon 3 1 Page 24 of 53
the use of the facility All inspection findings and any repairs required shall be documented on the
Aimual Decontamination Pad Inspection form The inspection findings any repairs required and
repairs completed shall be summanzed m the 2 Quarter DMT Monitonng Report due September 1
of each calendar year
b) Existing Decontamination Pad
Dunng the second quarter of each year the Existing Decontanunation Pad will be taken out of
service and inspected to ensure the integnty of the steel tank Once the water and any sediment
present is removed from the steel tank containment the walls and bottom of the tank will be
visually inspected for any areas of damage cracks or bubbling indicating corrosion that may
have occurred since the last inspection K any abnormalities are identified defects or damage
will be reported to Mill management and repairs will be made pnor to resunung the use of the
facility All inspection findings and any repairs required shall be documented on the Annual
Decontamination Pad Inspection form A record of the repairs will be maintained as a part of the
Annual Inspection records at the Mill site The inspection findings any repairs required and
repairs completed shall be summanzed in the 2nd Quarter DMT Monitonng Report due
September 1 of each calendar year
7 OTHER INSPECTIONS
All daily weekly monthly quarterly and annual inspections and evaluations should be performed as
specified m Sections 2 3 4 5 and 6 above However additional inspections should be conducted
after any sigmficant storm or significant namral or man made event occurs
8 REPORTING REQUIREMENTS
In addition to the Daily Inspection Data Weekly Tailings Inspection Monthly Inspection Data and
(Quarterly Inspection Data forms included as Appendix A and descnbed in Sections 2 3 4 and 5
respectively and the Operating Foreman s Daily Inspection and Weekly Mill Inspection forms
descnbed m Sections 2 and 3 respectively the following additional reports shall also be prepared
8 1 Monthly Tailings Reports
Monthly tadmgs reports are prepared every month and summanze the previous month s activities
around the tailings area If not prepared by the Radiation Safety Officer the report shall be
submitted to the Radiation Safety Officer for review The Mill Manager will review the report as
well before the report is filed in the Mill Cential File The report will contain a summary of
observations of concem noted on the daily and weekly tailings inspections Corrective measures
taken dunng the month will be documented along with the observations where appropnate All daily
and weekly tailings inspection forms will be attached to the report A monthly inspection form will
also be attached Quarterly inspection forms will accompany the report when applicable The report
wdl be signed and dated by the preparer in addition to the Radiation Safety Officer and the MiU
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I White Mesa Mill - Standard Operating Procedures 07/4-401/12 Revision Denisonll 43
Book 11 Environmental Protection Manual Section 3 1 Page 25 of 53
Manager
82 DMT Reports
Quarterly reports of DMT monitonng activities which will include the following mformation wiU
be provided to the Executive Secretary on the schedule provided in Table 5 of die GWDP
a) On a quarterly basis all required information required by Part 1 F 2 of the GWDP
relating to the inspections descnbed in Section 3 1 (b) (Shmes Drain Water Level
Monitonng) 3 1(d) (Taihngs Wastewater Pool and Beach Area Elevation
Monitonng) 3 2 (Weekly Inspection of Solution Levels m Roberts Pond) and 3 3
(Weekly Feedstock Storage Area Inspections)
b) On a quarterly basis a summary of the weekly water level (depth) inspections for
the quarter for the presence of fluid m all three vertical inspection portals for each
of the three chambers m the concrete settling tank system for the New
Decontanunation Pad which will include a table indicating the water level
measurements m each portal dunng the quarter
c) With respect to the annual inspection of the New Decontamination Pad descnbed
in Section 6 5(a) the inspection findings any repairs required and repairs
completed shall be summanzed in the 2 Quarter report due September 1 of
each calendar year
d) With respect to the annual inspection of the Existing Decontamination Pad
descnbed in Section 6 5(b) the inspection findings any repairs required and
repairs completed shall be summanzed in the 2 Charter report due September 1
of each calendar year and
e) An annual summary and graph for each calendar year of the depth to wastewater
in the Cell 2 shmes drain must be included in the fourth quarter report After the
first year and beginning in 2008 quarterly reports shall include both the current
year monthly values and a graphic companson to the previous year
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Book 11 Environmental Protection Manual SecUon 3 1 Page 26 of 53
APPENDIX A
FORMS
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1 I
White Mesa Mill - Standard Operating Procedures
Book 11 Environmental Protection Manual Section 3 1
07/4401/12 Revision Demson 11 43
Page 27 of 53
APPENDIX A (CONT)
DAILY INSPECTION DATA
Inspector.
Date
Accompanied by,
Time
Any Item not OK must be documented A check mark = OK X = Action Required
I TAILINGS SLURRY TRANSPORT SYSTEM
Insoection Items Conditions of Potential Concem Cell 1 CeU 2 CeU 3 Cell 4A Cell 4B
Slurry Pipeline Leaks Damage Blockage Sharp Bends
Pipeline Joints Leaks Loose Connections
Pipeline Supports Damage Loss of Support
Valves Leaks Blocked Closed
Point(s) of Discharge Improper Location or Onentation
II OPERATIONAL SYSTEMS
Inspection Items Conditions of Potential Concem Cell 1 CeU 2 CeU 3 Cell 4A Cell 4B
Water Level Greater Than Operating Level Large Change
Since Previous Inspection
Beach Cracks Severe Erosion Subsidence
Lmer and Cover Erosion of cover Exposure of Liner
Liner Observable Liner Damage
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I for pcrmitVTnibngs Mgnt System and
White Mesa Mill - Standard Operating Procedures
Book 11 Environmental Protection Manual Section 3 1
07/4401/12 Revision Demson 11 43
Page 28 of 53
ni DIKES AND EMBANKMENTS
Inspection Items Conditions of Potential Dike 1 I Dike 1 Dike 2 Dike 3 Dike Dike Dike
Concem lA 4A S 4AE 4B S
Slopes Sloughs or Sbding Cracks No No No No
Bulges Subsidence Severe visible visible visible visible
Erosion Moist Areas Areas slope or slope or slope or slope or
of Seepage Outbreak dike to dike to dike to dike to
inspect inspect inspect mspect
Crest Cracks Subsidence Severe No No No No
Erosion visible visible visible visible
slope or slope or slope or slope or
dike to dike to dike to dike to
inspect inspect inspect inspect
rv FLOW RATES
Slurry Linefs) Pond Remm S X Tails Spray Svstem
GPM
V PHYSICAL INSPECTION OF SLURRY LINES(S)
Walked to Discharge Point
Observed Entire Discharge Line
_Yes
Yes
_No
No
VI DUST CONTROL
CeU 2 CeU 3 CeU 4A Cell 4B
Dusting
Wind Movement of Tailings
Precipitation inches liquid
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White Mesa Mill - Standard OperaUng Procedures
Book 11 Environmental Protection Manual Section 3 1
07/1401/12 Revision Demson 11 43
Page 29 of 53
General Meteorological conditions
VII DAILY LEAK DETECTION CHECK | |
CeU 1 CeU 2 CeU 3 Cell 4A Cell 4B
Leak
Detection
System
Checked
Checked Checked Checked Checked Checked Leak
Detection
System
Checked
Wet Drv Wet Drv Wet Drv Wet Drv Wet Drv
Leak
Detection
System
Checked
Initial level Initial level Initial level Initial level Initial level
Leak
Detection
System
Checked
Final
level
Final
level
Final
level
Final
level
Final
level
Leak
Detection
System
Checked
Gal pumped Gal pumped Gal pumped Gal pumoed Gal pumped
Vin OBSERVATIONS OF POTENTLVL CONCERN Action Required
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I for permitVTaihngs Mgnt System and
Tailmgs Dail>' Inspection Report
Taihngs Shiii"^ Dischaige Location
o o
Q (2
•5 <zi
2 1
O rri
U
MILL SITE
CELL NO 1
CELL NO 4A /
Date
hispectoi
White Mesa Mill - Standard Operating Procedures 07/1101/12 Revision Denisonl 1 43
Book 11 Environmental Protection Manual Section 3 1 Page 31 of 53
APPENDIX A (CONT)
DENISON MINES (USA) CORP
WEEKLY TAILINGS INSPECTION
Date Inspectors
1 Pond and Beach CeH 1 (a) Pond SoluUon Elevation
elevations (msl ft)
(b) FML Bottom Elevation 5597.
(c) Depth of Water above FML ((a) (b))
Cell4A (a)Pond Solution Elevation
(b) FML Bottom Elevation 5555 14_
(c) Depth of Water above FML ((a) (b))
Cen4B (a)Pond Solution Elevation
(b) FML Bottom Elevation 5557 50
(c) Depth of Water above FML ((a) (b))
(d) Elevation of Beach Area with Highest Elevation
(monthly)
Roberts
Pond (a)Pond SoluUon Elevation
(b) FML Bottom Elevation ^5612 3_
(c) Depth of Water above FML ((a) (b))
2 Slimes Dram Liquid Levels Cell 2 Pump funcuoning properly.
_Depth to Liquid pre pump
.Depth to Liquid Post pump
(all measurements are depth in pipe)
Pre pump head is 38-37 97 Depth to Liquid Pre
pump =
Post pump head is 3&-37 97 -Depth to Liquid
Post pump =
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Book 11 Environmental Protection Manual SecUon 3 1
07/4401/12 Revision Denisonl I 43
Page 32 of 53
3 Leak Detection Systems
(Same data as Daily Inspection Form Record data on daily form)
Observation
New Decon Pad.
Portal 1
New Decon Pad.
Portal 2
New Decon Pad
Portal 3
Is LDS (Portal)
wet or dry*^
_wet dry _wet dry _wet ^dry
If wet Record
bquid level Liquid
Ft to
Liquid
Ft to Ft to
Liquid
If wet Report to
RSO
4 Taihngs Area Inspection (Note dispersal of blowing tailings)
5 Control Methods Implemented
6 Remarks.
7 Contaminated Waste DumpDesignated Disposal Area for Non Tailings Mill Waste (awaiting DRC
approval)
* Does Level exceed 12 mches above the lowest point on the bottom flexible membrane liner (solution
eievauon of 5556 14 amsl for Cell 4A and 5558 50 for CeU 4B)'> no yes
If Cell 4A leak detection system level exceeds 12 inches above the lowest point on the bottom flexible
membrane liner (elevation 5556 14 amsl) notify supervisor or Mill manager immediately
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Book 11 Environmental ProtecUon Manual Section 3 1 Page 33 of 53
APPENDIX A (CONT)
MONTHLY INSPECTION DATA
Inspector
Date
1 Slurry Pipelme
2 Diversion Ditches and Diversion Berm
Observation
Diversion Ditch 1 Diversion Ditch 2 Diversion Ditch 3 Diversion Berm 2
Diversion Ditches
Sloughing yes no yes no yes no
Erosion yes no yes no yes no
Undesirable yes no yes no yes no
VegetaUon
Obstmction of Row yes no yes no yes no
Diversion Berm
Stability Issues yes no
Signs of Distress yes no
Comments
3 Summary of Activities Around Sedimentation Pond
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Book 11 Environmental Protection Manual SecUon 3 1 Page 34 of 53
4 Overspray Dust Minimization
Overspray system functioning properly yes no
Overspray earned more than 50 feet from the cell yes no
If yes was system immediately shut off yes no
Comments
5 Remarks
6 Settlement Monitors
Cell 2 Wl CeU 2W3 S CeU 3 IN _
Cell 2 W2 Cell 2E1 N CeU 3 IC _
Cell2W3 CeU2El IS CeU 3 IS _
Cell 2 W4 Cell 2E1 2S Cell 3 2N _
Cell 2W7 C Cell 2 East Cell 2W5 N
Cell 2 W7N Cell 2 W7S Cell 2 W6N
Cell2W6C Cell2W6S Cen2W4N
Cell 4A Toe Cell 2 W4S Cell 2 W5C
Cen3 2C Cen3 2S Cen2W5S
Cell 3 3S Cell 3 3C. Cell3 3N
Cell 3^N Cell 3 6N Cell 3 7S
Cell 3 7C Cell 3 7N Cell 3 8S
Cell 3 8C Cell 3 8N
7 Movement Monitors (Is there visible damage to any movement monitor or to adjacent
surfaces)*^
8 Summary of Dady Weekly and Quarterly Inspections
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Book 11 Environmental Protection Manual SecUon 3 1 Page 35 of 53
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I White Mesa Mill - Standard Operating Procedures
Book 11 Environmental Protection Manual Section 3 1
07/4401/12 Revision Denisonl 1 43
Page 36 of 53
APPENDIX A (CONT)
WHITE MESA MILL
TAILINGS MANAGEMENT SYSTEM
QUARTERLY INSPECTION DATA
Inspector
Date
I Embankment Inspection
2 Operations/Maintenance Review
3 Construction Activities
4 Estimated Areas
CeU 3 Cell 4A Cell 4B
Estimated percent of beach surface area
Estimated percent of solution pool area
Estimated percent of cover area
Coniments
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White Mesa Mill - Standard Operating Procedures 07/4401/12 Revision Denisonl 143
Book 11 Envnonmental Protection Manual Section 3 1 Page 37 of 53
APPENDIX A (CONT)
ORE STORAGE/SAMPLE PLANT WEEKLY INSPECTION REPORT
Week of through Date of Inspection
Inspector
Weather conditions for the week
Blowing dust conditions for the week
Corrective actions needed or taken for the week
Are all bulk feedstock materials stored in the area indicated on the attached diagram
yes no
comments
Are all alternate feedstock matenals located outside the area indicated on the attached diagram maintained
within water tight containers
yes no
comments (e g conditions of containers).
Are all sumps and low lying areas free of standing soluUons''
Yes No
If No how was the situation corrected supervisor contacted and correction date"^
Is there free standing water or water mnning off of the feedstock stockpiles'^
Yes No
Comments
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Book 11 Environmental ProtecUon Manual SecUon 3 1 Page 38 of 53
Other comments
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Book 11 Environmental Protection Manual Section 3 1 Page 39 of 53
APPENDIX A (CONT)
ANNUAL DECONTAMINATION PAD INSPECTION
Date of Inspection
Inspector
New Decontamination Pad
Are there any cracks on the wash pad surface greater than 1/8 inch of separation'' Yes No
Is there any significant deterioration or damage of the pad surface'' Yes No
Findings
Repair Work Required
Existing Decontamination Pad
Were there any observed problems with the steel tank'' Yes No
Findings
Repair Work Required
Note For the annual inspection of die both the Existing and New Decontanunation Pads the
annual inspection findings any repairs required and repairs completed along with a summary of
the weekly inspections shall be discussed in the 2 Quarter report due September 1 of each
calendar year
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White Mesa Mill - Standard Operating Procedures 07/4401/12 Revision Demsonll43
Book 11 Environmental Protection Manual Section 3 1 Page 40 of 53
APPENDIX B
8 3 TAILINGS INSPECTOR TRAINING
This document provides the tiaimng necessary for qualifying management designated individuals for
conducting daily tailings inspections Training information is presented by the Radiation Safety
Officer or designee from the Environmental Department Dady tailmgs mspections are conducted in
accordance with the White Mesa Mill Tailings Management System and Discharge Minmuzation
Technology (DMT) Monitonng Plan The Radiation Safety Officer or designee from the Radiation
Safety Department is responsible for perfomung monthly and quarterly ladings inspections Tailings
inspection forms will be included in the monthly tailings inspection reports which summanze the
conditions activities and areas of concem regarding the tailings areas
Notifications
The inspector is required to record whether all inspection items are normal (satisfactory requinng no
action) or that conditions of potential concem exist (requinng action) A check mark indicates no
action required If conditions of potential concem exist the inspector should mark an X in the area
the condition pertains to note the condition and specify the conective action to be taken If an
observable concem is made it should be noted on the tailings report until the corrective action is
taken and the concem is remedied The dates of all corrective actions should be noted on the reports
as well
Any major catastiophic events or conditions pertaimng to the tailings area should be reported
immediately to the Mill Manager or the Radiation Safety Officer one of whom wdl notify Corporate
Management If dam failure occurs notify your supervisor and the Mill Manager immediately The
Mill Manager will dien notify Corporate Management MSHA (303 231 5465) and the State of
Utah Division ofDam Safety (801 538 7200)
Inspections
All areas of the tailmgs disposal system are routinely patrolled and visible observations are to be
noted on a daily tailings inspection form Refer to Appendix A for an example of the daily tailings
inspection form The inspection form consists of three pages and is summanzed as follows
1 Taihngs Slurry Transport System
The slurry pipeline is to be inspected for leaks damage and sharp bends The pipeline jomts
are to be monitored for leaks and loose coimections The pipeline supports are to be
inspected for damage and loss of support Valves are also to be mspected particularly for
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I White Mesa Mill - Standard Operating Procedures 07/4401/12 Revision Denisonl 1 43
Book 11 Environmental ProtecUon Manual Section 3 1 Page 41 of 53
leaks blocked valves and closed valves Pomts of discharge need to be mspected for
improper location and onentation
Operational Systems
Operating systems including water levels beach liners and covered areas are items to be
inspected and noted on the daily inspection forms Sudden changes in water levels
previously observed or water levels exceeding the operating level of a pond are potential
areas of concem and should be noted Beach areas that are observed as having cracks severe
erosion or cavities are also items that require investigation and notation on daily forms
Exposed lmer or absence of cover from erosion are potential items of concem for ponds and
covered areas These should also be noted on the daily inspection form
Cells 1 3 4A and 4B solution levels are to be monitored closely for conditions neanng
maximum operating level and for large changes in the water level since the last inspection
All pumping activities affecting the water level will be documented In Cells 1 and 3 the
PVC liner needs to be momtored closely for exposed liner especially after storm events It is
important to cover exposed liner immediately as exposure to sunlight will cause degradation
of the PVC liner Small areas of exposed liner should be covered by hand Large sections of
exposed liner will require the use of heavy equipment
These conditions are considered senous and require immediate action After these conditions
have been noted to the Radiation Safety Officer a work order will be wntten by the
Radiation Safety Officer and mmed into the Maintenance Department All such repairs
should be noted in the report and should contain the start and finish date of the repairs
Dikes and Embankments
Inspection items include the slopes and the crests of each dike For slopes areas of concem
are sloughs or sliding cracks bulges subsidence severe erosion moist areas and areas of
seepage outbreak For crests areas of concem are cracks subsidence and severe erosion
When any of these conditions are noted an X mark should be placed m the section marked
for that dike
In addition the dikes in particular dikes 4A S 4A E and 4B S should be mspected closely
for rmce holes and more importantly for praine dog holes as the praine dogs are likely to
burrow in deep possibly to the liner If any of these conditions exist the inspection report
should be marked accordingly
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Book 11 Environmental ProtecUon Manual SecUon 3 1 Page 42 of 53
4 Flow Rates
Presence of all flows m and out of the cells should be noted Flow rates are to be estimated
in gallons per minute (GPM) Rates need to be detemuned for slurry lines pond remm SX
tads and the spray system Dunng non operational modes the flow rate colunm should be
marked as 0 The same holds tme when the spray system is not utilized
5 Physical Inspection of Slurry Line(s)
A physical inspection of all slurry lines has to be made every 4 hours dunng operation ofthe
null If possible the inspection should include observation of the entire discharge line and
discharge spill point mto the cell If fill to elevation flags are in place the tadmgs and
build up IS to be monitored and controlled so as to not cover the flags
6 Dust Control
Dusting and wind movement of tailings should be noted for Cells 2 3 4A and 4B Other
observations to be noted mclude a bnef descnption of present weather conditions and a
record of any precipitation received Any dusting or wind movement of tailings should be
documented In addition an estimate should be made for wind speed at the time of the
observed dusting or wind movement of tailmgs
The Radiation Safety Department measures precipitation on a daily basis Daily
measurements should be made as near to 8 00 a m as possible every day Weekend
measurements will be taken by Environmental Health and Safety personnel as close to 8 00
a m as possible All snow or ice should be melted before a reading is taken
7 Observations of Potential Concern
All observations of concem dunng the inspection should be noted in this section Conective
action should follow each area of concem noted All work orders issued contacts or
notifications made should be noted in this section as well It is important to document all
these Items in order to assure that the tailings management system records are complete and
accurate
8 Map of Taihngs Cells
The last section of the mspection involves drawing as accurately as possible the following
Items where apphcable
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Book 11 Environmental ProtecUon Manual SecUon 3 1 Page 43 of 53
1 Cover area
2 Beach/tailing sands area
3 Solution as it exists
4 Pump lines
5 Activities around tailings cell (i e hauling trash to the dump liner repairs etc )
6 Slurry discharge when operating
7 Over spray system when operating
9 Safety Rules
All safety mles applicable to the null are applicable when in the tailings area These mles
meet the required MSHA regulations for the tailings area Please pay particular notice to the
following mles
1 The posted speed limit on Cell 4A and 4B dike is 5 mph and the posted speed limit for
the tailings area (other than the Cell 4A and 4B ddce) is 15 mph These linuts should not
be exceeded
2 No food or dnnk is permitted in the area
3 All personnel entenng the ladings area must have access to a two way radio
4 Horseplay is not penmtted at any time
5 Only those specifically authonzed may operate motor vehicles in the restncted area
6 When road conditions are muddy or slick a four wheel dnve vehicle is required in the
area
7 Any work performed in which there is a danger of falling or slipping in the cell will
require the use of a safety belt or hamess with attended life line and an approved life
jacket A portable eyewash must be present on site as well
8 Anytime the boat is used to perform any work an approved life jacket and goggles must
be wom at all times There must also be an approved safety watch with a two way hand
held radio on shore A portable eyewash must be present on site as well
10 Preservation of Wildhfe
Every effort should be made to prevent wildlife and domesticated animals from entenng the
tailings area All wildlife observed should be reported on the Wildlife Report Worksheet
dunng each shift Waterfowl seen near the tailings cells should be discouraged from landing
by the use of noisemakers
11 Certification
Following the review of this document and on site instmction on the tailings system
inspection program designated individuals will be certified to perform daily tailings
inspections The Radiation Safety Officer audionzes certification Refer to the Certification
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Book 11 Environmental Protection Manual Section 3 1 Page 44 of 53
Form Appendix C This form should be signed and dated only after a thorough review of the
tailings information previously presented The form will then be signed by the Radiation
Safety Officer and filed
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Book 11 Environmental Protection Manual SecUon 3 1 Page 45 of 53
APPENDIX C
CERTIFICATION FORM
Date
Name
I have read the document titled Tailings Management System White Mesa Mill Tailings
Inspector Training and have received on site mstmction at the tailings system This instmction
included documentation of daily tailmgs inspections analysis of potential problems (dike
failures unusual flows) notification procedures and safety
Signamre
I certify that the above named person is qualified to perform the daily inspection of the tailings
system at the White Mesa Mill
Radiation Safety Personnel/ Tailings System
Supervisor
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Book 11 Envnonmental ProtecUon Manual Section 3 1 Page 46 of 53
APPENDIX D
FEEDSTOCK STORAGE AREA
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White Mesa Mill - Standard Operating Procedures
Book 11 Environmental Protection Manual Section 3 1
07/4401/12 Revision Denisonl 143
Page 47 of 53
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Book 11 Environmental Protection Manual SecUon 3 1 ^ Page 48 of 53
APPENDDC E
TABLES
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t
I White Mesa Mill - Standard Operating Procedures
Book 11 Environmental Protection Manual Secuon 3 1
07/4401/12 Revision Denisonll 43
Page 49 of 53
Table lA
Calculated Action leakage Rates
for Vanous head Conditions
Cell 4A White mesa Mill
Blanding Utah
Head above Lmer System (feet) Calculated Action leakage Rate
(gallons / acre / day)
5 222 04
10 31401
15 384 58
20 444 08
25 496 50
30 543 88
35 587 46
37 604 01
Table IB
Calculated Action leakage Rates
for Vanous head Conditions
Cell 4B White mesa Mill
Blanding Utah
Head above Liner System (feet) Calculated Action leakage Rate
(gallons / acre / day )
5 21140
10 317 00
15 369 90
20 422 70
25 475 60
30 528 40
35 570 00
37 581 20
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Book 11 Environmental Protection Manual SecUon 3 1 Page 50 of 53
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White Mesa Mill - Standard OperaUng Procedures
Book 11 Environmental Protection Manual Section 3 1
07/4401/12 Revision Denisonll 4^
Page 51 of 53
APPENDIX F
Example of Freeboard Calculations
For CeU 4B
Assumptions and Factors
o Total PMP volume to be stored in CeU 4A - 159 4 acre feet
o Wave mnup factor for CeU 4AB - 0 77 feet
o Total capacity of Cell 4B - 2 094 000 dry tons
o Elevation of FML of Cell 4B - 5 600 35 FMSL
o Maximum pool surface area of Cell 4A-4B - 40 acres
o Total tailings sohds deposited into Cell 4B at time beach area first exceeds 5 594
FMSL - 1 000 000 dry tons*
o Date beach area first exceeds 5 594 FMSL - March 1 2012*
o Expected and acmal production is as set forth in the following table
Time Period Expected
Tailings Sohds
Disposition into
CeU 4B
Determined at
the beginnmg of
the penod (dry
tons)*
Expected
Tailings
Sohds
Dispositio
n into Cell
4B at the
beginning
of the
penod
multiplied
by 150%
Safety
Factor
(dry tons)
Actual Taihngs
Sohds
Disposition into
Cell 4B
determined at
end of the
period (dry
tons)*
March 1 2012
to November 1
2012
150 000 225 000 225 000
November 1
2012 to
November 1
2013
300 000 450 000 275 000
November 1
2013 to
November 1
2014
200 000 300 000 250 000
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Book 11 Environmental ProtecUon Manual Section 3 1 Page 52 of 53
*These expected and acmal tailings and production numbers and dates are fictional and have
been assumed for illustrative purposes only
Based on these assumptions and factors the freeboard limits for Cell 4B would be calculated
as follows
1 Pnor to March 1.2012
Pnor to March 1 2012 the maximum elevation of the beach area in Cell 4B is less than or
equal to 5 594 FMSL dierefore die freeboard limit is set at 5 594 6 FMSL
2 March 1. 2012 to November 1. 2012
The pool surface area would be reduced to the followmg amount
(1-225 000 / (2 094 000 - 1 000 000)) x 40 acres = 31 77 acres
Based on this reduced pool area the amount of freeboard would be 197 5 acre feet divided by 31 77
acres equals 6 22 feet When die wave mn up factor for Cell 4B of0 77 feet is added to this the total
freeboard required is 6 99 feet This means that the freeboard limit for Cell 4B would be reduced
from 5594 6 FMSL to 5592 2 FMSL (5594 6 FMSL nunus 6 22 feet rounded to the nearest one
tenth of a foot) This calculation would be performed at March 1 2012 and this freeboard limit
would persist until November 1 2012
3 November 1. 2012 to November 1. 2013
The pool surface area would be reduced to the following amount
First recalculate the pool surface area that should have applied dunng the previous penod
had modeled tonnages (i e expected tonnages grossed up by the 150% safety factor) equaled
actual tonnages for the penod Since the actual tonnage of 225 000 dry tons was the same as
the modeled tonnage of 225 000 dry tons the recalculated pool surface area is the same as
the modeled pool surface area for the previous penod which is 31 77 acres
Then calculate the modeled pool surface area to be used for the penod
(1 - 450 000/ (2 094 000 - 1 000 000 225 000)) x 31 77 acres = 15 32 acres
Based on this reduced pool area the amount of freel)oard would be 197 5 acre feet divided by
15 32 acres equals 12 89 feet When the wave mn up factor for Cell 4B of0 77 feet is added
to this the total freeboard required is 13 66 feet This means that the freeboard limit for Cell
4B would be reduced from 5592 2 FMSL to 5586 7 FMSL (5600 35 FMSL minus 13 66
feet rounded to the nearest one tenth of a foot) This calculation would be performed at
November 1 2012 and this freeboard linut would persist until November 1 2013
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Book 11 Envu-onmental ProtecUon Manual Section 3 1 Page 53 of 53
4 November 1. 2013 to November 1. 2014
The pool surface area would be reduced to the following amount
First recalculate the pool surface area that should have applied dunng the previous penod
had modeled tonnages (i e expected tonnages grossed up by the 150% safety factor) equaled
acmal totmages for die penod Since modeled tonnages exceeded acmal tonnages the pool
area was reduced too much dunng the previous penod and must be adjusted The
recalculated pool area for the previous penod is
(1-275 000/ (2 094 000 - 1 000 000 225 000) x 31 77 acres = 21 72 acres
This recalculated pool surface area will be used as die starting point for the freeboard
calculation to be performed at November 1 2013
Then calculate the modeled pool surface area to be used for the penod
(1-300 000 / (2 094 000 - 1 000 000 225 000 - 275 000)) x 21 72 acres:
10 75 acres
Based on this reduced pool area the amount of freeboard would be 197 5 acre feet divided by
10 75 acres equals 18 37 feet When the wave mn up factor for Cell 4B of0 77 feet is added
to this the total freeboard required is 19 14 feet This means that the freeboard limit for CeU
4B would be reduced from 5586 7 FMSL to 5581 2 FMSL (5600 4 FMSL minus 18 4 feet
rounded to the nearest one tenth of a foot) This calculation would be performed at
November 1 2013 and this freeboard limit would persist until November 1 2014
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