DRC-2010-003394 - 0901a0688018ee7a

DENISO
MINES
Sent VIA Federal Express
May 28, 2010
Denlson Mines (USA) Corp.
105017th Street, Suite 950
Denver, CO 802S5
USA
Tel: [phone]
Fax:[phone]S
www.(ien]sonmines.com
Mr. Dane L. Finerfrock
Co-Executive Secretary
Utah Water Quality Board
State of Utah Department of Environmental Quality
195 North 1950 West
Salt Lake City, UT 84114-4820
Re: Transmittal of 1st Quarter 2010 Routine Chloroform Monitoring Report
UDEQ Docket No. UGQ-20-01- White Mesa Uranium Mill
Dear Mr. Finerfrock:
Enclosed are two copies of the White Mesa Uranium Mill Chloroform Monitoring Report for the
1st Quarter of 2010 as required by the Notice of Violation and Groundwater Corrective Action
Order, UDEQ Docket No. UGQ-20-01 as well as two CDs each containing a word searchable
electronic copy of the report.
If you should have any questions regarding this report please contact me.
Yours very truly,
DENISON MINES (USA) CORP.
Jo Ann Tischler
Director, Compliance and Permitting
CC: Ron F. Hochstein
David C. Frydenlund
Harold R. Roberts
David E. Turk
OENISOJ)~~
MINES
Sent VIA Federal Express
May 28,2010
Mr.Dane L.Finerfrock
Co-Executive Secretary
Utah Water Quality Board
State of Utah Department ofEnvironmental Quality
195 North 1950 West
Salt Lake City,UT 84114-4820
Denison Mines (USA)Corp.
1050 17th Street,Suitt 950
Denver,CO 80265
USA
Tel:303 628·n98
Fax:[phone]
_.denisonmints.com
Re:Transmittal of 1st Quarter 2010 Routine Chloroform Monitoring Report
UDEQ Docket No.UGQ-20-01-White Mesa Uranium Mill
Dear Mr.Finerfrock:
Enclosed are two copies ofthe White Mesa Uranium Mill Chloroform Monitoring Report for the
1st Quarter of2010 as required by the Notice ofViolation and Groundwater Corrective Action
Order,UDEQ Docket No.UGQ-20-01 as well as two CDs each containing a word searchable
electronic copy of the report.
Ifyou should have any questions regarding this report please contact me.
Yours very truly,
~~
DENISON MINES (USA)CORP.
Jo Ann Tischler
Director,Compliance and Permitting
CC:Ron F.Hochstein
David C.Frydenlund
Harold R.Roberts
David E.Turk

White Mesa Uranium Mill

Chloroform Monitoring Report

State of Utah
Notice of Violation and Groundwater Corrective Action Order UDEQ
Docket No. UGQ-20-01

1st Quarter
(January through March)
2010

Prepared by:

Denison Mines (USA) Corp. (DUSA)
1050 17th Street, Suite 950
Denver CO 80265

May 28, 2010
i
TABLE OF CONTENTS
1.0 INTRODUCTION................................................................................................. 1 

2.0 CHLOROFORM MONITORING ...................................................................... 1 

2.1 Samples and Measurements Taken During the Quarter ..................................... 1 

2.1.1 Chloroform Monitoring .............................................................................. 1 
2.1.2 Parameters Analyzed .................................................................................. 2 
2.1.3 Groundwater Head Monitoring ................................................................... 2 

2.2 Sampling Methodology and Equipment and Decontamination Procedures ....... 3 

2.2.1 Well Purging and Depth to Groundwater ................................................... 3 
2.2.2 Sample Collection ....................................................................................... 4 

2.3 Field Data ............................................................................................................ 4 
2.4  Depth to Groundwater Data and Water Table Contour Map .............................. 5 
2.5 Laboratory Results .............................................................................................. 5 

2.5.1 Copy of Laboratory Results ........................................................................ 5 
2.5.2 Regulatory Framework ............................................................................... 5 

3.0 QUALITY ASSURANCE AND DATA VALIDATION ................................... 6 

3.1 Field QC Samples ............................................................................................... 6 
3.2 Adherence to Mill Sampling SOPs ..................................................................... 7 
3.3 Analyte Completeness Review ........................................................................... 7 
3.4 Data Validation ................................................................................................... 7 

3.4.1 Field Data QA/QC Evaluation .................................................................... 7 
3.4.2 Holding Time Evaluation ............................................................................ 8 
3.4.3 Receipt Temperature Evaluation ................................................................. 8 
3.4.4 Analytical Method Checklist ...................................................................... 8 
3.4.5 Reporting Limit Evaluation ........................................................................ 8 
3.4.6 Trip Blank Evaluation ................................................................................. 8 
3.4.7 QA/QC Evaluation for Sample Duplicates ................................................. 8 
3.4.8 Rinsate Check ............................................................................................. 9 
3.4.9 Other Laboratory QA/QC ......................................................................... 10 

4.0 INTERPRETATION OF DATA ....................................................................... 10 

4.1 Interpretation of Groundwater Levels, Gradients and Flow Directions. .......... 10 

4.1.1 Current Site Groundwater Contour Map................................................... 10 
ii
4.1.2 Comparison of Current Groundwater Contour Maps to Groundwater
Contour Maps for Previous Quarter .......................................................... 11 
4.1.3 Hydrographs .............................................................................................. 11 
4.1.4 Depth to Groundwater Measured and Groundwater Elevation ................. 11 
4.1.5 Evaluation of the Effectiveness of Hydraulic Capture ............................. 12 

4.2 Review of Analytical Results............................................................................ 12 

4.2.1 Current Chloroform Isoconcentration Map .............................................. 12 
4.2.2 Chloroform Concentration Trend Data and Graphs .................................. 13 
4.2.3 Interpretation of Analytical Data .............................................................. 13 

5.0 LONG TERM PUMP TEST AT MW-4, TW4-15 (MW-26), TW4-19, TW4-
20, AND TW4-4 OPERATIONS REPORT ...................................................... 14 

5.1 Introduction ....................................................................................................... 14 
5.2 Pump Test Data Collection ............................................................................... 14 
5.3 Water Level Measurements .............................................................................. 15 
5.4 Pumping Rates and Volumes ............................................................................ 15 

5.4.1 MW-4 ........................................................................................................ 15 
5.4.2 TW4-19 ..................................................................................................... 15 
5.4.3 TW4-15 (MW-26) ..................................................................................... 15 
5.4.4 TW4-20 ..................................................................................................... 16 
5.4.5 TW4-4 ....................................................................................................... 16 
5.4.6 TW4-18 ..................................................................................................... 16 

5.5 Mass Removed .................................................................................................. 17 
5.6 Daily Inspections .............................................................................................. 17 
5.7 Conditions That May Affect Water Levels in Piezometers .............................. 17 

6.0 CORRECTIVE ACTION REPORT ................................................................. 17 
6.1 Identification and Definition of the Problem .................................................... 17 
6.2 Assignment of Responsibility for Investigation of the Problem ....................... 18 
6.3 Investigation and Determination of Cause of the Problem ............................... 18 
6.4 Determination of a Corrective Action to Eliminate the Problem ..................... 19 
6.5 Assigning and Accepting Responsibility for Implementing the Corrective
Action ............................................................................................................... 19 
6.6 Implementing the Corrective Action and Evaluating Effectiveness ................. 19 
6.7 Verifying That the Corrective Action Has Eliminated the Problem ................. 20 

7.0 CONCLUSIONS AND RECOMMENDATIONS ............................................ 20 

8.0 ELECTRONIC DATA FILES AND FORMAT .............................................. 21 

9.0 SIGNATURE AND CERTIFICATION ........................................................... 22 
iii
LIST OF TABLES

Table 1 Summary of Well Sampling for the Period
Table 2 Mass of Chloroform Removed Per Well Per Quarter

INDEX OF TABS
Tab A Site Plan and Perched Well Locations White Mesa Site

Tab B Order of Sampling and Field Data Worksheets

Tab C Weekly and Monthly Depth to Water Data

Tab D Kriged Current Quarter Groundwater Contour Map, Capture Zone Map, Capture
Zone Details Map, and Depth to Water Data Table

Tab E Kriged Previous Quarter Groundwater Contour Map

Tab F Hydrographs of Groundwater Elevations Over Time for Chloroform Monitoring
Wells

Tab G Depths to Groundwater and Elevations Over Time for Monitoring Wells

Tab H Laboratory Analytical Reports

Tab I Quality Assurance and Data Validation Tables
I-1 Field Data QA/QC Evaluation
I-2 Holding Time Evaluation
I-3 Receipt Temperature Check
I-4 Analytical Method Check
I-5 Reporting Limit Evaluation
I-6 Trip Blank Evaluation
I-7 QA/QC Evaluation for Sample Duplicates
I-8 QC Control Limits for Analyses and Blanks
I-9 Rinsate Check

Tab J Kriged Current Quarter Chloroform Isoconcentration Map

Tab K Analyte Concentration Data Over Time

Tab L Chloroform Concentration Trend Graphs

Tab M Chloroform Well Daily Inspection Form

Tab N CSV Transmittal Letter
1
1.0 INTRODUCTION
The presence of chloroform was initially identified in groundwater at the White Mesa
Mill (the “Mill”) as result of split sampling performed in May 1999. The discovery
resulted in the issuance of State of Utah Notice of Violation (“NOV”) and Groundwater
Corrective Action Order (“CAO”) State of Utah Department of Environmental Quality
(“UDEQ”) Docket No. UGQ-20-01, which required that Denison Mines (USA) Corp.
(“DUSA”) submit a Contamination Investigation Plan and Report pursuant to the
provisions of UAC R317-6-6.15(D).

The frequency of chloroform sampling, which was initially performed on a monthly
basis, was modified on November 8, 2003. Since that time all chloroform contaminant
investigation wells have been sampled on a quarterly basis.

This is the Quarterly Chloroform Monitoring Report, as required under the NOV and
CAO for the 1st Quarter of 2010. This Report also includes the Operations Report for the
Long Term Pump Test at MW-4, TW4-19, TW4-15 (MW-26), TW4-20, and TW4-4 for
the Quarter.
2.0 CHLOROFORM MONITORING
2.1 Samples and Measurements Taken During the Quarter

A map showing the location of all groundwater monitoring wells, piezometers, existing
wells, temporary chloroform contaminant investigation wells and temporary nitrate
investigation wells is attached under Tab A. Chloroform samples and measurements
taken during this reporting period (January through March), are discussed in the
remainder of this section.

2.1.1 Chloroform Monitoring

Quarterly sampling for chloroform monitoring parameters is currently required in the
following wells:

TW4-1 TW4-10 TW4-21
TW4-2 TW4-11 TW4-22
TW4-3 TW4-12 TW4-23
TW4-4 TW4-13 TW4-24
TW4-5 TW4-14 TW4-25
TW4-6 TW4-16 MW-4
TW4-7 TW4-18 MW-26 (TW4-15)
TW4-8 TW4-19 MW-32 (TW4-17)
TW4-9 TW4-20

2
Table 1 provides an overview of all wells sampled during the current period, along with
the date samples were collected from each well, and the date(s) which analytical data
were received from the contract laboratory. Table 1 also identifies equipment rinsate
samples collected, as well as sample numbers associated with the DI field blank and any
required duplicates.

As indicated in Table 1, chloroform monitoring was performed in all of the required
chloroform monitoring wells.
2.1.2 Parameters Analyzed

Wells sampled during this reporting period were analyzed for the following constituents:

• Chloroform
• Chloromethane
• Carbon tetrachloride
• Methylene chloride
• Chloride
• Nitrate plus Nitrite as Nitrogen

Use of analytical methods is consistent with the requirements of the Chloroform
Investigation Monitoring Quality Assurance Program (the “Chloroform QAP”) attached
as Appendix A to the White Mesa Uranium Mill Groundwater Monitoring Quality
Assurance Plan.
2.1.3 Groundwater Head Monitoring

Depth to groundwater was measured in the following wells and/or piezometers, pursuant
to Part I.E.3 of the Groundwater Discharge Permit (the “GWDP”):

• The quarterly groundwater compliance monitoring wells.
• Existing monitoring well MW-4 and all of the temporary chloroform investigation
wells.
• Piezometers – P-1, P-2, P-3, P-4 and P-5.
• MW-20 and MW-22.
• Nitrate monitoring wells.
• In addition to the above, depth to water measurements are routinely observed in
conjunction with sampling events for all wells sampled during quarterly and
accelerated efforts, regardless of the sampling purpose.

All well levels used for groundwater contour mapping were measured and recorded
within 5 calendar days of each other as indicated by the measurement dates in the
summary sheet under Tab D.

3
In addition, weekly and monthly depth to groundwater measurements were taken in MW-
4, TW4-15 (MW-26), TW4-19, TW4-20, and, commencing regulrarly on March 1, 2010
for TW4-4, as part of the long term pumping test for MW-4.

2.2 Sampling Methodology and Equipment and Decontamination Procedures

DUSA completed, and transmitted to UDEQ on May 25, 2006, a revised Quality
Assurance Plan (“QAP”) for sampling under the Mill’s GWDP. While the water
sampling conducted for chloroform investigation purposes has conformed to the general
principles set out in the QAP, some of the requirements in the QAP were not fully
implemented prior to UDEQ’s approval for reasons set out in correspondence to UDEQ
dated December 8, 2006. Subsequent to the delivery of the December 8, 2006 letter,
DUSA discussed the issues brought forward in the letter with UDEQ and has received
correspondence from UDEQ about those issues. In response to UDEQ’s letter and
subsequent discussions with UDEQ, DUSA has incorporated changes in chloroform QA
procedures in the form of the Chloroform QAP, which is a separate Appendix A to the
QAP. The Chloroform QAP describes the differing needs of the chloroform investigation
program, and is an attachment to the GWDP QAP where QA requirements for the
chloroform investigation are addressed. On June 20, 2009 Chloroform QAP was
modified to require that the quarterly chloroform reports include additional items specific
to DUSA’s ongoing pump testing and chloroform capture efforts.

The sampling methodology, equipment and decontamination procedures that were
performed for the chloroform contaminant investigation, as summarized below, are
consistent with the QAP and the Chloroform QAP.
2.2.1 Well Purging and Depth to Groundwater

A list of the wells in order of increasing chloroform contamination is generated quarterly.
The order for purging and sampling is thus established. The list is included with the
Field Data Worksheets under Tab B. Mill personnel start purging with all of the non
detect wells and then move to the more contaminated wells in order of chloroform
contamination. The order of well purging and sampling for the first quarter is included in
Tab B.

Before leaving the Mill office, the portable pump and hose are rinsed with deionized
(“DI”) water. Mill personnel then proceed to the first well which is the well with the
lowest concentration of chloroform based on the previous quarter’s sampling results.
Well depth measurements are taken and the two casing volumes are calculated for those
wells which do not have a dedicated pump (measurements are made using the same
instrument used for the monitoring wells under the Mill’s GWDP). If the well has a
dedicated pump, it is pumped on a set schedule per the remediation plan and is
considered sufficiently evacuated to immediately collect a sample (however, if a pumping
well has been out of service for 48 hours or more, DUSA will follow the purging
requirements outlined in Section 6.2.7(d)(v) of the QAP. The dedicated pump is used to
collect parameters and to collect the samples. If the well does not have a dedicated
pump, a Grundfos pump ( 9 - 10 gpm pump) is then lowered to the screened interval in
4
the well and purging is started. The purge rate is established for the well by using a
calibrated 5 gallon bucket. The purging of the well is completed per Section 6.2.5 of the
QAP. In wells where the portable pump is used, a disposable bailer is used to collect the
samples the day following purging activities. After each use, the portable pump is
decontaminated and a rinsate sample is collected prior to reuse at the next sample
location. This process is repeated at each well location moving from least contaminated
to the most contaminated well. All wells are capped and secured prior to leaving the
sampling location.
2.2.2 Sample Collection

Samples are collected as described above. In all cases, on days when samples will be
collected, a cooler with ice is prepared. The trip blank is also gathered at that time (the
trip blank for these events is provided by the Analytical Laboratory). Once Mill
Personnel arrive at the well sites, labels are filled out for the various samples to be
collected. All personnel involved with the collection of water and samples are then
outfitted with rubber gloves. Chloroform investigation samples are collected by means of
disposable bailers.

Mill personnel use a disposable bailer to sample each well that does not have a dedicated
pump. The bailer is attached to a reel of approximately 150 feet of nylon rope and then
lowered into the well. After coming into contact with the water, the bailer is allowed to
sink into the water in order to fill. Once full, the bailer is reeled up out of the well and
the sample bottles are filled as follows:

• VOC samples are collected first. This sample consists of three 40 ml vials
provided by the Analytical Laboratory. The VOC sample is not filtered and is
preserved with HCl;

• A sample for nitrate/nitrite is then collected. This sample consists of one 250 ml.
bottle which is provided by the Analytical Laboratory. The chloride sample is
also not filtered and is preserved with H2SO4);

• A sample for chloride is then collected. This sample consists of one 250 ml.
bottle which is provided by the Analytical Laboratory. The nitrate/nitrite sample
is also not filtered and is not preserved.

After the samples have been collected for a particular well, the bailer is disposed of and
the samples are placed into the cooler that contains ice. The well is then recapped and
Mill personnel proceed to the next well.

2.3 Field Data

Attached under Tab B are copies of all Field Data Worksheets that were completed
during the quarter for the chloroform contaminant investigation monitoring wells
identified in paragraph 2.1.1 above, and Table 1.

5
2.4 Depth to Groundwater Data and Water Table Contour Map

Attached under Tab C are copies of the Depth to Water Sheets for the weekly monitoring
of MW-4, TW4-15 (MW-26), TW4-19, TW4-20, and commencing regularly on March 1,
2010, TW4-4, as well as the monthly depth to groundwater data for chloroform
contaminant investigation wells measured during the quarter. Depth to groundwater
measurements which were utilized for groundwater contours are included on the
Quarterly Depth to Water Worksheet at Tab D of this report, along with the kriged
groundwater contour map for the current quarter generated from this data. A copy of the
kriged groundwater contour map generated from the 4th quarter 2009 data is provided
under Tab E.

2.5 Laboratory Results
2.5.1 Copy of Laboratory Results

All analytical results were provided by Energy Laboratories (“EL”). Table 1 lists the
dates when analytical results were reported to the QA Manager for each well or other
sample.

Results from analysis of samples collected for the 1st Quarter chloroform contaminant
investigation are provided under Tab H of this Report. Also included under Tab H are
the results of analyses for duplicate samples and rinsate samples for this sampling effort,
as identified in Table 1, as well as results for trip blank analyses required by the
Chloroform QAP.

2.5.2 Regulatory Framework

As discussed in Section 1.0, above, the NOV and requirements of the CAO triggered a
series of actions on DUSA’s part. In addition to the monitoring program, DUSA has
equipped five wells with pumps to recover impacted groundwater, and has initiated
recovery of chloroform from the perched zone. The fifth well, TW4-4, was installed in
January 2010, and commenced pumping on January 31, 2010. It was not fully equipped
for flow measurement until March 31, 2010, when pumping when groundwater capture
flowrates and totals were first recorded. TW4-18 was equipped with a pump and
flowmeter in preparation for using water from this well to supply the New
Decontamination Pad at the Mill. Pumping commenced sporadically on March 22 and
ended on May 4, 2010.

Sections 4 and 5, below, interpret the groundwater level and flow information,
contaminant analytical results, and pump test data to assess effectiveness of DUSA’s
chloroform capture program.

6
3.0 QUALITY ASSURANCE AND DATA VALIDATION

The Mill QA Manager, which for the purposes of this Report was DUSA’s Director,
Compliance and Permitting, performed a Quality Assurance/Quality Control (“QA/QC”)
review to confirm compliance of the monitoring program with requirements of the QAP.
As required in the QAP, data quality assurance includes preparation and analysis of
quality control samples in the field, review of field procedures, an analyte completeness
review, and quality control review of laboratory methods and data. Identification of field
QC samples collected and analyzed is provided in Section 3.1. Discussion of adherence
to Mill sampling Standard Operating Procedures (SOPs) is provided in Section 3.2.
Analytical completeness review results are provided in Section 3.3. The steps and tests
applied to check laboratory data QA/QC are discussed in Sections 3.4.4 through 3.4.9
below.

The analytical laboratory has provided summary reports of the analytical quality QA/QC
measurements necessary to maintain conformance with NELAC certification and
reporting protocol. The Analytical Laboratory QA/QC Summary Reports, including
copies of the Mill’s Chain of Custody and Analytical Request Record forms for each set
of Analytical Results, follow the analytical results under Tab H. Results of review of the
laboratory QA/QC information are provided under Tab I and are discussed in Section 3.4,
below.

3.1 Field QC Samples

The following QC samples were generated by Mill personnel and submitted to the
analytical laboratory in order to assess the quality of data resulting from the field
sampling program.

Field Quality Control samples for the chloroform investigation program consist of one
field duplicate sample for each 20 samples, a trip blank for each shipped cooler, one DI
Field Blank (DIFB) and DI rinsate samples.

During the 1st Quarter of 2010, two duplicate samples were collected as indicated in
Table 1. The duplicates were sent blind to the analytical laboratory and analyzed for the
same parameters as the chloroform wells.

Three trip blanks were provided by Energy Laboratories and returned with the quarterly
monitoring samples.

Rinsates were also collected between well samples where nondedicated sampling
equipment was used. Rinsates were labeled with the name of the subsequently sampled
well with a terminal letter “R” added (e.g. TW4-7R). The results of these analyses are
included with the routine analyses under Tab H.

In addition, one DIFB, while not required by the Chloroform QAP, was collected and
analyzed for the same constituents as the well samples and rinsates.
7
3.2 Adherence to Mill Sampling SOPs

On a review of adherence by Mill personnel to the existing sampling SOPs, the QA
Manager observed that QA/QC requirements established in the QAP and Chloroform
QAP were being adhered to and that the SOP’s were implemented, except as described
below.

3.3 Analyte Completeness Review

All analyses required by the GWDP for chloroform monitoring for the period were
performed.

3.4 Data Validation

The QAP and GWDP identify the data validation steps and data quality control checks
required for the chloroform monitoring program. Consistent with these requirements, the
QA/QC Manager performed the following evaluations: a field data QA/QC evaluation, a
holding time check, a receipt temperature evaluation, an analytical method check, a
reporting limit check, a trip blank check, a QA/QC evaluation of sample duplicates, a
QA/QC evaluation of the DIFB and a rinsate check. Each evaluation is discussed in the
following sections. Data check tables indicating the results of each test are provided
under Tab I.

3.4.1 Field Data QA/QC Evaluation

The QA Manager performs a review of all field recorded parameters to assess their
adherence with QAP requirements. The assessment involved review of two sources of
information: the Field Data Sheets and the Quarterly Depth to Water summary sheet.
Review of the Field Data Sheets addresses well purging volumes and stability of five
parameters: conductance, pH, temperature, redox potential, and turbidity. Review of the
Depth to Water data confirms that all depth measurements used for development of
groundwater contour maps were conducted within a five-day period. The results of this
quarter’s review are provided under Tab I.

Based upon this review, all non-pumping wells conformed to the QAP requirement to
evacuate two well casing volumes before sampling except TW4-2, TW4-3, TW4-10, and
TW4-16. All of the above wells were pumped to dryness before two casing volumes
were evacuated. In each case, representative samples of formation water were collected
after the wells were allowed to recover.

During review of the field data sheets, it was observed that sampling personnel
consistently recorded depth to water to the nearest 0.01 foot.

All field parameters for all wells were within the required RPD (other than the wells that
were pumped to dryness, for which this requirement does not apply), except as follows.

8
Turbidity continues to vary widely based on multiple factors including natural variation,
sampling effects, and well condition. All but three turbidity measurements exceeded the
QAP’s 5 NTU goal. DUSA’s letter to DRC of April 2, 2010 discusses further why US
EPA guidance and source studies do not consider turbidity to be an appropriate parameter
for assessing well stabilization and/assuring collection of representative formation water
and proposes a Plan and Schedule to amend the QAP to address this issue. DUSA’s letter
to DRC proposing changes to the QAP, is in progress.
3.4.2 Holding Time Evaluation

QAP Table 1 identifies the method holding times for each suite of parameters. Sample
holding time checks are provided in Table I-2 under Tab I. All samples were received
and analyzed within the required holding time.

3.4.3 Receipt Temperature Evaluation

Chain of Custody sheets were reviewed to confirm compliance with the QAP requirement
which specifies that samples be received at 6oF or lower. Sample temperatures checks
are provided in Table I-3 under Tab I. All samples were received within the required
temperature limit.
3.4.4 Analytical Method Checklist

All analytical methods reported by the laboratory were checked against the required
methods enumerated in the Chloroform QAP. Analytical method checks are provided in
Table I-4 under Tab I. All methods were consistent with the requirements of the
Chloroform QAP.

3.4.5 Reporting Limit Evaluation

All analytical method reporting limits reported by the laboratory were checked against
the reporting limits enumerated in the Chloroform QAP. Reporting Limit Checks are
provided in table I-5 under Tab I. All analytes were measured and reported to the
required reporting limits.
3.4.6 Trip Blank Evaluation

All trip blank results were reviewed to identify any VOC contamination resulting from
transport of the samples. Trip blank checks are provided in Table I-6 under Tab I. All
trip blank results were less than detection level for all VOC analytes.
3.4.7 QA/QC Evaluation for Sample Duplicates

All analytical results were within the 20% RPD acceptance limits for each of the two
duplicates and its associated well. Results of the RPD test are provided in table I-7 under
Tab I.
9
3.4.8 Rinsate Check

Rinsate checks are provided in Table I-8 under Tab I. A review of the analytical results
reported for rinsate samples indicated that all but two rinsate samples contained some
presence of chloroform. The rinsate chloroform levels ranged from 1.2 to 17 ug/L.
Rinsates following wells with chloroform detections greater than or equal to 1000 ug/L
had rinsate concentrations on the order of magnitude of 10 ug/l. Detections of
chloroform were also reported in rinsates following nine wells that had non-detectable
results for all VOCs analyzed. Rinsates following “clean” wells had chloroform
detections on the order of magnitude of 1 to 3 ug/L.

A comparison of the rinsate concentration levels to the QAP requirements -- that rinsate
concentrations be one order of magnitude lower than that of the actual well -- indicated
that two of the rinsates, TW4-5R and TW4-24R, had concentrations of chloroform above
this conformance level. For TW4-24, the rinsate chloroform concentration was greater
than that of the subsequently sampled well.

TW4-5R also indicated the presence of chloride. The level of chloride was within the
conformance requirement of one order of magnitude or less.

Additionally, a review of the results for the DI blank indicated the presence of
chloroform in DI water at approximately the same order of magnitude concentration as
identified in the rinsate samples from uncontaminated wells (1 to 3 ug/L).

The above findings indicate that chloroform contamination present in the rinsate samples
is originating, at least in part, from the DI rinsate process, the hydrochloric acid sample
preservation process or both. There may also be some cross-contamination of sampling
equipment from field samples.

However, based on the above findings, for this current quarter’s data, the presence of
chloroform in the rinsate samples does not effect the validity or utility of the groundwater
data for the following reasons:

• For the two wells in which the preceding rinsate levels exceeded the conformance
criterion, the chloroform concentrations in both of the wells and both rinsates
were significantly lower than the GWDP GWCL of 70 ug/L for chloroform.

• The wells with non-detectable levels of chloroform were apparently unaffected by
the presence of chloroform in the preceding rinsates, regardless of the source.

Based on the QA Manager’s review of DI preparation, transport and use procedures, and
sample preservation requirements, chloroform may have entered the sampling process
through any of the following routes, a combination of these routes, or other pathways:

1. The DI filter system may be underperforming or performing inconsistently.
10
2. DI, which is both a corrosive agent to natural materials and an aggressive leaching
solvent to some synthetic materials, may have attacked the synthetic containers
used to carry it to the field and introduced VOCs from polymer degradation
products.
3. The preservative, hydrochloric acid, may itself be contaminated with VOCs.
4. Cross-contamination of sampling equipment from field samples may be
occurring, given that the rinsate samples that follow the higher concentration
monitoring wells tend to have higher concentrations of chloroform. The current
program of sampling from the least to the most contaminated wells was designed
to minimize the likelihood of this pathway. In addition, review of the rinsate data
shows that rinsate samples have detections of chloroform when their associated
samples do not. This indicates that if chloroform contamination is originating
from cross-contamination from the sampling equipment, this is not the only
source of contamination.

The QA Manager plans to implement a testing program to attempt to isolate the source(s)
which are introducing chloroform into the sampling and/or rinsate process. The planned
approach is discussed further in Section 6, below. Specific steps of the isolation program
are already underway as discussed in Section 6.
3.4.9 Other Laboratory QA/QC

Section 9.2 of the QAP requires that the laboratory’s QA/QC Manager check the
following items in developing data reports: (1) sample preparation information is correct
and complete, (2) analysis information is correct and complete, (3) appropriate analytical
laboratory procedures are followed, (4) analytical results are correct and complete, (5)
QC samples are within established control limits, (6) blanks are within QC limits, (7)
special sample preparation and analytical requirements have been met, and (8)
documentation is complete. In addition to other laboratory checks described above,
DUSA’s QA/QC manager rechecks QC samples and blanks (items (5) and (6) to confirm
that the percent recovery for spikes and the relative percent difference for spike
duplicates are within the method-specified acceptance limits, or that the case narrative
sufficiently explains any deviation from these limits. Results of this quantitative check
are provided in Table I-7 under Tab I. All lab QA/QC results met these specified
acceptance limits.
4.0 INTERPRETATION OF DATA
4.1 Interpretation of Groundwater Levels, Gradients and Flow Directions.
4.1.1 Current Site Groundwater Contour Map

As stated above, a listing of groundwater level readings for the current quarter (shown as
depth to groundwater in feet) is included under Tab D. The data from this tab has been
interpreted (kriged) and plotted in a water table contour map, provided under the same
tab.

11
Also included under Tab D is a groundwater contour map of the Mill site and a more
detailed map of a portion of the Mill site where the four chloroform pumping wells are
located, in each case with hand-drawn stream tubes, depicting hydraulic capture from the
pumping

The contour maps are based on the March 11, 2010 data for all wells.
4.1.2 Comparison of Current Groundwater Contour Maps to Groundwater
Contour Maps for Previous Quarter

The groundwater contour maps for the Mill site for the fourth quarter of 2009, as
submitted with the Chloroform Monitoring Report for the fourth quarter of 2009, are
attached under Tab E.

A comparison of the water table contour maps for the first quarter of 2010 to the water
table contour maps for the previous quarter indicates similar patterns of drawdown
related to pumping of MW-4, MW-26 (TW4-15), TW4-19 and TW4-20 (pumping in
TW4-4 had not progressed enough to have impacted the progress of drawdown). Water
levels and water level contours for the site have not changed significantly since the last
quarter, except for a few locations. Differences in water level contours south of MW-4
are partly due to the start-up of pumping at TW4-4.

A reported increase in water level of approximately 6 feet in well TWN-2 occurred, and
reported decreases of approximately 14 feet in well TWN-8, and 13 feet in well TWN-18
occurred. A reported decrease in water level of approximately 6 feet occurred in pumping
well MW-26 (TW4-15), and a reported increase in water level of approximately 22 feet
occurred in pumping well TW4-19. Water level changes at other pumping wells were less
than 5 feet.

Water level fluctuations at pumping wells MW-4, MW-26 (TW4-15), TW4-4, TW4-19,
and TW4-20 are due in part to fluctuations in pumping conditions just prior to and at the
time the measurements are taken. The largest decrease (increase in drawdown) of
approximately 6 feet occurred in well MW-26 (TW4-15) and the largest increase
(decrease in drawdown), of approximately 22 feet, occurred at TW4-19.
4.1.3 Hydrographs

Attached under Tab F are hydrographs showing groundwater elevation in each
chloroform contaminant investigation monitor well over time.
4.1.4 Depth to Groundwater Measured and Groundwater Elevation

Attached under Tab G are tables showing depth to groundwater measured and
groundwater elevation over time for each of the wells listed in Section 2.1.1 above.
12
4.1.5 Evaluation of the Effectiveness of Hydraulic Capture

Perched water containing chloroform has been removed from the subsurface by pumping
MW-4, MW-26 (TW4-15), TW4-19, TW4-20, and since January 31, 2010, TW4-4. The
purpose of the pumping is to reduce total chloroform mass in the perched zone as rapidly
as is practical. These wells were chosen for pumping because 1) they are located in areas
of the perched zone having relatively high permeability and saturated thickness, and 2)
high concentrations of chloroform were detected at these locations. TW4-4 was chosen n
order to attempt to contain the downgradient movement of the plume past TW4-6. The
relatively high transmissivity of the perched zone in the vicinity of pumping wells MW-4,
MW-26, TW4-19 and TW4-20 results in the wells having a relatively high productivity.
The combination of relatively high productivity and high chloroform concentrations
allows a high rate of chloroform mass removal from those wells.

The impact of pumping these wells is indicated by the water level contour maps attached
under Tabs D and E. Cones of depression have developed in the vicinity of pumping
wells MW-4, MW-26, TW4-19 and TW4-20, which continue to remove significant
quantities of chloroform from the perched zone. The water level contour maps indicate
that effective capture of water containing high chloroform concentrations in the vicinity
of these pumping wells is occurring. Since the last quarter, as noted in Section 4.1.2, a
decrease in water level (increase in drawdown) of more than 5 feet occurred at MW-26
(TW4-15), and an increase in water level (decrease in drawdown) of more than 5 feet
occurred at TW4-19. Overall, the combined capture of MW-4, MW-26 (TW4-15), TW4-
19, and TW4-20 has not changed significantly since the last quarter. The increase in
drawdown at MW-26 (TW4-15) and the decrease in drawdown at TW4-19 have
increased, and decreased, respectively, the apparent capture zones of these wells relative
to other nearby pumping wells.

High chloroform concentrations exist at some locations downgradient of pumping wells
MW-4, MW-26 (TW4-15), TW4-19, and TW4-20 (for example, near TW4-4), where the
low permeability of the perched zone significantly limits the rate at which chloroform
mass can be removed by pumping. By removing mass and reducing hydraulic gradients,
thereby reducing the rate of downgradient chloroform migration, and allowing natural
attenuation to be more effective, pumping at the productive, upgradient locations has a
beneficial effect on this downgradient chloroform. Pumping at TW4-4 was implemented
during the first quarter of 2010 to improve capture in this downgradient area to the extent
allowable by the low permeability conditions.

4.2 Review of Analytical Results
4.2.1 Current Chloroform Isoconcentration Map

Included under Tab J of this Report is a current chloroform iso-concentration map for the
Mill site.
13
4.2.2 Chloroform Concentration Trend Data and Graphs

Attached under Tab K is a table summarizing values for all required parameters, chloride,
nitrate/nitrite, carbon tetrachloride, chloroform, chloromethane, and methylene chloride,
for each well over time.

Attached under Tab L are graphs showing chloroform concentration trends in each
monitor well over time.
4.2.3 Interpretation of Analytical Data

Comparing the analytical results to those of the previous quarter, as summarized in the
table included under Tab K, the following observations can be made:

a) Chloroform concentrations have increased by more than 20% in the following
wells compared to last quarter: TW4-2, TW4-4, TW4-5, TW4-6, TW4-10, TW4-
18, and TW4-22;

b) Chloroform concentrations have decreased by more than 20% in the following
wells compared to last quarter: TW4-15, TW4-19, and TW4-20;

c) Chloroform concentrations have remained within 20% in the following wells
compared to last quarter: MW-4, TW4-1, TW4-7, TW4-11, TW4-21, and TW4-
24;

d) TW4-3, TW4-8, TW4-9, TW4-12, TW4-13, TW4-14, TW4-16, MW-32 (TW4-
17), TW4-23, and TW4-25 remained non-detect.

In addition, since the last quarter, the chloroform concentration in pumping well TW4-20
decreased from 15,000 µg/L to 3,500 µg/L, the concentration in pumping well TW4-19
decreased from 4,700 µg/L to 940 µg/L, the concentration in well TW4-21 increased
slightly from 160 to 170 µg/L, and the concentration in well TW4-22 increased from 380
µg/L to 2,200 µg/L. Wells TW4-23 and TW4-25 remained non-detect for chloroform,
and the concentration in well TW4-24 increased slightly from 1.2 µg/L to 1.3 µg/L.
TW4-24, located west of TW4-22, and TW4-25, located north of TW4-21, bound the
chloroform plume to the west and north.

The chloroform concentration in TW4-6, which was the most downgradient temporary
perched well prior to installation of temporary well TW4-23, and which remained outside
the chloroform plume until the first quarter of 2009, increased from 250 µg/L to 1,000
µg/L. This well likely remained outside the chloroform plume between installation in the
second quarter of 2000 and the fourth quarter of 2008 due to a combination of 1) slow
rates of downgradient chloroform migration in this area due to low permeability
conditions and the effects of upgradient chloroform removal by pumping, and 2) natural
attenuation. TW4-23 continues to bound the chloroform plume to the south.

14
The slow rate of chloroform migration in the vicinity of TW4-6 is demonstrated by
comparing the rate of increase in chloroform at this well to the rate of increase in the
nearest upgradient well TW4-4. Concentrations at TW4-4 increased from non-detect to
more than 2,200 µg/L within only 2 quarters whereas 16 quarters were required for
concentrations in TW4-6 to increase from non-detect to only 81 µg/L.

5.0 LONG TERM PUMP TEST AT MW-4, TW4-15 (MW-26), TW4-19, TW4-
20, AND TW4-4 OPERATIONS REPORT

5.1 Introduction

As a part of the investigation of chloroform contamination at the Mill site, DUSA has
been conducting a Long Term Pump Test on MW-4, TW4-19, TW4-15 (MW-26) and
TW4-20, and, since January 31, 2010, TW4-4. The purpose of the test is to serve as an
interim action that will remove a significant amount of chloroform-contaminated water
while gathering additional data on hydraulic properties in the area of investigation. The
following information documents the operational activities during the Quarter.

5.2 Pump Test Data Collection

The long term pump test for MW-4 was started on April 14, 2003, followed by the start
of pumping from TW4-19 on April 30, 2003, from TW4-15 (MW-26) on August 8, 2003,
from TW4-20 on August 4, 2005, and from TW4-4 on January 31, 2010. Personnel from
Hydro Geo Chem, Inc. were on site to conduct the first phase of the pump test and collect
the initial two days of monitoring data for MW-4. DUSA personnel have gathered
subsequent water level and pumping data.

Analyses of hydraulic parameters and discussions of perched zone hydrogeology near
MW-4 has been provided by Hydro Geo Chem in a separate report, dated November 12,
2001, and in the May 26, 2004 Final Report on the Long Term Pumping Test.

Data collected during the Quarter included the following:

• Measurement of water levels at MW-4, TW4-19, TW4-15 (MW-26), and
TW4-20 and, commencing regularly on March 1, 2020, TW4-4, on a
weekly basis, and at selected temporary wells and permanent monitoring
wells on a monthly basis.

• Measurement of pumping history, including:
- pumping rates
- total pumped volume
- operational and non-operational periods.

• Periodic sampling of pumped water for chloroform and nitrate/nitrite
analysis and other constituents.
15
5.3 Water Level Measurements

Beginning August 16, 2003, the frequency of water level measurements from MW-4,
TW4-15 (MW-26), and TW4-19 was reduced to weekly. From commencement of
pumping TW4-20, and regularly after March 1, 2010 for TW4-4, water levels in these
wells have been measured weekly. Depth to groundwater in all other chloroform
contaminant investigation wells is monitored monthly. Copies of the weekly Depth to
Water monitoring sheets for MW-4, TW4-15 (MW-26), TW4-19, TW4-20 and TW4-4
and the January and February monthly Depth to Water monitoring sheets for all of the
chloroform contaminant investigation wells are included under Tab C. Monthly depth to
water measurements for February are recorded in the Field Data Worksheets included
under Tab B.

5.4 Pumping Rates and Volumes

Table 2 summarizes the pumped volumes and recovered mass of chloroform by well per
quarter and historically since the inception of the chloroform recovery program for the
five currently-active pumping wells.
5.4.1 MW-4
Approximately 68,125 gallons of water were pumped from MW-4 during the Quarter.
The average pumping rate from MW-4, when the pump was pumping, was approximately
4.0 gpm throughout the Quarter. The well is not pumping continuously, but is on a delay
device. The well purges for a set amount of time and then shuts off to allow the well to
recharge. Water from MW-4 was transferred to the Cell 1 evaporation pond through a
pipeline installed specifically for that purpose.

5.4.2 TW4-19

Approximately 348,550 gallons of water were pumped from TW4-19 during the Quarter.
The average pumping rate from TW4-19, when the pump was pumping, was
approximately 6.0 gpm throughout the Quarter. The pump in this well is operating on a
delay. It pumps for approximately one and a half minutes and then is off for two to three
minutes. Water from TW4-19 was directly transferred to the Cell 1 evaporation pond
through a pipeline installed specifically for that purpose.
5.4.3 TW4-15 (MW-26)

Approximately 61,320 gallons of water were pumped from TW4-15 (MW-26) during the
Quarter. The average flow rate from TW4-15, when the pump was pumping, was
approximately 1.5 gpm throughout the Quarter. The well is not pumping continuously,
but is on a delay device. The well now purges for a set amount of time and then shuts off
to allow the well to recharge. The water is directly transferred to the Cell 1 evaporation
pond through a pipeline installed specifically for that purpose.
16
5.4.4 TW4-20

Approximately 14,490 gallons of water were pumped from TW4-20 during the Quarter.
The average flow rate from TW4-20, when the pump was pumping, was approximately
6.0 gpm throughout the Quarter. The well is not purging continuously but is on a delay
device. The well pump is set on a water elevation device. When the water reaches a set
point, the pump turns on until the water level drops to another set point. The water is
directly transferred to the Cell 1 evaporation pond through a pipeline installed
specifically for that purpose.
5.4.5 TW4-4

Consistent with the Revised Plan of Action and Work Schedule for Chloroform
Concentrations Exceeding Groundwater Quality Standard in Monitor Well TW4-6 and
related discussions with DRC staff, TW4-4 commenced pumping on January 31, 2010.
However, the flowmeter/totalizer was not fully operational until several days before
March 1, 2010. While the recovery well was pumping during the entire period since
January 31, 2010, the flow meter/totalizer only recorded approximately the gallons
pumped during the last month of the quarter. As a result, Table 2 under-represents the
amount of chloroform capture accomplished in the first quarter of 2010.

Based on the limited measurement period recorded on the meter, approximately 30,168
gallons were pumped from TW4-4 during the period from March 1 to March 31. The
average flow rate, when the pump was pumping, was 8.6 gpm. The well is not pumping
continuously, but is set on a water elevation device. When the water reaches a set point,
the pump turns on until the water level drops to another set point. The water is directly
transferred to the Cell 1 evaporation pond through a pipeline installed specifically for that
purpose.

5.4.6 TW4-18

TW4-18 was equipped with a pump and flowmeter in preparation for using water from
this well to supply the New Decontamination Pad at the Mill. Pumping commenced
sporadically on March 22 and ended on May 4, 2010. The amount of water pumped
during the nine-day period in the first quarter was negligible and, given the low
concentrations of chloroform in TW4-18, the recovered mass of chloroform would be
insignificant, and has not been included in the calculation of chloroform recovered. It
will be included in the calculation of mass removed in the second quarter of 2010. The
initial supply of water for the New Decontamination Pad was provided from Recapture
Reservoir via water truck and not from TW4-18.

17
5.5 Mass Removed

Chloroform removal was estimated as of the 1st Quarter 2007. Since that estimation the
mass removed by well for each quarter has been compiled in Table 2 below, indicating
that a total of 484.8 pounds of chloroform have been removed.

5.6 Daily Inspections

Denison has submitted an Operations and Maintenance Plan, Chloroform Pumping
System, White Mesa Mill, Blanding, Utah, Revision 1.0 to UDEQ for approval. Upon
approval of that plan, the Mill will commence documenting its daily inspections of the
operational status of the chloroform pumping wells on the daily inspection form, an
example of the form of which is attached as Tab M, Chloroform Well Daily Inspection
Form.

No operational problems in the pumping wells were reported during the 1st Quarter, 2010
period.

5.7 Conditions That May Affect Water Levels in Piezometers

No significant amount of water was added to any of the three wildlife diversion ponds
during the Quarter.

6.0 CORRECTIVE ACTION REPORT
Necessary corrective actions identified during the current monitoring period are described
below.

6.1 Identification and Definition of the Problem

Stabilization of Parameters
Conductivity results for one well marginally exceeded the 10% RPD. However, that well
was pumped to dryness and a representative sample of formation water was collected
after it was allowed to recover. Turbidity continues to vary widely based on multiple
factors including natural variation, sampling effects, and well condition. All but three
turbidity measurements exceeded the QAP’s 5 NTU goal.

Rinsate Chloroform Levels
DI water used for decontamination continues to indicate presence of chloroform. Rinsate
samples generated from use of the DI for decontamination have chloroform levels and
level trends that appear to be possibly related, in part, to the chloroform presence in the
preceding well samples, and in part to other factors. Although rinsates following high
concentration wells appear to be somewhat higher than rinsates following low
concentration wells, rinsates following sampling of uncontaminated wells, appear to also
be contaminated with chloroform. Presence of chloroform in DI and rinsates is not
consistent from one sampling event to the next.
18

In addition, data available at present are not sufficient to isolate the source of the
chloroform being reported in the rinsate samples. Additional studies are necessary to
isolate the source of reported chloroform to either:
1. the laboratory preservative in the analyzed rinsate samples,
2. the field water sources and transport mechanisms and procedures that generated
the rinsate sources, or
3. The effectiveness of decontamination procedures.

6.2 Assignment of Responsibility for Investigation of the Problem

The problems are already under investigation by the QA Manager.

6.3 Investigation and Determination of Cause of the Problem

Stabilization of Parameters
Data continue to indicate that it may not be feasible to achieve both a turbidity level of
less than 5 NTU and a stabilized turbidity between any two measurements within 10%
RPD in every well. Discussions are underway with DRC to address the fact that it may
not be appropriate or feasible to achieve consistent turbidity levels of 5 NTU in the Mill’s
groundwater program wells under the current evacuation scheme, and that other well
purging approaches, such as micro-purging, may be more appropriate. A letter report
addressing modification of monitoring methods relative to turbidity issues, submitted by
DUSA to DRC on April 2, 2010, is currently under review by DRC.

DUSA’s letter to DRC, in progress, proposing changes to the QAP, addresses the
stabilization of conductivity and other field parameters, and explains why EPA guidance
and source studies consider parameter measurement as only one of several methods to
assure collection of representative formation water.

Rinsate Chloroform Levels
The QA Manager plans to implement a testing program to attempt to isolate the source(s)
which are introducing chloroform into the sampling and/or rinsate process. As discussed
above, and based on evaluations to date, chloroform may have entered the samples from
any number of sources. The QA Manager plans an initial investigation focused on
confirming or eliminating the following sources:

1. The DI filter system may be underperforming or performing inconsistently.
2. DI, which is both a corrosive agent to natural materials and an aggressive leaching
solvent to some synthetic materials, may have attacked the synthetic containers
used to carry it to the field and introduced VOCs from polymer degradation
products.
3. The preservative, hydrochloric acid, may itself be contaminated with VOCs.
4. Cross-contamination of sampling equipment from field samples may be
occurring, given that the rinsate samples that follow the higher concentration
monitoring wells tend to have higher concentrations of chloroform. The current
19
program of sampling from the least to the most contaminated wells was designed
to minimize the likelihood of this pathway. In addition, review of the rinsate data
shows that rinsate samples have detections of chloroform when their associated
samples do not. This indicates that if chloroform contamination is originating
from cross-contamination from the sampling equipment, this is not the only
source of contamination.

Sampling and analysis to resolve issues related to Items 1 and 2 will be conducted during
the upcoming monitoring period. The QA Manager has already required the analytical
laboratory to analyze and confirm the quality of the hydrochloric acid in preserved bottles
(Item 3). Data evaluation, which will occur after the results of analyses in the next
quarter are received, will be used to isolate and eliminate or confirm each of these three
sources.

6.4 Determination of a Corrective Action to Eliminate the Problem

Turbidity
A letter report addressing modification of monitoring methods relative to turbidity issues,
submitted by DUSA to DRC on April 2, 2010, is currently under review by DRC. DUSA
is currently evaluating the suitability of turbidity, as well as other parameters, in
determining stabilization of monitoring wells, and is preparing proposed changes to the
QAP to address these issues.

Rinsate Chloroform Levels
A corrective action will be determined following completion of the analytical test results
and data review outlined above.

6.5 Assigning and Accepting Responsibility for Implementing the Corrective
Action

Turbidity
It will be the responsibility of the Director, Compliance and Permitting to implement both
corrective actions. Development of recommendations and QAP changes to address
turbidity are already underway.

Rinsate Chloroform Levels
It will be the joint responsibility of the Director, Compliance and Permitting, and the
Mill’s sampling staff to implement the isolation testing and whichever actions result from
its findings.

6.6 Implementing the Corrective Action and Evaluating Effectiveness

Turbidity
Implementation of the corrective action for turbidity will follow development and DRC
approval of an action plan for well purging, as discussed in Section 4.3.

20
Rinsate Chloroform Levels
Implementation to remove the chloroform source(s) will occur after isolation testing
identifies the source(s).

6.7 Verifying That the Corrective Action Has Eliminated the Problem

Turbidity
Verification will occur following DRC review and approval of the proposed revisions to
the QAP and proposal for field testing of approaches to collect representative formation
water.

Rinsate Chloroform Levels
Verification will occur after field changes are implemented to remove the chloroform
source(s) identified in the isolation testing study.
7.0 CONCLUSIONS AND RECOMMENDATIONS
The water level contour map for the first quarter, 2010 indicates that effective capture of
water containing high chloroform concentrations in the vicinity of the pumping wells is
occurring.

Between the fourth quarter of 2009 and the first quarter of 2010, the chloroform
concentration in pumping well TW4-20 decreased from 15,000 µg/L to 3,500 µg/L, the
concentration in pumping well TW4-19 decreased from 4,700 µg/L to 940 µg/L, the
concentration in well TW4-21 increased slightly from 160 to 170 µg/L, and the
concentration in well TW4-22 increased from 380 µg/L to 2,200 µg/L. Fluctuations in
concentrations in these wells are likely related to variations in pumping in TW4-20 and
nearby wells, and their location near the suspected former office leach field source area.
Regardless of these measured fluctuations in chloroform concentrations, sampling of
temporary wells TW4-24 (located west of TW4-22) and TW4-25 (located north of TW4-
21), indicates these wells remain outside the chloroform plume and thus bound the plume
to the west and north. Chloroform was not detected at TW4-25, and was detected at a
concentration of 1.3 µg/L at TW4-24.

The chloroform concentration at downgradient well TW4-6, which remained outside the
plume until the first quarter of 2009, increased from 250 to 1,000 µg/L. Although
fluctuations in concentrations have occurred, this well likely remained outside the
chloroform plume between installation in the second quarter of 2000 and the fourth
quarter of 2008 due to a combination of 1) slow rates of downgradient chloroform
migration in this area due to low permeability conditions and the effects of upgradient
chloroform removal by pumping, and 2) natural attenuation. Chloroform remained non-
detect at downgradient temporary well TW4-23, which continues to bound the
chloroform plume to the south.

Continued pumping of MW-4, MW-26 (TW4-15), TW4-19, and TW4-20 is
recommended. Pumping these wells, regardless of any short term fluctuations in
concentrations detected at the wells (such as at TW4-20), helps to reduce downgradient
21
chloroform migration by removing chloroform mass and reducing average hydraulic
gradients, thereby allowing natural attenuation to be more effective. Continued pumping
at TW4-4 is also recommended to improve capture of chloroform to the extent practical
in the southern portion of the plume where low permeability conditions exist, and to help
mitigate the increase in concentration at downgradient well TW4-6.

8.0 ELECTRONIC DATA FILES AND FORMAT
DUSA has provided to the Executive Secretary an electronic copy of all laboratory
results for groundwater quality monitoring conducted under the chloroform contaminant
investigation during the first quarter, in Comma Separated Values (CSV) format. A copy
of the transmittal e-mail is included under Tab N.
9.0 SIGNATURE AND CERTIFICATION
This document was prepared by Denison Mines (USA)Corp.on May 28,2010.
DENISON MINES (USA)CORP.
By:
David C.Frydenlund
Vice President,Regulatory Affairs and Counsel
22
Certification:
I certify,under penalty of law,that this document and all attachments were
prepared under my direction or supervision in accordance with a system designed to
assure that qualified personnel properly gather and evaluate the information submitted.
Based on my inquiry of the person or persons who manage the system,or those persons
directly responsible for gathering the information,the information submitted is,to the
best ofmy knowledge and belief,true,accurate,and complete.I am aware that there are
significant pe alties or submitting false information,including the possibility of fine and
imprisonm for owing violations.
David .yden und
Vice President,egulatory Affairs and Counsel
Denison Mines (USA)Corp.
23
Table 1: Summary of Well Sampling and Constituents for the Period
Well Date of Field Data Date of Lab Report
MW-4 2/17/10 15:03 3/2/2010
TW4-1 3/3/10 10:17 3/15/2010
TW4-1R 3/2/10 13:28 3/15/2010
TW4-2 3/3/10 9:58 3/15/2010
TW4-2R 3/2/10 14:15 3/15/2010
TW4-3 2/23/10 8:52 3/5/2010
TW4-3R 2/22/10 9:45 3/5/2010
TW4-4 2/17/10 15:10 3/2/2010
TW4-5 2/25/10 8:22 3/5/2010
TW4-5R 2/24/10 12:30 3/5/2010
TW4-6 2/25/10 8:33 3/5/2010
TW4-6R 2/24/10 15:00 3/5/2010
TW4-7 3/3/10 10:06 3/15/2010
TW4-7R 3/2/10 11:17 3/15/2010
TW4-8 2/24/10 8:35 3/5/2010
TW4-8R 2/23/10 9:40 3/5/2010
TW4-9 2/23/10 9:05 3/5/2010
TW4-9R 2/22/10 12:25 3/5/2010
TW4-10 3/3/10 9:37 3/15/2010
TW4-10R 3/2/10 8:20 3/15/2010
TW4-11 3/3/10 9:49 3/15/2010
TW4-11R 3/2/10 10:35 3/15/2010
TW4-12 2/23/10 8:20 3/5/2010
TW4-12R 2/22/10 14:27 3/5/2010
TW4-13 2/24/10 7:45 3/5/2010
TW4-13R 2/23/10 13:02 3/5/2010
TW4-14 3/3/10 10:42 3/15/2010
TW4-14R 2/23/10 14:08 3/5/2010
TW4-15 2/17/10 14:52 3/2/2010
TW4-16 2/24/10 8:15 3/5/2010
TW4-16R 2/23/10 10:35 3/5/2010
TW4-17 2/17/10 13:34 3/2/2010
TW4-18 2/24/10 10:50 3/5/2010
TW4-19 2/17/10 14:30 3/2/2010
TW4-20 2/17/10 14:42 3/2/2010
TW4-21 2/25/10 8:05 3/5/2010
TW4-21R 2/24/10 13:25 3/5/2010
TW4-22 3/3/10 9:24 3/15/2010
TW4-22R 3/2/10 9:32 3/15/2010
TW4-23 2/24/10 8:05 3/5/2010
TW4-23R 2/23/10 11:21 3/5/2010
TW4-24 2/25/10 8:11 3/5/2010
TW4-24R 2/24/10 9:35 3/5/2010
TW4-25 2/23/10 7:35 3/5/2010
TW4-25R 2/22/10 11:20 3/5/2010
TW4-60 (DI Blank) 3/2/10 8:25 3/15/2010
TW4-65 (Duplicate of TW4-17) 2/17/10 13:34 3/2/2010
TW4-70 (Duplicate of TW4-10) 3/3/10 9:37 3/15/2010
All sample locations were sampled for:
Carbon Tetrachloride, Chloride, Chloroform, Chloromethane, Methylene Chloride, and Nitrate and Nitrates as Nitrogen
"R" following a well number designates an equipment rinsate sample collected prior to sampling of the well of that number.
Table 2: Chloroform Mass Removal Per Well Per Quarter
Quarter
MW-4
(lbs)
TW4-4
(lbs)
MW4-15
(lbs)
MW4-19
(lbs)
MW4-20
(lbs)
Quarter Totals
(lbs)
Q1 2007* 36.8 12.9 150.2 87.0 286.9
Q2 2007 1.4 0.1 0.0 2.5 4.0
Q3 2007 2.2 0.8 2.9 3.1 9.0
Q4 2007 1.7 1.0 3.1 4.8 10.6
Q1 2008 1.7 0.4 4.6 7.2 13.8
Q2 2008 1.3 0.5 3.2 9.9 14.8
Q3 2008 1.2 0.3 15.9 9.3 26.8
Q4 2008 1.3 0.3 20.7 0.4 22.7
Q1 2009 1.7 0.4 4.3 3.6 10.0
Q2 2009 6.8 0.2 3.7 2.8 13.5
Q3 2009 1.5 0.4 11.1 5.5 18.5
Q4 2009 4.8 0.6 17.8 26.1 49.4
Q1 2010 0.9 0.4 0.4 2.7 0.4 4.9
Well Totals 63.2 0.4 18.4 240.2 162.6 484.8
* Sums recovered in each well, and total, from inception through Q1 2007.
#N/A
INDEX OF TABS

Tab A Site Plan and Perched Well Locations White Mesa Site
Tab B Order of Sampling and Field Data Worksheets
Tab C Weekly and Monthly Depth to Water Data
Tab D Kriged Current Quarter Groundwater Contour Map, Capture Zone Map, Capture Zone Details
Map, and Depth to Water Data
Tab E Kriged Previous Quarter Groundwater Contour Map
Tab F Hydrographs of Groundwater Elevations Over Time for Chloroform Monitoring Wells
Tab G Depths to Groundwater and Elevations Over Time for Groundwater Monitoring Wells
Tab H Laboratory Analytical Reports
Tab I Quality Assurance and Data Validation Tables
I-1 Field Data QA/QC Evaluation
I-2 Holding Time Evaluation
I-3 Receipt Temperature Check
I-4 Analytical Method Check
I-5 Reporting Limit Evaluation
I-6 Trip Blank Evaluation
I-7 QA/QC Evaluation for Sample Duplicates
I-8 QC Control Limits for Analyses and Blanks
I-9 Rinsate Check
Tab J Kriged Current Quarter Chloroform Isoconcentration Map
Tab K Analyte Concentration Data Over Time
Tab L Chloroform Concentration Trend Graphs
Tab M Chloroform Well Daily Inspection Form
Tab N CSV Transmittal Letter

Tab A
Site Plan and Perched Well Locations White Mesa Site

HYDRO
GEO
CHEM, INC.APPROVED DATE REFERENCE FIGURE
CELL NO. 2
CELL NO. 4A
3332
MW-21

3000
BOUNDARY
PROPERTY
SCALE IN FEET
0
CELL NO. 1
MILL SITE
MW-01
MW-02
MW-03
MW-05
MW-11
MW-12
MW-14
MW-15
MW-16
MW-17
MW-18
MW-19
MW-20
MW-22
MW-23
MW-24
MW-25
MW-27
MW-28
MW-29
MW-30
MW-31
MW-32
PIEZ-1
PIEZ-2
PIEZ-3
PIEZ-4
PIEZ-5
MW-26
TW4-1
TW4-2
TW4-3
TW4-4
TW4-5
TW4-6
TW4-9
TW4-11
TW4-12
TW4-13
TW4-14
TW4-16
TW4-18
TW4-20
TW4-21
MW-04TW4-7 TW4-8
TW4-10
TW4-22
TW4-19
TW4-23
TW4-24
TW4-25
TWN-1
TWN-2
TWN-3
TWN-4
TWN-5
TWN-6
TWN-7
TWN-8
TWN-9
TWN-10
TWN-11 TWN-12
TWN-13
TWN-14
TWN-15
TWN-16
TWN-17
TWN-18
TWN-19
MW-20
PIEZ-1
perched monitoring well
temporary perched monitoring
well installed April, 2005
perched piezometer
MW-31
temporary perched monitoring well
perched monitoring well
installed April, 2005
SITE PLAN
AND PERCHED WELL LOCATIONS
WHITE MESA SITE
H:/718000/may10/welloc.srf
TW4-19
TW4-20
EXPLANATION
temporary perched monitoring well
installed May, 2007
TW4-23
wildlife pond
SJS
temporary perched nitrate
monitoring well
TWN-1

Tab B
Order of Sampling and Field Data Worksheets

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,
----= .'
fMfU!Ill -([][(u:tJillfIT<11W~lte.r lDij[J[:hRfJ(ge1i?e:mru[
(i]Ji1frU~ftWvfB0Bl' M@lurOO1"llEg
Jfllliliw be {Q), iii g.ftlill!il.
S/iliiJI= =.:::l q
','0.
NiIlDlllllOOir ®1f c@ililng 'II®IUi~e~-~lM-ttl.·~ftir~@).",;"'"",,-,-,,,-,,"---"-c':""':'-'-_"---''-'-_
l!f well e'll.!lCll!l!t~ lID IIirryJlleDB, lIlilDllllOO[ li1fg~~~~-e~~~~~:"i:,;''-'" "'-' ~ __ -"'-__ :"':"' __ _
Nm_ IIH!erliifie!ll Amlnlyl~clllll!.JilbIlJ(!!~~Vn;,~'~i~lllijji
,H'
OJ ( ""-..
'" . ~; '. , ,?~
\ \ .,:...-" \ ,......,.
I .. ,~ , i' 1"."., j3' , "F". Iv '-: .'-'I
-~/ \..). J I I...../L/'-'I..:, -CA"J I V' I I
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: I,'
I'v'JWlln -€Jm-:tE!lR{(!VJZl1i:@A' lilJiisc;hEmE}3 JP'eiEiillnt
t11ElIf20WjJ\!J203lf Th£:[nUR0[}j~Elg
Q@&iffi~y ffi}lZtETBlITiGB JflkJfiR (<<J1&IP)
IDeEe ~~p,!il 'J['n_ fur ~gimJg_L:-~"':"'=_._lli'
t' __ • __ -_ ,,:v:_:' :-,_ -::_ _ _ -
]VetH lP~Dg l!lIninjb'f&~:'~t~ ~ri_. J"~'o/ •
.s~)lii'illn1gJE!lfeli1l~ (M'AC\"'~ c"b IQ~c,foC',V) . .. ... ' . r ........ ''' ..
J!llHi lB!Mffer 1.1fi,-:-= .. , .. c:c-.. ~7,-,-. ",0,---:-,,,,,,.,,,,, .. ,-,,, , . .-::. ,.".;
""',"; n" 'bidi,' ."'. '."" ?:"",. ~,,~. .,.. .. ,..--"--------
r' -.
IiiM©lt il'l!l"dJifi]iliilllil ((1ll1ll~~_' __ ~~
v·,l)
. .
t" :; ','
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"
.'
·BAliiHll-«lrt!}~mrl!.WJlil£f·r IDtisr:NEOJrga lPilirfiJ[ij~
I[lK@~iit1lIWl~ Il!1wJllii!IT!mg
QilllElliity _~ruilui>Ji'i~~ (QAJP:)
']!'qqfuJid!ii.j(~=====-":· __
. /; ;r ;'!~1, ~"t(\?~
••.• e~b1;~ ~W@ @!ilEfujJgiri)j!!ID!!J.!lB (2V)1
:.}J!,;X~;'iF}"'I::' ~';'.:~.~.;o.: .. ::,.,.' -,:;',
., ' . . ,,"
:3:r"f-LJJ,;;,;t; a-I {L~,_3~;rt.¥X@2:· t1:f3.if~· ~~~~
0C1{)1:',~!t .;( Twl./-/d ~1')1I-~1 Sc:~~fL. 5~.21"~

Tab C
Weekly and Monthly Depth to Water Data

Depth to Water
Date \ -y ~ ;;;2.0 10 mmHg bd.-(,.3("L\
Time Well Depth Comments
~\.3
14SD MW-4 7&'.71 Flow 4.3 G-PjV\
Meter
it.\'i~ TW4-15 <;<3. bl Flow 5.1 (,. PfJ\
,:>,\£..o\C\..::4. Meter Ot?:.? "\30
Iq'l~ TW4-19 bS.Sb Flow b G-P/i\
Meter ceo'\ 7C
l'i3S TW4-20 7S 51 Flow :;!.. ~ 6· P l'1
Meter !Z?i17:';,O
Water: :'i).{,;lOO
Depth to Water
Date 1-/1-.::toro mmHg b~ 7. ~g8
Time Well Depth Comments
'i7A
1'1";'1" MW-4 -m .4 i Flow p.,,:,,,. .. ''''''M.\ ... \"f ~c ,,' <~,~ k
Meter 'i7tJO
i 'i).)$ TW4-15 It.{. 1'3 Flow 6 . d. (. .. J:> JII\
Meter ,):~ 7'S'J.6
I~ TW4-19 {,1.4 Flow f'J...e~c.r .{.' .. o'teJ\ "I"I".~ I),.t AlIA
Meter bbClI i 0
1i.(.0 ... TW4-20 11') 7d-.. Flow d....7 G-PM
Meter "64 "?:>.5q/)
Water: ~~C>510
Depth to Water
Date 1-/8 -;),0 10 mmHg G 17 QfC2,
Time Well Depth Comments
'.prJ
WtS MW-4 ~T'i) l Flow p()~. .:..+>1 I off of' ;"111.) i-i
Meter 1..i7(/O
flL/D TW4-15 <)'1':0 .' I _ Flow yq &P,,,\
Meter ,;).Lj)370
1 ct :!::~ v' TW4-19 I:,q Yi Flow t, ') i >1)IIJ "-' ".;\,> i
Meter £-hOI3D
'4'2,::' TW4-20 70rst Flow :;L;J. G-P;V\
Meter ~ '-1 T'3,){{j
,
,
.-,
If , L
Water: 33S'/70
Depth to Water
Date\-;::tS=;),O 10 mmHg G;;!'O.?bS
Time Well Depth Comments
1410 MW-4 hl. tS'i Flow I """~ PouJcJ' M ""',;\ IvlAI' Pt·
14:>-,0 Meter 4]~O
1~1.f) TW4-15 1t..(.(...x Flow 11 5.8 (,PM
Meter ~47~ YD
l<-{fO TW4-19 b6.<;'Y Flow b.LI &PM
. ".~. / Meter bb61~()
.'",t.;
1500 TW4-20 {.. 'S. 71 Flow d.4 (,.PM
Meter jl,F501{..,()
" .
RK
.,-,·i1'¥:.~.·-
.
Water: 3:38S5~
Chloroform Wells
Date ('28';<-0/0 mmHg tl9. SJ?
Time Well De~th Comments
~ ifs5"" MW-4 ~2LL3
12.35 TW4-1 6(, s I
CJ)153 TW4-2 ~5.31
[01(2 TW4-3 1(£ 7
/2-3q TW4-4 ~3.3;L
£21 '>£ TW4-5 5~· 1&
124~ TW4-6 1/. IJ 3
/1.33 TW4-7 ~/. tYI
1230 TW4-8 ~s, 1.<;
IOllil TW4-9 ,:S:2 .;-g
~Q4<; TW4-10 6.5", 'J
Q);56 TW4-11 ,2::3',11
iIiJ'2 TW4-12 ;:215'.35
L/ifJ TW4-13 i/ I{ 'i
III ;;. TW4-14 $1. db
LM41 TW4-15 153.2/
/O/d TW4-16 0.~, 't..~
10 I 'I TW4-17 1&.15
13qq TW4-18 51;..03
!':l60 TW4-19 1.1.6 '(
QK'IJ-TW4-20 kt,SL{
~'lg) TW4-21 5.5, 1S'i
a6J~ TW4-22 Sf?·.2 &,
pSi TW4-23 ~Ie, 4)
Q'631 TW4-24 ,Ii /z.. I tJ
6'i4~ TW4-25 ~4.1&
(
Date ;+-1·-;2.0(0
Time Well
!'::LIS MW-4
ntl~ TW4-15
11dJ) TW4-19
1:107 TW4-20
-rh \1-\.-!..I
Water:
Depth to Water
mmHg bd,Q,26g
Depth Comments
!:"S.q I Flow U i G-pfV1
Meter b~C;()
K~.b Flow ').s, G-P/V\
sr\",\,~~ «.\-11-:::-Meter :)sJ.,.l.sO
-Ikrf'\
~;:2.~ \ Flow 5·C! G-PM
Meter 1;)"03b6
(:"5. g:;l, Flow M<:l-r fl.."y'" ",;H n .. I
Meter s<t:,OX::lO
,
Fioh\
'M l.~
< s'/ 17,f(L/
14<,,' b
Depth to Water /
Date;l !i: j2!)1/l mmH9 _____ _
Time Well Depth Comments
/LJJI-J MW-4 ~ i It Flow lJ. :5 bIn{
'" Meter trY:3 t-I if {l6tf
Ii( }/} TW4-15 '1350 Flow 5 . .< b;LJ~
Meter :J .')70 7 ()
IS 10 TW4-19 t::1, Y"'! Flow r;, . 2 {" A/J/l
Meter '1203t:4
jL( if/ TW4-20 b%,17 Flow :J J t, Pr1
Meter :f.2s-.:z. ifl
J9/j' m .. d<I-i/ h.J-: :5.s-A ll/LA&C 70 i/
I /.L MA'" ~"-"-; ~T
Water: ')1,/<)/,7/
Depth to Water
Date 2/'z'3 / / D , I mmHg &;24.07-8'
Time Well Depth Comments
In'-C MW-4 o {.'?.f' Flow 1-/ I) t. n< &--0.
Meter +21')+
10'( <) TW4-15 ?),7u Flow 4, 7 .: M,l/"-
Meter 20",/2 +()
In <;''', TW4-19 !J~". 3 , Flow c;. L/ ,,,""-
Meter '64 -=r;:J..(,;,L'
1,0 Vi' TW4-20 7-\~, ~'-z. Flow 3.0 <a~
Meter 11'J~.2
il,on TLtJli L( ;. ,,7 I r:: I '" '"-'
)lVtc -h--
Water: 3'J3 xlfr/
Depth to Water
Date ~-Ik -;;J..Oj () mmHg 02;;l,.:SSY
Time Well Depth Comments
I Ll50 MW-4 (..X .qf<;. Flow Lj J (~PM
Meter r.:. f,::l t) t;. ") II
1.::..00 TW4-15 ({7.71 Flow \.L\ G-PM
<'11""'''',1 ,.I. 1'1.;c.. Meter '!LICI'IO
."" 0" p 'rlj
1353 TW4-19 y,S.Ci2. Flow b &Pi"\
Meter 7)( IISO
14 Lj:;l" TW4-20 f,C( .c(t Flow J.::' ("PM
Meter (;'SlR('" .~"
(tA)--zt· (J
Water: St.fl/573
Date ;). -J.6-;;2,O to
Time Well
1.29jC{ MW-4
O~ TW4-1
Dq:\~ TW4-2
()qL.j Ia TW4-3
D~);7 TW4-4
Q:J 4'::' TW4-5
01 ::'9 TW4-6
og5D TW4-7
-q~ . O.ot TW4-8
O'\~~ TW4-9
iYt':Jl TW4-10
IID3 TW4-11
IQO~ TW4-12
IQOi? TW4-13
IDII TW4-14
og·~q TW4-15
11Qb TW4-16
IIQ~ TW4-17
TW4-18
IUD. TW4-19
tfi"1b TW4-20
1117 TW4-21
ct£34 TW4-22
iO:S~ TW4-23
0«33 TW4-24
D~2 TW4-25
Depth
b1.12,
b( ,77
71.32.
E,£.15
66,qq
5b,~
18.SI
if,'J . 1)10
Comments
, ,
'\ " ,~ ~
{l \ ,\
Depth to Water
Date 3,~1 ~dDiO mmHg __ ~(~~~\~"~03~ __ _
Time Well Depth Comments
1500 MW-4 {}l. ;;:23 Flow 3.7 &PM
Meter 17br:,~Lq
1 1.1':;" TW4-15 ~3 .:J.() Flow j. 7 6-PIVl
! ~i\""'<.l.. ,.tt\.~ Puih Meter 271'-J~O
v.
13 LLt:; TW4-19 165.5Y Flow t::,' i-( &PM
Meter ~tt70<.j6
ILl ~jq TW4-20 7fl }:::~ Flow :2.;). G-f' fVI
Meter I'-V;r.\I./) l.s!
150b T~'-\-'-l \50·3i Flo,;> -7. I G-PM
I Mif 31)17.$(
-
Water: 3~7()4+-
Depth to Water
Date 3"·8'-.?610 mmHg fa (q, 13 r
Time Well Depth Comments
iY'l.,q MW-4 b't4S Flow ttd. &.p11A
Meter SLj 163;) \
H~o... TW4-15 is 1'~1 Flow 5,Q {~PM
Meter ~1:c,qq6
ISoS TW4-19 £:2 ~3 Flow~ I S ,q G-PM
Meter' . M ~qT050
1411-\ TW4-20 {i .. \ 31 Flow .J ,I G-PM
Meter 1'7 "')7 t.l.J. 7
144 5 ''"[1.(),-\ -L; -rt0 '1-L/ (~/'II 'Flo!» Cf.O GP~
/vlpJa-1O;;J.l.j I f,
Water: 3t;"a I bS
Time Well
15--;;2 MW-4
IZs/' TW4-15
1~2() TW4-19
I~ )<t TW4-20
Ig~ 'rTIA I L/ -l/
Water:
Depth to Water
mmHg (d0,3ti
n~Dth Comments
Co//' "1 s Flow '% s //) ,4
Meter 9t1S:tJ2. tf
ff} 1;1... *' Flow 5.7-b.Pf'I\.
Il .r. uP /£ I Meter 2 .M?()(')
xl. (FI Flow S 7' "-/J~A
Meter q; f<-Lft/()
---z:~.s / Flow 2.3 (7 i#1
Meter :J()/)S~ 7'<-,
f.t 1'1 I FIIIIAJ .. ;;;. / &, f)/I1
IIY/f>kf V)~
/h1{J:5~O
Date 3 'u-JAIO
Time Well
!.>rJ3 MW-4
1'157 TW4-15
i(}36 TW4-19
I'IS& TW4-20 ,
-W~J-I
16 It) 1V\J'-)-Y
Water:
Depth to Water
mmHg 0 ;20. 26 Y
Depth Comments
70. -"("i Flow 2. ;) &frrr.
Meter /J111IJ 71.:;;
73.3/ Flow 6. ~ ??t11.
Meter (,Xl'?fs'lr; iJ
ttl-.2t Flow s: r 0/111
Meter q#.'irlijfcl
;(2.2/ Flow 2. / hf1Y11
Meter I)~ ~32"1. 3
!it"'jJ /-wJ eN ,~ f<w:r /lr"~E.o -1JeJ., PVC,", r1-;k",-uJ ,
8tJ.1'6 ~tv' : ?! s trPt1A..
;i!trftL /JOO 23SZJ '1.t
<3f7-4~1
Depth to Water
Date '3",']q. 10 mmHg 620.26' 6'
Time Well Depth Comments
11m MW-4 77;). I Flow Lj I G-P!J)
Meter }():'.,q J.. k,.4{j
lYlL:, TW4-15 7b.n Flow GO C-P;\'\
Meter ;NO).,70
II i-b TW4-19 ~IL-II Flow 50:;), G-PM
Meter qgL)\L\O
I LlII TW4-20 bS.b'd... Flow :l:l &9M
Meter 'J:tb<1KO.6
IWd--T -nAlL.i -Li t...KII l=iNJ '1.LI C-FM
.M,J.(:r~D \(... Tl
Water: 3Q170b

Tab D
Kriged Current Quarter Groundwater Contour Map, Details Map, and Depth to Water Summary

HYDRO
GEO
CHEM, INC.APPROVED DATE REFERENCE FIGURE
3332
3000
SCALE IN FEET
0
5582
5503
5472
5503
5521
5501
5494
5494
5499
5587
5604
5458
5450
5498
5507
5537
5577
5543
5512
5538
5547 5557
5558
5584
5546
5586
5538
5584
5578
5565
5586
5572
5523
5544
5560
5548
55855571
5564
5583
5574
5593
5612
5602
5543
5541
MW-01
MW-02
MW-03
MW-05
MW-11
MW-12
MW-14
MW-15
MW-17
MW-18
MW-19
MW-20
MW-22
MW-23
MW-24
MW-25
MW-27
MW-28
MW-29
MW-30
MW-31

MW-26

MW-32
TW4-19

PIEZ-1
PIEZ-2
PIEZ-3
PIEZ-4
PIEZ-5
5546
5555 5555MW-04
5541
5569
5600

TWN-3
TWN-4
TWN-5
TWN-6
TWN-7
TWN-8
TWN-9
TWN-10
TWN-11 TWN-12
TWN-13
TWN-14
TWN-15
TWN-16
TWN-17
TWN-18
TWN-19
5603
5605
5585
5590
5560
5590
5583
5585
5615 5630
5587
5587
5584
5604
5606
5587
5607
5601
5612
TWN-1
TWN-2
TW4-20
TW4-4
MW-22
PIEZ-1
5450
5593
perched monitoring well showing
elevation in feet amsl
temporary perched monitoring well installed
April, 2005 showing elevation in feet amsl
perched piezometer showing
elevation in feet amsl
5557
MW-31
5547
temporary perched monitoring well
showing elevation in feet amsl
5574
perched monitoring well installed April, 2005
showing elevation in feet amsl KRIGED 1st QUARTER, 2010 WATER LEVELS
WHITE MESA SITE
H:/718000/may10/wl0310.srf
EXPLANATION
temporary perched monitoring well installed
May, 2007 showing elevation in feet amsl5541 SJS
temporary perched nitrate
monitoring well showing
elevation in feet amsl
TWN-4
5605
NOTE: MW-4, MW-26, TW4-4, TW4-19 and TW4-20 are pumping wells
HYDRO
GEO
CHEM, INC.APPROVED DATE REFERENCE FIGURE
3332
3000
SCALE IN FEET
0
5582
5503
5472
5503
5521
5501
5494
5494
5499
5587
5604
5458
5450
5498
5507
5537
5577
5543
5512
5538
5547 5557
5558
5584
5546
5586
5538
5584
5578
5565
5586
5572
5523
5544
5560
5548
55855571
5564
5583
5574
5593
5612
5602
5543
5541
MW-01
MW-02
MW-03
MW-05
MW-11
MW-12
MW-14
MW-15
MW-17
MW-18
MW-19
MW-20
MW-22
MW-23
MW-24
MW-25
MW-27
MW-28
MW-29
MW-30
MW-31

MW-26

MW-32
TW4-19

PIEZ-1
PIEZ-2
PIEZ-3
PIEZ-4
PIEZ-5
5546
5555 5555MW-04
5541
5569
5600

TWN-3
TWN-4
TWN-5
TWN-6
TWN-7
TWN-8
TWN-9
TWN-10
TWN-11 TWN-12
TWN-13
TWN-14
TWN-15
TWN-16
TWN-17
TWN-18
TWN-19
5603
5605
5585
5590
5560
5590
5583
5585
5615 5630
5587
5587
5584
5604
5606
5587
5607
5601
5612
TWN-1
TWN-2
TW4-20
TW4-4
MW-22
PIEZ-1
5450
5593
perched monitoring well showing
elevation in feet amsl
temporary perched monitoring well installed
April, 2005 showing elevation in feet amsl
perched piezometer showing
elevation in feet amsl
5557
MW-31
5547
temporary perched monitoring well
showing elevation in feet amsl
5574
perched monitoring well installed April, 2005
showing elevation in feet amsl
KRIGED 1st QUARTER, 2010 WATER LEVELS
AND ESTIMATED CAPTURE ZONES
WHITE MESA SITE
H:/718000/may10/wl0310cz2.srf
EXPLANATION
temporary perched monitoring well installed
May, 2007 showing elevation in feet amsl5541 SJS
temporary perched nitrate
monitoring well showing
elevation in feet amsl
TWN-4
5605
NOTE: MW-4, MW-26, TW4-4, TW4-19 and TW4-20 are pumping wells
estimated capture zone
boundary stream tubes
resulting from pumping
HYDRO
GEO
CHEM, INC.APPROVED DATE REFERENCE FIGURE
SCALE IN FEET
0 300150
( buried line )Tank
Holding
Waste
Lab
5537
5577
5547
5557
5558
5584
5546
5586
5538
5584
5578
5565
5586
5572
5523
5544
5560
5548
55855571
5564
5583
5574
5541
5569
5600
5612
5602
5601
5612
5603
5605
5560
5587
55465555
MW-25
MW-27
MW-31
TW4-1
TW4-2
TW4-3
TW4-4
TW4-5
TW4-6
TW4-9
TW4-10
TW4-11
TW4-12
TW4-13
TW4-14
MW-26
TW4-16
MW-32
TW4-18TW4-19
TW4-20
TW4-21
TW4-22
TW4-23
TW4-24
TW4-25
PIEZ-2
PIEZ-3
TWN-1
TWN-2
TWN-3
TWN-4
TWN-7
TWN-18
MW-04TW4-7
KRIGED 1st QUARTER, 2010 WATER LEVELS
AND ESTIMATED CAPTURE ZONES
WHITE MESA SITE
(detail map)
temporary perched monitoring well
showing elevation in feet amsl
perched monitoring well showing
elevation in feet amsl
TW4-1
5557
MW-32
5548
EXPLANATION
estimated capture zone
boundary stream tubes
resulting from pumping
NOTE: MW-4, MW-26, TW4-4, TW4-19, and TW4-20 are pumping wells
SJS H:/718000/fmay10/wl0310cz.srf
TWN-1
5601 temporary perched nitrate monitoring
well showing elevation in feet amsl
Quarterly Depth to Water
NAME: Tanner Holliday MMHG:
Start time: 800
DATE: 3/11/2010 Finish Time: 1530
TIME WELL I.D. DEPTH TIME WELL I.D. DEPTH TIME WELL I.D. DEPTH
1256 MW-l 65.65 1017 MW-4 76.25 1217 PIEZ-l 62.25
1332 MW-2 109.64 1021 TW4-1 61.83 1212 PIEZ-2 16.67
1439 MW-3 83.17 1015 TW4-2 66.85 1209 PIEZ-3 35.82
~-1442 MW-3A 85.24 1013 TW4-3 48.60 1035 PIEZ-4 48.61
1021 MW-4 61.83 1024 TW4-4 67.89 1042 PIEZ-5 43.31
816 MW-5 106.41 1010 TW4-5 55.04
832 MW-11 89.81 1027 TW4-6 70.85 1156 TWN-l 47.54
821 MW-12 108.43 1018 TW4-7 66.43 803 TWN-2 14.24
828 MW-14 103.76 1023 TW4-8 66.75 1159 TWN-3 31.60
825 MW-15 106.40 1012 TW4-9 53.59 1206 TWN-4 36.56
1435 MW-17 76.57 1009 TW4-1O 55.86 1301 TWN-5 70.21
1253 MW-18 70.75 844 TW4-11 58.48 1246 TWN-6 74.70
1214 MW-19 50.61 1426 TW4-12 38.35 1301 TWN-7 89.72
1446 MW-20 83.00 1427 TW4-13 47.93 1249 TWN-8 61.80
1451 MW-22 67.10 1428 TW4-14 89.79 1220 TWN-9 64.53
814 MW-23 113.91 849 TW4-15 81.67 1243 TWN-lO 81.77
857 MW-24 114.62 1510 TW4-16 64.22 1235 TWN-11 69.88
830 MW:25 75.31 841 TW4-17 76.74 1233 TWN-12 37.97
849 MW-26 81.67 1404 TW4-18 56.02 1224 TWN-13 46.87
1048 MW-27 50.87 1516 TW4-19 60.81 1226 TWN-14 62.82
809 MW-28 77.41 1007 TW4-20 65.44 1240 TWN-15 92.39
813 MW-29 102.50 807 TW4-21 56.54 1231 TWN-16 48.86
839 MW-30 76.91 1004 TW4-22 55.12 1229 TWN-17 35.30
840 MW-31 69.31 1030 TW4-23 66.22 1201 TWN-18 58.09
841 MW-32 76.74 1003 TW4-24 55.97 1320 TWN-19 54.14
805 TW4-25 45.16
Comments: some of the times appear to be off a little bit, its due totJsing two different vehicles with which the
clocks varied by about 15~20 minutes. This was not identified until the event was done. So rather than change
numbers to what we think they should have been the times will be left as recorded.

Tab E
Kriged Previous Quarter Groundwater Contour Map

HYDRO
GEO
CHEM, INC.APPROVED DATE REFERENCE FIGURE
3332
3000
SCALE IN FEET
0
5582
5503
5471
5502
5521
5501
5494
5493
5498
5587
5604
5458
5450
5498
5507
5537
5576
5543
5512
5537
5547 5557
5557
5583
5550
5585
5537
5583
5578
5565
5586
5571
5524
5549
5559
5548
55845548
5561
5580
5574
5593
5614
5600
5542
5541
MW-01
MW-02
MW-03
MW-05
MW-11
MW-12
MW-14
MW-15
MW-17
MW-18
MW-19
MW-20
MW-22
MW-23
MW-24
MW-25
MW-27
MW-28
MW-29
MW-30
MW-31

MW-26

MW-32
TW4-19

PIEZ-1
PIEZ-2
PIEZ-3
PIEZ-4
PIEZ-5
5551
5553 5554MW-04
5541
5569
5599

TWN-3
TWN-4
TWN-5
TWN-6
TWN-7
TWN-8
TWN-9
TWN-10
TWN-11 TWN-12
TWN-13
TWN-14
TWN-15
TWN-16
TWN-17
TWN-18
TWN-19
5603
5606
5585
5590
5559
5603
5583
5585
5614 5629
5587
5587
5584
5604
5606
5600
5607
5603
5607
TWN-1
TWN-2
TW4-20
MW-22
PIEZ-1
5450
5593
perched monitoring well showing
elevation in feet amsl
temporary perched monitoring well installed
April, 2005 showing elevation in feet amsl
perched piezometer showing
elevation in feet amsl
5556
MW-31
5547
temporary perched monitoring well
showing elevation in feet amsl
5574
perched monitoring well installed April, 2005
showing elevation in feet amsl KRIGED 4th QUARTER, 2009 WATER LEVELS
WHITE MESA SITE
H:/718000/feb10/wl1209c.srf
EXPLANATION
temporary perched monitoring well installed
May, 2007 showing elevation in feet amsl5541 SJS
temporary perched nitrate
monitoring well showing
elevation in feet amsl
TWN-4
5605

Tab F
Hydrographs of Groundwater Elevations Over Time for Chloroform Monitoring Wells

50.0
60.0
70.0
80.0
10
/
1
0
/
7
9
09
/
1
5
/
8
0
12
/
0
1
/
8
4
10
/
0
1
/
8
5
06
/
1
9
/
8
6
04
/
2
8
/
8
7
06
/
0
1
/
8
8
06
/
2
1
/
8
9
05
/
0
8
/
9
0
05
/
2
1
/
9
1
06
/
1
1
/
9
2
06
/
0
8
/
9
3
06
/
1
5
/
9
4
06
/
2
7
/
9
5
06
/
0
7
/
9
6
05
/
1
1
/
9
9
04
/
0
4
/
0
0
05
/
2
5
/
0
0
07
/
0
6
/
0
0
08
/
0
2
/
0
0
09
/
0
8
/
0
0
10
/
0
5
/
0
0
11
/
0
9
/
0
0
12
/
0
7
/
0
0
04
/
3
0
/
0
1
08
/
2
0
/
0
1
12
/
0
3
/
0
1
04
/
0
9
/
0
2
08
/
2
3
/
0
2
12
/
0
3
/
0
2
04
/
0
2
/
0
3
08
/
0
4
/
0
3
12
/
0
3
/
0
3
04
/
1
2
/
0
4
08
/
3
0
/
0
4
12
/
2
2
/
0
4
04
/
2
6
/
0
5
09
/
1
2
/
0
5
06
/
1
3
/
0
6
05
/
0
2
/
0
7
06
/
2
5
/
0
8
06
/
2
4
/
0
9
ea
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
MW‐4 Water Depth Over Time (ft. blmp)
50.0
60.0
70.0
80.0
90.0
100.0
110.0
120.0
10
/
1
0
/
7
9
09
/
1
5
/
8
0
12
/
0
1
/
8
4
10
/
0
1
/
8
5
06
/
1
9
/
8
6
04
/
2
8
/
8
7
06
/
0
1
/
8
8
06
/
2
1
/
8
9
05
/
0
8
/
9
0
05
/
2
1
/
9
1
06
/
1
1
/
9
2
06
/
0
8
/
9
3
06
/
1
5
/
9
4
06
/
2
7
/
9
5
06
/
0
7
/
9
6
05
/
1
1
/
9
9
04
/
0
4
/
0
0
05
/
2
5
/
0
0
07
/
0
6
/
0
0
08
/
0
2
/
0
0
09
/
0
8
/
0
0
10
/
0
5
/
0
0
11
/
0
9
/
0
0
12
/
0
7
/
0
0
04
/
3
0
/
0
1
08
/
2
0
/
0
1
12
/
0
3
/
0
1
04
/
0
9
/
0
2
08
/
2
3
/
0
2
12
/
0
3
/
0
2
04
/
0
2
/
0
3
08
/
0
4
/
0
3
12
/
0
3
/
0
3
04
/
1
2
/
0
4
08
/
3
0
/
0
4
12
/
2
2
/
0
4
04
/
2
6
/
0
5
09
/
1
2
/
0
5
06
/
1
3
/
0
6
05
/
0
2
/
0
7
06
/
2
5
/
0
8
06
/
2
4
/
0
9
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
MW‐4 Water Depth Over Time (ft. blmp)
55.0
60.0
65.0
70 0
11
/
0
8
/
9
9
02
/
0
8
/
0
0
05
/
0
8
/
0
0
08
/
0
8
/
0
0
11
/
0
8
/
0
0
02
/
0
8
/
0
1
05
/
0
8
/
0
1
08
/
0
8
/
0
1
11
/
0
8
/
0
1
02
/
0
8
/
0
2
05
/
0
8
/
0
2
08
/
0
8
/
0
2
11
/
0
8
/
0
2
02
/
0
8
/
0
3
05
/
0
8
/
0
3
08
/
0
8
/
0
3
11
/
0
8
/
0
3
02
/
0
8
/
0
4
05
/
0
8
/
0
4
08
/
0
8
/
0
4
11
/
0
8
/
0
4
02
/
0
8
/
0
5
05
/
0
8
/
0
5
08
/
0
8
/
0
5
11
/
0
8
/
0
5
02
/
0
8
/
0
6
05
/
0
8
/
0
6
08
/
0
8
/
0
6
11
/
0
8
/
0
6
02
/
0
8
/
0
7
05
/
0
8
/
0
7
08
/
0
8
/
0
7
11
/
0
8
/
0
7
02
/
0
8
/
0
8
05
/
0
8
/
0
8
08
/
0
8
/
0
8
11
/
0
8
/
0
8
02
/
0
8
/
0
9
05
/
0
8
/
0
9
08
/
0
8
/
0
9
11
/
0
8
/
0
9
02
/
0
8
/
1
0
asu
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐1 Water Depth Over Time (ft. blmp)
55.0
60.0
65.0
70.0
75.0
80.0
85.0
11
/
0
8
/
9
9
02
/
0
8
/
0
0
05
/
0
8
/
0
0
08
/
0
8
/
0
0
11
/
0
8
/
0
0
02
/
0
8
/
0
1
05
/
0
8
/
0
1
08
/
0
8
/
0
1
11
/
0
8
/
0
1
02
/
0
8
/
0
2
05
/
0
8
/
0
2
08
/
0
8
/
0
2
11
/
0
8
/
0
2
02
/
0
8
/
0
3
05
/
0
8
/
0
3
08
/
0
8
/
0
3
11
/
0
8
/
0
3
02
/
0
8
/
0
4
05
/
0
8
/
0
4
08
/
0
8
/
0
4
11
/
0
8
/
0
4
02
/
0
8
/
0
5
05
/
0
8
/
0
5
08
/
0
8
/
0
5
11
/
0
8
/
0
5
02
/
0
8
/
0
6
05
/
0
8
/
0
6
08
/
0
8
/
0
6
11
/
0
8
/
0
6
02
/
0
8
/
0
7
05
/
0
8
/
0
7
08
/
0
8
/
0
7
11
/
0
8
/
0
7
02
/
0
8
/
0
8
05
/
0
8
/
0
8
08
/
0
8
/
0
8
11
/
0
8
/
0
8
02
/
0
8
/
0
9
05
/
0
8
/
0
9
08
/
0
8
/
0
9
11
/
0
8
/
0
9
02
/
0
8
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐1 Water Depth Over Time (ft. blmp)
62.0
64.0
66.0
68.0
70.0
72.0
11
/
0
8
/
9
9
01
/
1
0
/
0
0
02
/
0
1
/
0
0
02
/
2
3
/
0
0
03
/
1
5
/
0
0
04
/
0
4
/
0
0
04
/
2
8
/
0
0
05
/
1
5
/
0
0
06
/
1
6
/
0
0
07
/
1
3
/
0
0
08
/
0
2
/
0
0
08
/
3
1
/
0
0
09
/
2
0
/
0
0
12
/
0
6
/
0
0
03
/
2
9
/
0
1
06
/
2
1
/
0
1
09
/
1
9
/
0
1
12
/
0
3
/
0
1
03
/
2
6
/
0
2
06
/
0
5
/
0
2
09
/
1
1
/
0
2
12
/
0
3
/
0
2
03
/
2
6
/
0
3
06
/
0
9
/
0
3
09
/
1
1
/
0
3
12
/
0
3
/
0
3
03
/
2
8
/
0
4
06
/
1
8
/
0
4
09
/
1
6
/
0
4
12
/
2
2
/
0
4
03
/
1
5
/
0
5
06
/
3
0
/
0
5
12
/
0
7
/
0
5
07
/
1
8
/
0
6
05
/
0
2
/
0
7
03
/
2
6
/
0
8
10
/
1
4
/
0
8
09
/
1
0
/
0
9
ow Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐2 Water Depth Over Time (ft. blmp)
62.0
64.0
66.0
68.0
70.0
72.0
74.0
76.0
78.0
80.0
11
/
0
8
/
9
9
01
/
1
0
/
0
0
02
/
0
1
/
0
0
02
/
2
3
/
0
0
03
/
1
5
/
0
0
04
/
0
4
/
0
0
04
/
2
8
/
0
0
05
/
1
5
/
0
0
06
/
1
6
/
0
0
07
/
1
3
/
0
0
08
/
0
2
/
0
0
08
/
3
1
/
0
0
09
/
2
0
/
0
0
12
/
0
6
/
0
0
03
/
2
9
/
0
1
06
/
2
1
/
0
1
09
/
1
9
/
0
1
12
/
0
3
/
0
1
03
/
2
6
/
0
2
06
/
0
5
/
0
2
09
/
1
1
/
0
2
12
/
0
3
/
0
2
03
/
2
6
/
0
3
06
/
0
9
/
0
3
09
/
1
1
/
0
3
12
/
0
3
/
0
3
03
/
2
8
/
0
4
06
/
1
8
/
0
4
09
/
1
6
/
0
4
12
/
2
2
/
0
4
03
/
1
5
/
0
5
06
/
3
0
/
0
5
12
/
0
7
/
0
5
07
/
1
8
/
0
6
05
/
0
2
/
0
7
03
/
2
6
/
0
8
10
/
1
4
/
0
8
09
/
1
0
/
0
9
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐2 Water Depth Over Time (ft. blmp)
40.0
45.0
50.0
55.0
11
/
2
9
/
9
9
01
/
1
7
/
0
0
02
/
0
7
/
0
0
03
/
0
1
/
0
0
03
/
2
0
/
0
0
04
/
1
3
/
0
0
05
/
0
1
/
0
0
05
/
2
5
/
0
0
06
/
2
6
/
0
0
07
/
1
3
/
0
0
08
/
0
2
/
0
0
08
/
3
1
/
0
0
09
/
2
0
/
0
0
12
/
0
6
/
0
0
03
/
2
8
/
0
1
06
/
2
1
/
0
1
09
/
1
9
/
0
1
06
/
2
1
/
0
1
09
/
1
9
/
0
1
12
/
0
3
/
0
1
03
/
2
6
/
0
2
06
/
0
5
/
0
2
09
/
1
1
/
0
2
12
/
0
3
/
0
2
03
/
2
6
/
0
3
06
/
0
9
/
0
3
09
/
1
1
/
0
3
12
/
0
3
/
0
3
03
/
2
8
/
0
4
06
/
1
8
/
0
4
09
/
1
6
/
0
4
12
/
2
2
/
0
4
03
/
1
5
/
0
5
06
/
3
0
/
0
5
12
/
0
7
/
0
5
07
/
1
8
/
0
6
05
/
0
2
/
0
7
03
/
2
6
/
0
8
10
/
1
4
/
0
8
09
/
1
0
/
0
9
eas
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐3 Water Depth Over Time (ft.  blmp)
40.0
45.0
50.0
55.0
60.0
65.0
70.0
75.0
11
/
2
9
/
9
9
01
/
1
7
/
0
0
02
/
0
7
/
0
0
03
/
0
1
/
0
0
03
/
2
0
/
0
0
04
/
1
3
/
0
0
05
/
0
1
/
0
0
05
/
2
5
/
0
0
06
/
2
6
/
0
0
07
/
1
3
/
0
0
08
/
0
2
/
0
0
08
/
3
1
/
0
0
09
/
2
0
/
0
0
12
/
0
6
/
0
0
03
/
2
8
/
0
1
06
/
2
1
/
0
1
09
/
1
9
/
0
1
06
/
2
1
/
0
1
09
/
1
9
/
0
1
12
/
0
3
/
0
1
03
/
2
6
/
0
2
06
/
0
5
/
0
2
09
/
1
1
/
0
2
12
/
0
3
/
0
2
03
/
2
6
/
0
3
06
/
0
9
/
0
3
09
/
1
1
/
0
3
12
/
0
3
/
0
3
03
/
2
8
/
0
4
06
/
1
8
/
0
4
09
/
1
6
/
0
4
12
/
2
2
/
0
4
03
/
1
5
/
0
5
06
/
3
0
/
0
5
12
/
0
7
/
0
5
07
/
1
8
/
0
6
05
/
0
2
/
0
7
03
/
2
6
/
0
8
10
/
1
4
/
0
8
09
/
1
0
/
0
9
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐3 Water Depth Over Time (ft.  blmp)
50.0
60.0
70.0
80.0
05
/
2
5
/
0
0
11
/
2
5
/
0
0
05
/
2
5
/
0
1
11
/
2
5
/
0
1
05
/
2
5
/
0
2
11
/
2
5
/
0
2
05
/
2
5
/
0
3
11
/
2
5
/
0
3
05
/
2
5
/
0
4
11
/
2
5
/
0
4
05
/
2
5
/
0
5
11
/
2
5
/
0
5
05
/
2
5
/
0
6
11
/
2
5
/
0
6
05
/
2
5
/
0
7
11
/
2
5
/
0
7
05
/
2
5
/
0
8
11
/
2
5
/
0
8
05
/
2
5
/
0
9
11
/
2
5
/
0
9
ea
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐4 Water Depth Over Time (ft. blmp)
50.0
60.0
70.0
80.0
90.0
100.0
110.0
05
/
2
5
/
0
0
11
/
2
5
/
0
0
05
/
2
5
/
0
1
11
/
2
5
/
0
1
05
/
2
5
/
0
2
11
/
2
5
/
0
2
05
/
2
5
/
0
3
11
/
2
5
/
0
3
05
/
2
5
/
0
4
11
/
2
5
/
0
4
05
/
2
5
/
0
5
11
/
2
5
/
0
5
05
/
2
5
/
0
6
11
/
2
5
/
0
6
05
/
2
5
/
0
7
11
/
2
5
/
0
7
05
/
2
5
/
0
8
11
/
2
5
/
0
8
05
/
2
5
/
0
9
11
/
2
5
/
0
9
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐4 Water Depth Over Time (ft. blmp)
50.0
52.0
54.0
56.0
01
/
0
2
/
0
0
07
/
0
2
/
0
0
01
/
0
2
/
0
1
07
/
0
2
/
0
1
01
/
0
2
/
0
2
07
/
0
2
/
0
2
01
/
0
2
/
0
3
07
/
0
2
/
0
3
01
/
0
2
/
0
4
07
/
0
2
/
0
4
01
/
0
2
/
0
5
07
/
0
2
/
0
5
01
/
0
2
/
0
6
07
/
0
2
/
0
6
01
/
0
2
/
0
7
07
/
0
2
/
0
7
01
/
0
2
/
0
8
07
/
0
2
/
0
8
01
/
0
2
/
0
9
07
/
0
2
/
0
9
01
/
0
2
/
1
0
eas
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐5 Water Depth Over time (ft. blmp)
50.0
52.0
54.0
56.0
58.0
60.0
62.0
01
/
0
2
/
0
0
07
/
0
2
/
0
0
01
/
0
2
/
0
1
07
/
0
2
/
0
1
01
/
0
2
/
0
2
07
/
0
2
/
0
2
01
/
0
2
/
0
3
07
/
0
2
/
0
3
01
/
0
2
/
0
4
07
/
0
2
/
0
4
01
/
0
2
/
0
5
07
/
0
2
/
0
5
01
/
0
2
/
0
6
07
/
0
2
/
0
6
01
/
0
2
/
0
7
07
/
0
2
/
0
7
01
/
0
2
/
0
8
07
/
0
2
/
0
8
01
/
0
2
/
0
9
07
/
0
2
/
0
9
01
/
0
2
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐5 Water Depth Over time (ft. blmp)
TW4‐6 Water level Over time (ft. blmp)
50.0
05
/
2
5
/
0
0
08
/
2
5
/
0
0
11
/
2
5
/
0
0
02
/
2
5
/
0
1
05
/
2
5
/
0
1
08
/
2
5
/
0
1
11
/
2
5
/
0
1
02
/
2
5
/
0
2
05
/
2
5
/
0
2
08
/
2
5
/
0
2
11
/
2
5
/
0
2
02
/
2
5
/
0
3
05
/
2
5
/
0
3
08
/
2
5
/
0
3
11
/
2
5
/
0
3
02
/
2
5
/
0
4
05
/
2
5
/
0
4
08
/
2
5
/
0
4
11
/
2
5
/
0
4
02
/
2
5
/
0
5
05
/
2
5
/
0
5
08
/
2
5
/
0
5
11
/
2
5
/
0
5
02
/
2
5
/
0
6
05
/
2
5
/
0
6
08
/
2
5
/
0
6
11
/
2
5
/
0
6
02
/
2
5
/
0
7
05
/
2
5
/
0
7
08
/
2
5
/
0
7
11
/
2
5
/
0
7
02
/
2
5
/
0
8
05
/
2
5
/
0
8
08
/
2
5
/
0
8
11
/
2
5
/
0
8
02
/
2
5
/
0
9
05
/
2
5
/
0
9
08
/
2
5
/
0
9
11
/
2
5
/
0
9
02
/
2
5
/
1
0
TW4‐6 Water level Over time (ft. blmp)
50.0
55.0
60.0
05
/
2
5
/
0
0
08
/
2
5
/
0
0
11
/
2
5
/
0
0
02
/
2
5
/
0
1
05
/
2
5
/
0
1
08
/
2
5
/
0
1
11
/
2
5
/
0
1
02
/
2
5
/
0
2
05
/
2
5
/
0
2
08
/
2
5
/
0
2
11
/
2
5
/
0
2
02
/
2
5
/
0
3
05
/
2
5
/
0
3
08
/
2
5
/
0
3
11
/
2
5
/
0
3
02
/
2
5
/
0
4
05
/
2
5
/
0
4
08
/
2
5
/
0
4
11
/
2
5
/
0
4
02
/
2
5
/
0
5
05
/
2
5
/
0
5
08
/
2
5
/
0
5
11
/
2
5
/
0
5
02
/
2
5
/
0
6
05
/
2
5
/
0
6
08
/
2
5
/
0
6
11
/
2
5
/
0
6
02
/
2
5
/
0
7
05
/
2
5
/
0
7
08
/
2
5
/
0
7
11
/
2
5
/
0
7
02
/
2
5
/
0
8
05
/
2
5
/
0
8
08
/
2
5
/
0
8
11
/
2
5
/
0
8
02
/
2
5
/
0
9
05
/
2
5
/
0
9
08
/
2
5
/
0
9
11
/
2
5
/
0
9
02
/
2
5
/
1
0
(ft
.
)
TW4‐6 Water level Over time (ft. blmp)
50.0
55.0
60.0
65.0
70.0
75.0
05
/
2
5
/
0
0
08
/
2
5
/
0
0
11
/
2
5
/
0
0
02
/
2
5
/
0
1
05
/
2
5
/
0
1
08
/
2
5
/
0
1
11
/
2
5
/
0
1
02
/
2
5
/
0
2
05
/
2
5
/
0
2
08
/
2
5
/
0
2
11
/
2
5
/
0
2
02
/
2
5
/
0
3
05
/
2
5
/
0
3
08
/
2
5
/
0
3
11
/
2
5
/
0
3
02
/
2
5
/
0
4
05
/
2
5
/
0
4
08
/
2
5
/
0
4
11
/
2
5
/
0
4
02
/
2
5
/
0
5
05
/
2
5
/
0
5
08
/
2
5
/
0
5
11
/
2
5
/
0
5
02
/
2
5
/
0
6
05
/
2
5
/
0
6
08
/
2
5
/
0
6
11
/
2
5
/
0
6
02
/
2
5
/
0
7
05
/
2
5
/
0
7
08
/
2
5
/
0
7
11
/
2
5
/
0
7
02
/
2
5
/
0
8
05
/
2
5
/
0
8
08
/
2
5
/
0
8
11
/
2
5
/
0
8
02
/
2
5
/
0
9
05
/
2
5
/
0
9
08
/
2
5
/
0
9
11
/
2
5
/
0
9
02
/
2
5
/
1
0
Mea
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐6 Water level Over time (ft. blmp)
50.0
55.0
60.0
65.0
70.0
75.0
80.0
85.0
90.0
05
/
2
5
/
0
0
08
/
2
5
/
0
0
11
/
2
5
/
0
0
02
/
2
5
/
0
1
05
/
2
5
/
0
1
08
/
2
5
/
0
1
11
/
2
5
/
0
1
02
/
2
5
/
0
2
05
/
2
5
/
0
2
08
/
2
5
/
0
2
11
/
2
5
/
0
2
02
/
2
5
/
0
3
05
/
2
5
/
0
3
08
/
2
5
/
0
3
11
/
2
5
/
0
3
02
/
2
5
/
0
4
05
/
2
5
/
0
4
08
/
2
5
/
0
4
11
/
2
5
/
0
4
02
/
2
5
/
0
5
05
/
2
5
/
0
5
08
/
2
5
/
0
5
11
/
2
5
/
0
5
02
/
2
5
/
0
6
05
/
2
5
/
0
6
08
/
2
5
/
0
6
11
/
2
5
/
0
6
02
/
2
5
/
0
7
05
/
2
5
/
0
7
08
/
2
5
/
0
7
11
/
2
5
/
0
7
02
/
2
5
/
0
8
05
/
2
5
/
0
8
08
/
2
5
/
0
8
11
/
2
5
/
0
8
02
/
2
5
/
0
9
05
/
2
5
/
0
9
08
/
2
5
/
0
9
11
/
2
5
/
0
9
02
/
2
5
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐6 Water level Over time (ft. blmp)
50.0
55.0
60.0
65.0
70.0
75.0
80.0
85.0
90.0
95.0
100.0
05
/
2
5
/
0
0
08
/
2
5
/
0
0
11
/
2
5
/
0
0
02
/
2
5
/
0
1
05
/
2
5
/
0
1
08
/
2
5
/
0
1
11
/
2
5
/
0
1
02
/
2
5
/
0
2
05
/
2
5
/
0
2
08
/
2
5
/
0
2
11
/
2
5
/
0
2
02
/
2
5
/
0
3
05
/
2
5
/
0
3
08
/
2
5
/
0
3
11
/
2
5
/
0
3
02
/
2
5
/
0
4
05
/
2
5
/
0
4
08
/
2
5
/
0
4
11
/
2
5
/
0
4
02
/
2
5
/
0
5
05
/
2
5
/
0
5
08
/
2
5
/
0
5
11
/
2
5
/
0
5
02
/
2
5
/
0
6
05
/
2
5
/
0
6
08
/
2
5
/
0
6
11
/
2
5
/
0
6
02
/
2
5
/
0
7
05
/
2
5
/
0
7
08
/
2
5
/
0
7
11
/
2
5
/
0
7
02
/
2
5
/
0
8
05
/
2
5
/
0
8
08
/
2
5
/
0
8
11
/
2
5
/
0
8
02
/
2
5
/
0
9
05
/
2
5
/
0
9
08
/
2
5
/
0
9
11
/
2
5
/
0
9
02
/
2
5
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐6 Water level Over time (ft. blmp)
50.0
55.0
60.0
65.0
70.0
75.0
80.0
85.0
90.0
95.0
100.0
05
/
2
5
/
0
0
08
/
2
5
/
0
0
11
/
2
5
/
0
0
02
/
2
5
/
0
1
05
/
2
5
/
0
1
08
/
2
5
/
0
1
11
/
2
5
/
0
1
02
/
2
5
/
0
2
05
/
2
5
/
0
2
08
/
2
5
/
0
2
11
/
2
5
/
0
2
02
/
2
5
/
0
3
05
/
2
5
/
0
3
08
/
2
5
/
0
3
11
/
2
5
/
0
3
02
/
2
5
/
0
4
05
/
2
5
/
0
4
08
/
2
5
/
0
4
11
/
2
5
/
0
4
02
/
2
5
/
0
5
05
/
2
5
/
0
5
08
/
2
5
/
0
5
11
/
2
5
/
0
5
02
/
2
5
/
0
6
05
/
2
5
/
0
6
08
/
2
5
/
0
6
11
/
2
5
/
0
6
02
/
2
5
/
0
7
05
/
2
5
/
0
7
08
/
2
5
/
0
7
11
/
2
5
/
0
7
02
/
2
5
/
0
8
05
/
2
5
/
0
8
08
/
2
5
/
0
8
11
/
2
5
/
0
8
02
/
2
5
/
0
9
05
/
2
5
/
0
9
08
/
2
5
/
0
9
11
/
2
5
/
0
9
02
/
2
5
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐6 Water level Over time (ft. blmp)
TW4‐7 Water Level Over time (ft. blmp)
50.0
11
/
2
9
/
9
9
02
/
2
9
/
0
0
05
/
3
1
/
0
0
08
/
3
1
/
0
0
11
/
3
0
/
0
0
02
/
2
8
/
0
1
05
/
3
1
/
0
1
08
/
3
1
/
0
1
11
/
3
0
/
0
1
02
/
2
8
/
0
2
05
/
3
1
/
0
2
08
/
3
1
/
0
2
11
/
3
0
/
0
2
02
/
2
8
/
0
3
05
/
3
1
/
0
3
08
/
3
1
/
0
3
11
/
3
0
/
0
3
02
/
2
9
/
0
4
05
/
3
1
/
0
4
08
/
3
1
/
0
4
11
/
3
0
/
0
4
02
/
2
8
/
0
5
05
/
3
1
/
0
5
08
/
3
1
/
0
5
11
/
3
0
/
0
5
02
/
2
8
/
0
6
05
/
3
1
/
0
6
08
/
3
1
/
0
6
11
/
3
0
/
0
6
02
/
2
8
/
0
7
05
/
3
1
/
0
7
08
/
3
1
/
0
7
11
/
3
0
/
0
7
02
/
2
9
/
0
8
05
/
3
1
/
0
8
08
/
3
1
/
0
8
11
/
3
0
/
0
8
02
/
2
8
/
0
9
05
/
3
1
/
0
9
08
/
3
1
/
0
9
11
/
3
0
/
0
9
02
/
2
8
/
1
0
TW4‐7 Water Level Over time (ft. blmp)
50.0
55.0
60.0
11
/
2
9
/
9
9
02
/
2
9
/
0
0
05
/
3
1
/
0
0
08
/
3
1
/
0
0
11
/
3
0
/
0
0
02
/
2
8
/
0
1
05
/
3
1
/
0
1
08
/
3
1
/
0
1
11
/
3
0
/
0
1
02
/
2
8
/
0
2
05
/
3
1
/
0
2
08
/
3
1
/
0
2
11
/
3
0
/
0
2
02
/
2
8
/
0
3
05
/
3
1
/
0
3
08
/
3
1
/
0
3
11
/
3
0
/
0
3
02
/
2
9
/
0
4
05
/
3
1
/
0
4
08
/
3
1
/
0
4
11
/
3
0
/
0
4
02
/
2
8
/
0
5
05
/
3
1
/
0
5
08
/
3
1
/
0
5
11
/
3
0
/
0
5
02
/
2
8
/
0
6
05
/
3
1
/
0
6
08
/
3
1
/
0
6
11
/
3
0
/
0
6
02
/
2
8
/
0
7
05
/
3
1
/
0
7
08
/
3
1
/
0
7
11
/
3
0
/
0
7
02
/
2
9
/
0
8
05
/
3
1
/
0
8
08
/
3
1
/
0
8
11
/
3
0
/
0
8
02
/
2
8
/
0
9
05
/
3
1
/
0
9
08
/
3
1
/
0
9
11
/
3
0
/
0
9
02
/
2
8
/
1
0
nt (f
t
.
)
TW4‐7 Water Level Over time (ft. blmp)
50.0
55.0
60.0
65.0
70.0
11
/
2
9
/
9
9
02
/
2
9
/
0
0
05
/
3
1
/
0
0
08
/
3
1
/
0
0
11
/
3
0
/
0
0
02
/
2
8
/
0
1
05
/
3
1
/
0
1
08
/
3
1
/
0
1
11
/
3
0
/
0
1
02
/
2
8
/
0
2
05
/
3
1
/
0
2
08
/
3
1
/
0
2
11
/
3
0
/
0
2
02
/
2
8
/
0
3
05
/
3
1
/
0
3
08
/
3
1
/
0
3
11
/
3
0
/
0
3
02
/
2
9
/
0
4
05
/
3
1
/
0
4
08
/
3
1
/
0
4
11
/
3
0
/
0
4
02
/
2
8
/
0
5
05
/
3
1
/
0
5
08
/
3
1
/
0
5
11
/
3
0
/
0
5
02
/
2
8
/
0
6
05
/
3
1
/
0
6
08
/
3
1
/
0
6
11
/
3
0
/
0
6
02
/
2
8
/
0
7
05
/
3
1
/
0
7
08
/
3
1
/
0
7
11
/
3
0
/
0
7
02
/
2
9
/
0
8
05
/
3
1
/
0
8
08
/
3
1
/
0
8
11
/
3
0
/
0
8
02
/
2
8
/
0
9
05
/
3
1
/
0
9
08
/
3
1
/
0
9
11
/
3
0
/
0
9
02
/
2
8
/
1
0
Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐7 Water Level Over time (ft. blmp)
50.0
55.0
60.0
65.0
70.0
75.0
80.0
11
/
2
9
/
9
9
02
/
2
9
/
0
0
05
/
3
1
/
0
0
08
/
3
1
/
0
0
11
/
3
0
/
0
0
02
/
2
8
/
0
1
05
/
3
1
/
0
1
08
/
3
1
/
0
1
11
/
3
0
/
0
1
02
/
2
8
/
0
2
05
/
3
1
/
0
2
08
/
3
1
/
0
2
11
/
3
0
/
0
2
02
/
2
8
/
0
3
05
/
3
1
/
0
3
08
/
3
1
/
0
3
11
/
3
0
/
0
3
02
/
2
9
/
0
4
05
/
3
1
/
0
4
08
/
3
1
/
0
4
11
/
3
0
/
0
4
02
/
2
8
/
0
5
05
/
3
1
/
0
5
08
/
3
1
/
0
5
11
/
3
0
/
0
5
02
/
2
8
/
0
6
05
/
3
1
/
0
6
08
/
3
1
/
0
6
11
/
3
0
/
0
6
02
/
2
8
/
0
7
05
/
3
1
/
0
7
08
/
3
1
/
0
7
11
/
3
0
/
0
7
02
/
2
9
/
0
8
05
/
3
1
/
0
8
08
/
3
1
/
0
8
11
/
3
0
/
0
8
02
/
2
8
/
0
9
05
/
3
1
/
0
9
08
/
3
1
/
0
9
11
/
3
0
/
0
9
02
/
2
8
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐7 Water Level Over time (ft. blmp)
50.0
55.0
60.0
65.0
70.0
75.0
80.0
85.0
90.0
11
/
2
9
/
9
9
02
/
2
9
/
0
0
05
/
3
1
/
0
0
08
/
3
1
/
0
0
11
/
3
0
/
0
0
02
/
2
8
/
0
1
05
/
3
1
/
0
1
08
/
3
1
/
0
1
11
/
3
0
/
0
1
02
/
2
8
/
0
2
05
/
3
1
/
0
2
08
/
3
1
/
0
2
11
/
3
0
/
0
2
02
/
2
8
/
0
3
05
/
3
1
/
0
3
08
/
3
1
/
0
3
11
/
3
0
/
0
3
02
/
2
9
/
0
4
05
/
3
1
/
0
4
08
/
3
1
/
0
4
11
/
3
0
/
0
4
02
/
2
8
/
0
5
05
/
3
1
/
0
5
08
/
3
1
/
0
5
11
/
3
0
/
0
5
02
/
2
8
/
0
6
05
/
3
1
/
0
6
08
/
3
1
/
0
6
11
/
3
0
/
0
6
02
/
2
8
/
0
7
05
/
3
1
/
0
7
08
/
3
1
/
0
7
11
/
3
0
/
0
7
02
/
2
9
/
0
8
05
/
3
1
/
0
8
08
/
3
1
/
0
8
11
/
3
0
/
0
8
02
/
2
8
/
0
9
05
/
3
1
/
0
9
08
/
3
1
/
0
9
11
/
3
0
/
0
9
02
/
2
8
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐7 Water Level Over time (ft. blmp)
50.0
55.0
60.0
65.0
70.0
75.0
80.0
85.0
90.0
11
/
2
9
/
9
9
02
/
2
9
/
0
0
05
/
3
1
/
0
0
08
/
3
1
/
0
0
11
/
3
0
/
0
0
02
/
2
8
/
0
1
05
/
3
1
/
0
1
08
/
3
1
/
0
1
11
/
3
0
/
0
1
02
/
2
8
/
0
2
05
/
3
1
/
0
2
08
/
3
1
/
0
2
11
/
3
0
/
0
2
02
/
2
8
/
0
3
05
/
3
1
/
0
3
08
/
3
1
/
0
3
11
/
3
0
/
0
3
02
/
2
9
/
0
4
05
/
3
1
/
0
4
08
/
3
1
/
0
4
11
/
3
0
/
0
4
02
/
2
8
/
0
5
05
/
3
1
/
0
5
08
/
3
1
/
0
5
11
/
3
0
/
0
5
02
/
2
8
/
0
6
05
/
3
1
/
0
6
08
/
3
1
/
0
6
11
/
3
0
/
0
6
02
/
2
8
/
0
7
05
/
3
1
/
0
7
08
/
3
1
/
0
7
11
/
3
0
/
0
7
02
/
2
9
/
0
8
05
/
3
1
/
0
8
08
/
3
1
/
0
8
11
/
3
0
/
0
8
02
/
2
8
/
0
9
05
/
3
1
/
0
9
08
/
3
1
/
0
9
11
/
3
0
/
0
9
02
/
2
8
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐7 Water Level Over time (ft. blmp)
TW4‐8 Water Level Over Time (ft. blmp)
60.0
11
/
2
9
/
9
9
02
/
2
9
/
0
0
05
/
3
1
/
0
0
08
/
3
1
/
0
0
11
/
3
0
/
0
0
02
/
2
8
/
0
1
05
/
3
1
/
0
1
08
/
3
1
/
0
1
11
/
3
0
/
0
1
02
/
2
8
/
0
2
05
/
3
1
/
0
2
08
/
3
1
/
0
2
11
/
3
0
/
0
2
02
/
2
8
/
0
3
05
/
3
1
/
0
3
08
/
3
1
/
0
3
11
/
3
0
/
0
3
02
/
2
9
/
0
4
05
/
3
1
/
0
4
08
/
3
1
/
0
4
11
/
3
0
/
0
4
02
/
2
8
/
0
5
05
/
3
1
/
0
5
08
/
3
1
/
0
5
11
/
3
0
/
0
5
02
/
2
8
/
0
6
05
/
3
1
/
0
6
08
/
3
1
/
0
6
11
/
3
0
/
0
6
02
/
2
8
/
0
7
05
/
3
1
/
0
7
08
/
3
1
/
0
7
11
/
3
0
/
0
7
02
/
2
9
/
0
8
05
/
3
1
/
0
8
08
/
3
1
/
0
8
11
/
3
0
/
0
8
02
/
2
8
/
0
9
05
/
3
1
/
0
9
08
/
3
1
/
0
9
11
/
3
0
/
0
9
02
/
2
8
/
1
0
TW4‐8 Water Level Over Time (ft. blmp)
60.0
62.0
64.0
66.0
11
/
2
9
/
9
9
02
/
2
9
/
0
0
05
/
3
1
/
0
0
08
/
3
1
/
0
0
11
/
3
0
/
0
0
02
/
2
8
/
0
1
05
/
3
1
/
0
1
08
/
3
1
/
0
1
11
/
3
0
/
0
1
02
/
2
8
/
0
2
05
/
3
1
/
0
2
08
/
3
1
/
0
2
11
/
3
0
/
0
2
02
/
2
8
/
0
3
05
/
3
1
/
0
3
08
/
3
1
/
0
3
11
/
3
0
/
0
3
02
/
2
9
/
0
4
05
/
3
1
/
0
4
08
/
3
1
/
0
4
11
/
3
0
/
0
4
02
/
2
8
/
0
5
05
/
3
1
/
0
5
08
/
3
1
/
0
5
11
/
3
0
/
0
5
02
/
2
8
/
0
6
05
/
3
1
/
0
6
08
/
3
1
/
0
6
11
/
3
0
/
0
6
02
/
2
8
/
0
7
05
/
3
1
/
0
7
08
/
3
1
/
0
7
11
/
3
0
/
0
7
02
/
2
9
/
0
8
05
/
3
1
/
0
8
08
/
3
1
/
0
8
11
/
3
0
/
0
8
02
/
2
8
/
0
9
05
/
3
1
/
0
9
08
/
3
1
/
0
9
11
/
3
0
/
0
9
02
/
2
8
/
1
0
nt (f
t
.
)
TW4‐8 Water Level Over Time (ft. blmp)
60.0
62.0
64.0
66.0
68.0
70.0
11
/
2
9
/
9
9
02
/
2
9
/
0
0
05
/
3
1
/
0
0
08
/
3
1
/
0
0
11
/
3
0
/
0
0
02
/
2
8
/
0
1
05
/
3
1
/
0
1
08
/
3
1
/
0
1
11
/
3
0
/
0
1
02
/
2
8
/
0
2
05
/
3
1
/
0
2
08
/
3
1
/
0
2
11
/
3
0
/
0
2
02
/
2
8
/
0
3
05
/
3
1
/
0
3
08
/
3
1
/
0
3
11
/
3
0
/
0
3
02
/
2
9
/
0
4
05
/
3
1
/
0
4
08
/
3
1
/
0
4
11
/
3
0
/
0
4
02
/
2
8
/
0
5
05
/
3
1
/
0
5
08
/
3
1
/
0
5
11
/
3
0
/
0
5
02
/
2
8
/
0
6
05
/
3
1
/
0
6
08
/
3
1
/
0
6
11
/
3
0
/
0
6
02
/
2
8
/
0
7
05
/
3
1
/
0
7
08
/
3
1
/
0
7
11
/
3
0
/
0
7
02
/
2
9
/
0
8
05
/
3
1
/
0
8
08
/
3
1
/
0
8
11
/
3
0
/
0
8
02
/
2
8
/
0
9
05
/
3
1
/
0
9
08
/
3
1
/
0
9
11
/
3
0
/
0
9
02
/
2
8
/
1
0
Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐8 Water Level Over Time (ft. blmp)
60.0
62.0
64.0
66.0
68.0
70.0
72.0
74.0
76.0
11
/
2
9
/
9
9
02
/
2
9
/
0
0
05
/
3
1
/
0
0
08
/
3
1
/
0
0
11
/
3
0
/
0
0
02
/
2
8
/
0
1
05
/
3
1
/
0
1
08
/
3
1
/
0
1
11
/
3
0
/
0
1
02
/
2
8
/
0
2
05
/
3
1
/
0
2
08
/
3
1
/
0
2
11
/
3
0
/
0
2
02
/
2
8
/
0
3
05
/
3
1
/
0
3
08
/
3
1
/
0
3
11
/
3
0
/
0
3
02
/
2
9
/
0
4
05
/
3
1
/
0
4
08
/
3
1
/
0
4
11
/
3
0
/
0
4
02
/
2
8
/
0
5
05
/
3
1
/
0
5
08
/
3
1
/
0
5
11
/
3
0
/
0
5
02
/
2
8
/
0
6
05
/
3
1
/
0
6
08
/
3
1
/
0
6
11
/
3
0
/
0
6
02
/
2
8
/
0
7
05
/
3
1
/
0
7
08
/
3
1
/
0
7
11
/
3
0
/
0
7
02
/
2
9
/
0
8
05
/
3
1
/
0
8
08
/
3
1
/
0
8
11
/
3
0
/
0
8
02
/
2
8
/
0
9
05
/
3
1
/
0
9
08
/
3
1
/
0
9
11
/
3
0
/
0
9
02
/
2
8
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐8 Water Level Over Time (ft. blmp)
60.0
62.0
64.0
66.0
68.0
70.0
72.0
74.0
76.0
78.0
80.0
11
/
2
9
/
9
9
02
/
2
9
/
0
0
05
/
3
1
/
0
0
08
/
3
1
/
0
0
11
/
3
0
/
0
0
02
/
2
8
/
0
1
05
/
3
1
/
0
1
08
/
3
1
/
0
1
11
/
3
0
/
0
1
02
/
2
8
/
0
2
05
/
3
1
/
0
2
08
/
3
1
/
0
2
11
/
3
0
/
0
2
02
/
2
8
/
0
3
05
/
3
1
/
0
3
08
/
3
1
/
0
3
11
/
3
0
/
0
3
02
/
2
9
/
0
4
05
/
3
1
/
0
4
08
/
3
1
/
0
4
11
/
3
0
/
0
4
02
/
2
8
/
0
5
05
/
3
1
/
0
5
08
/
3
1
/
0
5
11
/
3
0
/
0
5
02
/
2
8
/
0
6
05
/
3
1
/
0
6
08
/
3
1
/
0
6
11
/
3
0
/
0
6
02
/
2
8
/
0
7
05
/
3
1
/
0
7
08
/
3
1
/
0
7
11
/
3
0
/
0
7
02
/
2
9
/
0
8
05
/
3
1
/
0
8
08
/
3
1
/
0
8
11
/
3
0
/
0
8
02
/
2
8
/
0
9
05
/
3
1
/
0
9
08
/
3
1
/
0
9
11
/
3
0
/
0
9
02
/
2
8
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐8 Water Level Over Time (ft. blmp)
60.0
62.0
64.0
66.0
68.0
70.0
72.0
74.0
76.0
78.0
80.0
11
/
2
9
/
9
9
02
/
2
9
/
0
0
05
/
3
1
/
0
0
08
/
3
1
/
0
0
11
/
3
0
/
0
0
02
/
2
8
/
0
1
05
/
3
1
/
0
1
08
/
3
1
/
0
1
11
/
3
0
/
0
1
02
/
2
8
/
0
2
05
/
3
1
/
0
2
08
/
3
1
/
0
2
11
/
3
0
/
0
2
02
/
2
8
/
0
3
05
/
3
1
/
0
3
08
/
3
1
/
0
3
11
/
3
0
/
0
3
02
/
2
9
/
0
4
05
/
3
1
/
0
4
08
/
3
1
/
0
4
11
/
3
0
/
0
4
02
/
2
8
/
0
5
05
/
3
1
/
0
5
08
/
3
1
/
0
5
11
/
3
0
/
0
5
02
/
2
8
/
0
6
05
/
3
1
/
0
6
08
/
3
1
/
0
6
11
/
3
0
/
0
6
02
/
2
8
/
0
7
05
/
3
1
/
0
7
08
/
3
1
/
0
7
11
/
3
0
/
0
7
02
/
2
9
/
0
8
05
/
3
1
/
0
8
08
/
3
1
/
0
8
11
/
3
0
/
0
8
02
/
2
8
/
0
9
05
/
3
1
/
0
9
08
/
3
1
/
0
9
11
/
3
0
/
0
9
02
/
2
8
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐8 Water Level Over Time (ft. blmp)
0/9
9
0/0
0
0/0
0
0/0
1
0/0
1
0/0
2
0/0
2
0/0
3
0/0
3
0/0
4
0/0
4
0/0
5
0/0
5
0/0
6
0/0
6
0/0
7
0/0
7
0/0
8
0/0
8
0/0
9
0/0
9
TW4‐9 Water Level Over Time (ft. blmp)
50.0
52.0
12
/
2
0
/
9
9
06
/
2
0
/
0
0
12
/
2
0
/
0
0
06
/
2
0
/
0
1
12
/
2
0
/
0
1
06
/
2
0
/
0
2
12
/
2
0
/
0
2
06
/
2
0
/
0
3
12
/
2
0
/
0
3
06
/
2
0
/
0
4
12
/
2
0
/
0
4
06
/
2
0
/
0
5
12
/
2
0
/
0
5
06
/
2
0
/
0
6
12
/
2
0
/
0
6
06
/
2
0
/
0
7
12
/
2
0
/
0
7
06
/
2
0
/
0
8
12
/
2
0
/
0
8
06
/
2
0
/
0
9
12
/
2
0
/
0
9
TW4‐9 Water Level Over Time (ft. blmp)
50.0
52.0
54.0
56.0
12
/
2
0
/
9
9
06
/
2
0
/
0
0
12
/
2
0
/
0
0
06
/
2
0
/
0
1
12
/
2
0
/
0
1
06
/
2
0
/
0
2
12
/
2
0
/
0
2
06
/
2
0
/
0
3
12
/
2
0
/
0
3
06
/
2
0
/
0
4
12
/
2
0
/
0
4
06
/
2
0
/
0
5
12
/
2
0
/
0
5
06
/
2
0
/
0
6
12
/
2
0
/
0
6
06
/
2
0
/
0
7
12
/
2
0
/
0
7
06
/
2
0
/
0
8
12
/
2
0
/
0
8
06
/
2
0
/
0
9
12
/
2
0
/
0
9
nt (f
t
.
)
TW4‐9 Water Level Over Time (ft. blmp)
50.0
52.0
54.0
56.0
58.0
60.0
12
/
2
0
/
9
9
06
/
2
0
/
0
0
12
/
2
0
/
0
0
06
/
2
0
/
0
1
12
/
2
0
/
0
1
06
/
2
0
/
0
2
12
/
2
0
/
0
2
06
/
2
0
/
0
3
12
/
2
0
/
0
3
06
/
2
0
/
0
4
12
/
2
0
/
0
4
06
/
2
0
/
0
5
12
/
2
0
/
0
5
06
/
2
0
/
0
6
12
/
2
0
/
0
6
06
/
2
0
/
0
7
12
/
2
0
/
0
7
06
/
2
0
/
0
8
12
/
2
0
/
0
8
06
/
2
0
/
0
9
12
/
2
0
/
0
9
ow Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐9 Water Level Over Time (ft. blmp)
50.0
52.0
54.0
56.0
58.0
60.0
62.0
64.0
66 0
12
/
2
0
/
9
9
06
/
2
0
/
0
0
12
/
2
0
/
0
0
06
/
2
0
/
0
1
12
/
2
0
/
0
1
06
/
2
0
/
0
2
12
/
2
0
/
0
2
06
/
2
0
/
0
3
12
/
2
0
/
0
3
06
/
2
0
/
0
4
12
/
2
0
/
0
4
06
/
2
0
/
0
5
12
/
2
0
/
0
5
06
/
2
0
/
0
6
12
/
2
0
/
0
6
06
/
2
0
/
0
7
12
/
2
0
/
0
7
06
/
2
0
/
0
8
12
/
2
0
/
0
8
06
/
2
0
/
0
9
12
/
2
0
/
0
9
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐9 Water Level Over Time (ft. blmp)
50.0
52.0
54.0
56.0
58.0
60.0
62.0
64.0
66.0
68.0
70.0
12
/
2
0
/
9
9
06
/
2
0
/
0
0
12
/
2
0
/
0
0
06
/
2
0
/
0
1
12
/
2
0
/
0
1
06
/
2
0
/
0
2
12
/
2
0
/
0
2
06
/
2
0
/
0
3
12
/
2
0
/
0
3
06
/
2
0
/
0
4
12
/
2
0
/
0
4
06
/
2
0
/
0
5
12
/
2
0
/
0
5
06
/
2
0
/
0
6
12
/
2
0
/
0
6
06
/
2
0
/
0
7
12
/
2
0
/
0
7
06
/
2
0
/
0
8
12
/
2
0
/
0
8
06
/
2
0
/
0
9
12
/
2
0
/
0
9
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐9 Water Level Over Time (ft. blmp)
50.0
52.0
54.0
56.0
58.0
60.0
62.0
64.0
66.0
68.0
70.0
12
/
2
0
/
9
9
06
/
2
0
/
0
0
12
/
2
0
/
0
0
06
/
2
0
/
0
1
12
/
2
0
/
0
1
06
/
2
0
/
0
2
12
/
2
0
/
0
2
06
/
2
0
/
0
3
12
/
2
0
/
0
3
06
/
2
0
/
0
4
12
/
2
0
/
0
4
06
/
2
0
/
0
5
12
/
2
0
/
0
5
06
/
2
0
/
0
6
12
/
2
0
/
0
6
06
/
2
0
/
0
7
12
/
2
0
/
0
7
06
/
2
0
/
0
8
12
/
2
0
/
0
8
06
/
2
0
/
0
9
12
/
2
0
/
0
9
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐9 Water Level Over Time (ft. blmp)
2 2 2 3 3 3 4 4 4 5 5 5 6 6 6 7 7 7 8 8 8 9 9 9 0
TW4‐10 Water Level Over Time (ft. blmp)
52.00
53 00
Ja
n
‐02
Ap
r
‐02
Ju
l
‐02
Oc
t
‐02
Ja
n
‐03
Ap
r
‐03
Ju
l
‐03
Oc
t
‐03
Ja
n
‐04
Ap
r
‐04
Ju
l
‐04
Oc
t
‐04
Ja
n
‐05
Ap
r
‐05
Ju
l
‐05
Oc
t
‐05
Ja
n
‐06
Ap
r
‐06
Ju
l
‐06
Oc
t
‐06
Ja
n
‐07
Ap
r
‐07
Ju
l
‐07
Oc
t
‐07
Ja
n
‐08
Ap
r
‐08
Ju
l
‐08
Oc
t
‐08
Ja
n
‐09
Ap
r
‐09
Ju
l
‐09
Oc
t
‐09
Ja
n
‐10
TW4‐10 Water Level Over Time (ft. blmp)
52.00
53.00
54.00
55 00
Ja
n
‐02
Ap
r
‐02
Ju
l
‐02
Oc
t
‐02
Ja
n
‐03
Ap
r
‐03
Ju
l
‐03
Oc
t
‐03
Ja
n
‐04
Ap
r
‐04
Ju
l
‐04
Oc
t
‐04
Ja
n
‐05
Ap
r
‐05
Ju
l
‐05
Oc
t
‐05
Ja
n
‐06
Ap
r
‐06
Ju
l
‐06
Oc
t
‐06
Ja
n
‐07
Ap
r
‐07
Ju
l
‐07
Oc
t
‐07
Ja
n
‐08
Ap
r
‐08
Ju
l
‐08
Oc
t
‐08
Ja
n
‐09
Ap
r
‐09
Ju
l
‐09
Oc
t
‐09
Ja
n
‐10
oin
t
 (f
t
.
)
TW4‐10 Water Level Over Time (ft. blmp)
52.00
53.00
54.00
55.00
56.00
Ja
n
‐02
Ap
r
‐02
Ju
l
‐02
Oc
t
‐02
Ja
n
‐03
Ap
r
‐03
Ju
l
‐03
Oc
t
‐03
Ja
n
‐04
Ap
r
‐04
Ju
l
‐04
Oc
t
‐04
Ja
n
‐05
Ap
r
‐05
Ju
l
‐05
Oc
t
‐05
Ja
n
‐06
Ap
r
‐06
Ju
l
‐06
Oc
t
‐06
Ja
n
‐07
Ap
r
‐07
Ju
l
‐07
Oc
t
‐07
Ja
n
‐08
Ap
r
‐08
Ju
l
‐08
Oc
t
‐08
Ja
n
‐09
Ap
r
‐09
Ju
l
‐09
Oc
t
‐09
Ja
n
‐10
w Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐10 Water Level Over Time (ft. blmp)
52.00
53.00
54.00
55.00
56.00
57.00
58.00
Ja
n
‐02
Ap
r
‐02
Ju
l
‐02
Oc
t
‐02
Ja
n
‐03
Ap
r
‐03
Ju
l
‐03
Oc
t
‐03
Ja
n
‐04
Ap
r
‐04
Ju
l
‐04
Oc
t
‐04
Ja
n
‐05
Ap
r
‐05
Ju
l
‐05
Oc
t
‐05
Ja
n
‐06
Ap
r
‐06
Ju
l
‐06
Oc
t
‐06
Ja
n
‐07
Ap
r
‐07
Ju
l
‐07
Oc
t
‐07
Ja
n
‐08
Ap
r
‐08
Ju
l
‐08
Oc
t
‐08
Ja
n
‐09
Ap
r
‐09
Ju
l
‐09
Oc
t
‐09
Ja
n
‐10
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐10 Water Level Over Time (ft. blmp)
52.00
53.00
54.00
55.00
56.00
57.00
58.00
59.00
60.00
Ja
n
‐02
Ap
r
‐02
Ju
l
‐02
Oc
t
‐02
Ja
n
‐03
Ap
r
‐03
Ju
l
‐03
Oc
t
‐03
Ja
n
‐04
Ap
r
‐04
Ju
l
‐04
Oc
t
‐04
Ja
n
‐05
Ap
r
‐05
Ju
l
‐05
Oc
t
‐05
Ja
n
‐06
Ap
r
‐06
Ju
l
‐06
Oc
t
‐06
Ja
n
‐07
Ap
r
‐07
Ju
l
‐07
Oc
t
‐07
Ja
n
‐08
Ap
r
‐08
Ju
l
‐08
Oc
t
‐08
Ja
n
‐09
Ap
r
‐09
Ju
l
‐09
Oc
t
‐09
Ja
n
‐10
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐10 Water Level Over Time (ft. blmp)
52.00
53.00
54.00
55.00
56.00
57.00
58.00
59.00
60.00
Ja
n
‐02
Ap
r
‐02
Ju
l
‐02
Oc
t
‐02
Ja
n
‐03
Ap
r
‐03
Ju
l
‐03
Oc
t
‐03
Ja
n
‐04
Ap
r
‐04
Ju
l
‐04
Oc
t
‐04
Ja
n
‐05
Ap
r
‐05
Ju
l
‐05
Oc
t
‐05
Ja
n
‐06
Ap
r
‐06
Ju
l
‐06
Oc
t
‐06
Ja
n
‐07
Ap
r
‐07
Ju
l
‐07
Oc
t
‐07
Ja
n
‐08
Ap
r
‐08
Ju
l
‐08
Oc
t
‐08
Ja
n
‐09
Ap
r
‐09
Ju
l
‐09
Oc
t
‐09
Ja
n
‐10
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐10 Water Level Over Time (ft. blmp)
50.0
55.0
60.0
65.0
01
/
0
3
/
0
2
04
/
0
3
/
0
2
07
/
0
3
/
0
2
10
/
0
3
/
0
2
01
/
0
3
/
0
3
04
/
0
3
/
0
3
07
/
0
3
/
0
3
10
/
0
3
/
0
3
01
/
0
3
/
0
4
04
/
0
3
/
0
4
07
/
0
3
/
0
4
10
/
0
3
/
0
4
01
/
0
3
/
0
5
04
/
0
3
/
0
5
07
/
0
3
/
0
5
10
/
0
3
/
0
5
01
/
0
3
/
0
6
04
/
0
3
/
0
6
07
/
0
3
/
0
6
10
/
0
3
/
0
6
01
/
0
3
/
0
7
04
/
0
3
/
0
7
07
/
0
3
/
0
7
10
/
0
3
/
0
7
01
/
0
3
/
0
8
04
/
0
3
/
0
8
07
/
0
3
/
0
8
10
/
0
3
/
0
8
01
/
0
3
/
0
9
04
/
0
3
/
0
9
07
/
0
3
/
0
9
10
/
0
3
/
0
9
01
/
0
3
/
1
0
Mea
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐11 Water Level Over Time (ft. blmp)
50.0
55.0
60.0
65.0
70.0
75.0
80.0
01
/
0
3
/
0
2
04
/
0
3
/
0
2
07
/
0
3
/
0
2
10
/
0
3
/
0
2
01
/
0
3
/
0
3
04
/
0
3
/
0
3
07
/
0
3
/
0
3
10
/
0
3
/
0
3
01
/
0
3
/
0
4
04
/
0
3
/
0
4
07
/
0
3
/
0
4
10
/
0
3
/
0
4
01
/
0
3
/
0
5
04
/
0
3
/
0
5
07
/
0
3
/
0
5
10
/
0
3
/
0
5
01
/
0
3
/
0
6
04
/
0
3
/
0
6
07
/
0
3
/
0
6
10
/
0
3
/
0
6
01
/
0
3
/
0
7
04
/
0
3
/
0
7
07
/
0
3
/
0
7
10
/
0
3
/
0
7
01
/
0
3
/
0
8
04
/
0
3
/
0
8
07
/
0
3
/
0
8
10
/
0
3
/
0
8
01
/
0
3
/
0
9
04
/
0
3
/
0
9
07
/
0
3
/
0
9
10
/
0
3
/
0
9
01
/
0
3
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐11 Water Level Over Time (ft. blmp)
30.0
32.0
34.0
36.0
38.0
8/
2
3
/
2
0
0
2
11
/
2
3
/
2
0
0
2
2/
2
3
/
2
0
0
3
5/
2
3
/
2
0
0
3
8/
2
3
/
2
0
0
3
11
/
2
3
/
2
0
0
3
2/
2
3
/
2
0
0
4
5/
2
3
/
2
0
0
4
8/
2
3
/
2
0
0
4
11
/
2
3
/
2
0
0
4
2/
2
3
/
2
0
0
5
5/
2
3
/
2
0
0
5
8/
2
3
/
2
0
0
5
11
/
2
3
/
2
0
0
5
2/
2
3
/
2
0
0
6
5/
2
3
/
2
0
0
6
8/
2
3
/
2
0
0
6
11
/
2
3
/
2
0
0
6
2/
2
3
/
2
0
0
7
5/
2
3
/
2
0
0
7
8/
2
3
/
2
0
0
7
11
/
2
3
/
2
0
0
7
2/
2
3
/
2
0
0
8
5/
2
3
/
2
0
0
8
8/
2
3
/
2
0
0
8
11
/
2
3
/
2
0
0
8
2/
2
3
/
2
0
0
9
5/
2
3
/
2
0
0
9
8/
2
3
/
2
0
0
9
11
/
2
3
/
2
0
0
9
2/
2
3
/
2
0
1
0
Mea
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐12 Water Level Over Time (ft. blmp)
30.0
32.0
34.0
36.0
38.0
40.0
42.0
44.0
46.0
8/
2
3
/
2
0
0
2
11
/
2
3
/
2
0
0
2
2/
2
3
/
2
0
0
3
5/
2
3
/
2
0
0
3
8/
2
3
/
2
0
0
3
11
/
2
3
/
2
0
0
3
2/
2
3
/
2
0
0
4
5/
2
3
/
2
0
0
4
8/
2
3
/
2
0
0
4
11
/
2
3
/
2
0
0
4
2/
2
3
/
2
0
0
5
5/
2
3
/
2
0
0
5
8/
2
3
/
2
0
0
5
11
/
2
3
/
2
0
0
5
2/
2
3
/
2
0
0
6
5/
2
3
/
2
0
0
6
8/
2
3
/
2
0
0
6
11
/
2
3
/
2
0
0
6
2/
2
3
/
2
0
0
7
5/
2
3
/
2
0
0
7
8/
2
3
/
2
0
0
7
11
/
2
3
/
2
0
0
7
2/
2
3
/
2
0
0
8
5/
2
3
/
2
0
0
8
8/
2
3
/
2
0
0
8
11
/
2
3
/
2
0
0
8
2/
2
3
/
2
0
0
9
5/
2
3
/
2
0
0
9
8/
2
3
/
2
0
0
9
11
/
2
3
/
2
0
0
9
2/
2
3
/
2
0
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐12 Water Level Over Time (ft. blmp)
TW4‐13 Water Level Over Time (ft.blmp)
40.0
08
/
2
3
/
0
2
11
/
2
3
/
0
2
02
/
2
3
/
0
3
05
/
2
3
/
0
3
08
/
2
3
/
0
3
11
/
2
3
/
0
3
02
/
2
3
/
0
4
05
/
2
3
/
0
4
08
/
2
3
/
0
4
11
/
2
3
/
0
4
02
/
2
3
/
0
5
05
/
2
3
/
0
5
08
/
2
3
/
0
5
11
/
2
3
/
0
5
02
/
2
3
/
0
6
05
/
2
3
/
0
6
08
/
2
3
/
0
6
11
/
2
3
/
0
6
02
/
2
3
/
0
7
05
/
2
3
/
0
7
08
/
2
3
/
0
7
11
/
2
3
/
0
7
02
/
2
3
/
0
8
05
/
2
3
/
0
8
08
/
2
3
/
0
8
11
/
2
3
/
0
8
02
/
2
3
/
0
9
05
/
2
3
/
0
9
08
/
2
3
/
0
9
11
/
2
3
/
0
9
02
/
2
3
/
1
0
TW4‐13 Water Level Over Time (ft. blmp)
40.0
50.0
60 0
08
/
2
3
/
0
2
11
/
2
3
/
0
2
02
/
2
3
/
0
3
05
/
2
3
/
0
3
08
/
2
3
/
0
3
11
/
2
3
/
0
3
02
/
2
3
/
0
4
05
/
2
3
/
0
4
08
/
2
3
/
0
4
11
/
2
3
/
0
4
02
/
2
3
/
0
5
05
/
2
3
/
0
5
08
/
2
3
/
0
5
11
/
2
3
/
0
5
02
/
2
3
/
0
6
05
/
2
3
/
0
6
08
/
2
3
/
0
6
11
/
2
3
/
0
6
02
/
2
3
/
0
7
05
/
2
3
/
0
7
08
/
2
3
/
0
7
11
/
2
3
/
0
7
02
/
2
3
/
0
8
05
/
2
3
/
0
8
08
/
2
3
/
0
8
11
/
2
3
/
0
8
02
/
2
3
/
0
9
05
/
2
3
/
0
9
08
/
2
3
/
0
9
11
/
2
3
/
0
9
02
/
2
3
/
1
0
nt (f
t
.
)
TW4‐13 Water Level Over Time (ft. blmp)
40.0
50.0
60.0
70.0
08
/
2
3
/
0
2
11
/
2
3
/
0
2
02
/
2
3
/
0
3
05
/
2
3
/
0
3
08
/
2
3
/
0
3
11
/
2
3
/
0
3
02
/
2
3
/
0
4
05
/
2
3
/
0
4
08
/
2
3
/
0
4
11
/
2
3
/
0
4
02
/
2
3
/
0
5
05
/
2
3
/
0
5
08
/
2
3
/
0
5
11
/
2
3
/
0
5
02
/
2
3
/
0
6
05
/
2
3
/
0
6
08
/
2
3
/
0
6
11
/
2
3
/
0
6
02
/
2
3
/
0
7
05
/
2
3
/
0
7
08
/
2
3
/
0
7
11
/
2
3
/
0
7
02
/
2
3
/
0
8
05
/
2
3
/
0
8
08
/
2
3
/
0
8
11
/
2
3
/
0
8
02
/
2
3
/
0
9
05
/
2
3
/
0
9
08
/
2
3
/
0
9
11
/
2
3
/
0
9
02
/
2
3
/
1
0
w Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐13 Water Level Over Time (ft. blmp)
40.0
50.0
60.0
70.0
80.0
90.0
08
/
2
3
/
0
2
11
/
2
3
/
0
2
02
/
2
3
/
0
3
05
/
2
3
/
0
3
08
/
2
3
/
0
3
11
/
2
3
/
0
3
02
/
2
3
/
0
4
05
/
2
3
/
0
4
08
/
2
3
/
0
4
11
/
2
3
/
0
4
02
/
2
3
/
0
5
05
/
2
3
/
0
5
08
/
2
3
/
0
5
11
/
2
3
/
0
5
02
/
2
3
/
0
6
05
/
2
3
/
0
6
08
/
2
3
/
0
6
11
/
2
3
/
0
6
02
/
2
3
/
0
7
05
/
2
3
/
0
7
08
/
2
3
/
0
7
11
/
2
3
/
0
7
02
/
2
3
/
0
8
05
/
2
3
/
0
8
08
/
2
3
/
0
8
11
/
2
3
/
0
8
02
/
2
3
/
0
9
05
/
2
3
/
0
9
08
/
2
3
/
0
9
11
/
2
3
/
0
9
02
/
2
3
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐13 Water Level Over Time (ft. blmp)
40.0
50.0
60.0
70.0
80.0
90.0
100.0
08
/
2
3
/
0
2
11
/
2
3
/
0
2
02
/
2
3
/
0
3
05
/
2
3
/
0
3
08
/
2
3
/
0
3
11
/
2
3
/
0
3
02
/
2
3
/
0
4
05
/
2
3
/
0
4
08
/
2
3
/
0
4
11
/
2
3
/
0
4
02
/
2
3
/
0
5
05
/
2
3
/
0
5
08
/
2
3
/
0
5
11
/
2
3
/
0
5
02
/
2
3
/
0
6
05
/
2
3
/
0
6
08
/
2
3
/
0
6
11
/
2
3
/
0
6
02
/
2
3
/
0
7
05
/
2
3
/
0
7
08
/
2
3
/
0
7
11
/
2
3
/
0
7
02
/
2
3
/
0
8
05
/
2
3
/
0
8
08
/
2
3
/
0
8
11
/
2
3
/
0
8
02
/
2
3
/
0
9
05
/
2
3
/
0
9
08
/
2
3
/
0
9
11
/
2
3
/
0
9
02
/
2
3
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐13 Water Level Over Time (ft. blmp)
40.0
50.0
60.0
70.0
80.0
90.0
100.0
08
/
2
3
/
0
2
11
/
2
3
/
0
2
02
/
2
3
/
0
3
05
/
2
3
/
0
3
08
/
2
3
/
0
3
11
/
2
3
/
0
3
02
/
2
3
/
0
4
05
/
2
3
/
0
4
08
/
2
3
/
0
4
11
/
2
3
/
0
4
02
/
2
3
/
0
5
05
/
2
3
/
0
5
08
/
2
3
/
0
5
11
/
2
3
/
0
5
02
/
2
3
/
0
6
05
/
2
3
/
0
6
08
/
2
3
/
0
6
11
/
2
3
/
0
6
02
/
2
3
/
0
7
05
/
2
3
/
0
7
08
/
2
3
/
0
7
11
/
2
3
/
0
7
02
/
2
3
/
0
8
05
/
2
3
/
0
8
08
/
2
3
/
0
8
11
/
2
3
/
0
8
02
/
2
3
/
0
9
05
/
2
3
/
0
9
08
/
2
3
/
0
9
11
/
2
3
/
0
9
02
/
2
3
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐13 Water Level Over Time (ft. blmp)
86.0
87.0
88.0
89.0
90.0
08
/
2
3
/
0
2
11
/
2
3
/
0
2
02
/
2
3
/
0
3
05
/
2
3
/
0
3
08
/
2
3
/
0
3
11
/
2
3
/
0
3
02
/
2
3
/
0
4
05
/
2
3
/
0
4
08
/
2
3
/
0
4
11
/
2
3
/
0
4
02
/
2
3
/
0
5
05
/
2
3
/
0
5
08
/
2
3
/
0
5
11
/
2
3
/
0
5
02
/
2
3
/
0
6
05
/
2
3
/
0
6
08
/
2
3
/
0
6
11
/
2
3
/
0
6
02
/
2
3
/
0
7
05
/
2
3
/
0
7
08
/
2
3
/
0
7
11
/
2
3
/
0
7
02
/
2
3
/
0
8
05
/
2
3
/
0
8
08
/
2
3
/
0
8
11
/
2
3
/
0
8
02
/
2
3
/
0
9
05
/
2
3
/
0
9
08
/
2
3
/
0
9
11
/
2
3
/
0
9
02
/
2
3
/
1
0
sur
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐14 Water Level Over Time (ft. blmp)
86.0
87.0
88.0
89.0
90.0
91.0
92.0
93.0
94.0
95.0
96.0
08
/
2
3
/
0
2
11
/
2
3
/
0
2
02
/
2
3
/
0
3
05
/
2
3
/
0
3
08
/
2
3
/
0
3
11
/
2
3
/
0
3
02
/
2
3
/
0
4
05
/
2
3
/
0
4
08
/
2
3
/
0
4
11
/
2
3
/
0
4
02
/
2
3
/
0
5
05
/
2
3
/
0
5
08
/
2
3
/
0
5
11
/
2
3
/
0
5
02
/
2
3
/
0
6
05
/
2
3
/
0
6
08
/
2
3
/
0
6
11
/
2
3
/
0
6
02
/
2
3
/
0
7
05
/
2
3
/
0
7
08
/
2
3
/
0
7
11
/
2
3
/
0
7
02
/
2
3
/
0
8
05
/
2
3
/
0
8
08
/
2
3
/
0
8
11
/
2
3
/
0
8
02
/
2
3
/
0
9
05
/
2
3
/
0
9
08
/
2
3
/
0
9
11
/
2
3
/
0
9
02
/
2
3
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐14 Water Level Over Time (ft. blmp)
TW4‐15 Water Level Over Time (ft. blmp)
40
08
/
2
3
/
0
2
11
/
2
3
/
0
2
02
/
2
3
/
0
3
05
/
2
3
/
0
3
08
/
2
3
/
0
3
11
/
2
3
/
0
3
02
/
2
3
/
0
4
05
/
2
3
/
0
4
08
/
2
3
/
0
4
11
/
2
3
/
0
4
02
/
2
3
/
0
5
05
/
2
3
/
0
5
08
/
2
3
/
0
5
11
/
2
3
/
0
5
02
/
2
3
/
0
6
05
/
2
3
/
0
6
08
/
2
3
/
0
6
11
/
2
3
/
0
6
02
/
2
3
/
0
7
05
/
2
3
/
0
7
08
/
2
3
/
0
7
11
/
2
3
/
0
7
02
/
2
3
/
0
8
05
/
2
3
/
0
8
08
/
2
3
/
0
8
11
/
2
3
/
0
8
02
/
2
3
/
0
9
05
/
2
3
/
0
9
08
/
2
3
/
0
9
11
/
2
3
/
0
9
02
/
2
3
/
1
0
TW4‐15 Water Level Over Time (ft. blmp)
40
50
60
08
/
2
3
/
0
2
11
/
2
3
/
0
2
02
/
2
3
/
0
3
05
/
2
3
/
0
3
08
/
2
3
/
0
3
11
/
2
3
/
0
3
02
/
2
3
/
0
4
05
/
2
3
/
0
4
08
/
2
3
/
0
4
11
/
2
3
/
0
4
02
/
2
3
/
0
5
05
/
2
3
/
0
5
08
/
2
3
/
0
5
11
/
2
3
/
0
5
02
/
2
3
/
0
6
05
/
2
3
/
0
6
08
/
2
3
/
0
6
11
/
2
3
/
0
6
02
/
2
3
/
0
7
05
/
2
3
/
0
7
08
/
2
3
/
0
7
11
/
2
3
/
0
7
02
/
2
3
/
0
8
05
/
2
3
/
0
8
08
/
2
3
/
0
8
11
/
2
3
/
0
8
02
/
2
3
/
0
9
05
/
2
3
/
0
9
08
/
2
3
/
0
9
11
/
2
3
/
0
9
02
/
2
3
/
1
0
nt (f
t
.
)
TW4‐15 Water Level Over Time (ft. blmp)
40
50
60
70
80
08
/
2
3
/
0
2
11
/
2
3
/
0
2
02
/
2
3
/
0
3
05
/
2
3
/
0
3
08
/
2
3
/
0
3
11
/
2
3
/
0
3
02
/
2
3
/
0
4
05
/
2
3
/
0
4
08
/
2
3
/
0
4
11
/
2
3
/
0
4
02
/
2
3
/
0
5
05
/
2
3
/
0
5
08
/
2
3
/
0
5
11
/
2
3
/
0
5
02
/
2
3
/
0
6
05
/
2
3
/
0
6
08
/
2
3
/
0
6
11
/
2
3
/
0
6
02
/
2
3
/
0
7
05
/
2
3
/
0
7
08
/
2
3
/
0
7
11
/
2
3
/
0
7
02
/
2
3
/
0
8
05
/
2
3
/
0
8
08
/
2
3
/
0
8
11
/
2
3
/
0
8
02
/
2
3
/
0
9
05
/
2
3
/
0
9
08
/
2
3
/
0
9
11
/
2
3
/
0
9
02
/
2
3
/
1
0
w Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐15 Water Level Over Time (ft. blmp)
40
50
60
70
80
90
100
08
/
2
3
/
0
2
11
/
2
3
/
0
2
02
/
2
3
/
0
3
05
/
2
3
/
0
3
08
/
2
3
/
0
3
11
/
2
3
/
0
3
02
/
2
3
/
0
4
05
/
2
3
/
0
4
08
/
2
3
/
0
4
11
/
2
3
/
0
4
02
/
2
3
/
0
5
05
/
2
3
/
0
5
08
/
2
3
/
0
5
11
/
2
3
/
0
5
02
/
2
3
/
0
6
05
/
2
3
/
0
6
08
/
2
3
/
0
6
11
/
2
3
/
0
6
02
/
2
3
/
0
7
05
/
2
3
/
0
7
08
/
2
3
/
0
7
11
/
2
3
/
0
7
02
/
2
3
/
0
8
05
/
2
3
/
0
8
08
/
2
3
/
0
8
11
/
2
3
/
0
8
02
/
2
3
/
0
9
05
/
2
3
/
0
9
08
/
2
3
/
0
9
11
/
2
3
/
0
9
02
/
2
3
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐15 Water Level Over Time (ft. blmp)
40
50
60
70
80
90
100
110
08
/
2
3
/
0
2
11
/
2
3
/
0
2
02
/
2
3
/
0
3
05
/
2
3
/
0
3
08
/
2
3
/
0
3
11
/
2
3
/
0
3
02
/
2
3
/
0
4
05
/
2
3
/
0
4
08
/
2
3
/
0
4
11
/
2
3
/
0
4
02
/
2
3
/
0
5
05
/
2
3
/
0
5
08
/
2
3
/
0
5
11
/
2
3
/
0
5
02
/
2
3
/
0
6
05
/
2
3
/
0
6
08
/
2
3
/
0
6
11
/
2
3
/
0
6
02
/
2
3
/
0
7
05
/
2
3
/
0
7
08
/
2
3
/
0
7
11
/
2
3
/
0
7
02
/
2
3
/
0
8
05
/
2
3
/
0
8
08
/
2
3
/
0
8
11
/
2
3
/
0
8
02
/
2
3
/
0
9
05
/
2
3
/
0
9
08
/
2
3
/
0
9
11
/
2
3
/
0
9
02
/
2
3
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐15 Water Level Over Time (ft. blmp)
40
50
60
70
80
90
100
110
08
/
2
3
/
0
2
11
/
2
3
/
0
2
02
/
2
3
/
0
3
05
/
2
3
/
0
3
08
/
2
3
/
0
3
11
/
2
3
/
0
3
02
/
2
3
/
0
4
05
/
2
3
/
0
4
08
/
2
3
/
0
4
11
/
2
3
/
0
4
02
/
2
3
/
0
5
05
/
2
3
/
0
5
08
/
2
3
/
0
5
11
/
2
3
/
0
5
02
/
2
3
/
0
6
05
/
2
3
/
0
6
08
/
2
3
/
0
6
11
/
2
3
/
0
6
02
/
2
3
/
0
7
05
/
2
3
/
0
7
08
/
2
3
/
0
7
11
/
2
3
/
0
7
02
/
2
3
/
0
8
05
/
2
3
/
0
8
08
/
2
3
/
0
8
11
/
2
3
/
0
8
02
/
2
3
/
0
9
05
/
2
3
/
0
9
08
/
2
3
/
0
9
11
/
2
3
/
0
9
02
/
2
3
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐15 Water Level Over Time (ft. blmp)
50.0
55.0
60.0
65.0
08
/
2
3
/
0
2
11
/
2
3
/
0
2
02
/
2
3
/
0
3
05
/
2
3
/
0
3
08
/
2
3
/
0
3
11
/
2
3
/
0
3
02
/
2
3
/
0
4
05
/
2
3
/
0
4
08
/
2
3
/
0
4
11
/
2
3
/
0
4
02
/
2
3
/
0
5
05
/
2
3
/
0
5
08
/
2
3
/
0
5
11
/
2
3
/
0
5
02
/
2
3
/
0
6
05
/
2
3
/
0
6
08
/
2
3
/
0
6
11
/
2
3
/
0
6
02
/
2
3
/
0
7
05
/
2
3
/
0
7
08
/
2
3
/
0
7
11
/
2
3
/
0
7
02
/
2
3
/
0
8
05
/
2
3
/
0
8
08
/
2
3
/
0
8
11
/
2
3
/
0
8
02
/
2
3
/
0
9
05
/
2
3
/
0
9
08
/
2
3
/
0
9
11
/
2
3
/
0
9
02
/
2
3
/
1
0
w Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐16 Water Level Over Time (ft. blmp)
50.0
55.0
60.0
65.0
70.0
75.0
80.0
08
/
2
3
/
0
2
11
/
2
3
/
0
2
02
/
2
3
/
0
3
05
/
2
3
/
0
3
08
/
2
3
/
0
3
11
/
2
3
/
0
3
02
/
2
3
/
0
4
05
/
2
3
/
0
4
08
/
2
3
/
0
4
11
/
2
3
/
0
4
02
/
2
3
/
0
5
05
/
2
3
/
0
5
08
/
2
3
/
0
5
11
/
2
3
/
0
5
02
/
2
3
/
0
6
05
/
2
3
/
0
6
08
/
2
3
/
0
6
11
/
2
3
/
0
6
02
/
2
3
/
0
7
05
/
2
3
/
0
7
08
/
2
3
/
0
7
11
/
2
3
/
0
7
02
/
2
3
/
0
8
05
/
2
3
/
0
8
08
/
2
3
/
0
8
11
/
2
3
/
0
8
02
/
2
3
/
0
9
05
/
2
3
/
0
9
08
/
2
3
/
0
9
11
/
2
3
/
0
9
02
/
2
3
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐16 Water Level Over Time (ft. blmp)
TW4‐17 Water Level Over Time (ft. blmp)
75.0
8/
2
3
/
2
0
0
2
11
/
2
3
/
2
0
0
2
2/
2
3
/
2
0
0
3
5/
2
3
/
2
0
0
3
8/
2
3
/
2
0
0
3
11
/
2
3
/
2
0
0
3
2/
2
3
/
2
0
0
4
5/
2
3
/
2
0
0
4
8/
2
3
/
2
0
0
4
11
/
2
3
/
2
0
0
4
2/
2
3
/
2
0
0
5
5/
2
3
/
2
0
0
5
8/
2
3
/
2
0
0
5
11
/
2
3
/
2
0
0
5
2/
2
3
/
2
0
0
6
5/
2
3
/
2
0
0
6
8/
2
3
/
2
0
0
6
11
/
2
3
/
2
0
0
6
2/
2
3
/
2
0
0
7
5/
2
3
/
2
0
0
7
8/
2
3
/
2
0
0
7
11
/
2
3
/
2
0
0
7
2/
2
3
/
2
0
0
8
5/
2
3
/
2
0
0
8
8/
2
3
/
2
0
0
8
11
/
2
3
/
2
0
0
8
2/
2
3
/
2
0
0
9
5/
2
3
/
2
0
0
9
8/
2
3
/
2
0
0
9
11
/
2
3
/
2
0
0
9
2/
2
3
/
2
0
1
0
TW4‐17 Water Level Over Time (ft. blmp)
75.0
76.0
77.0
8/
2
3
/
2
0
0
2
11
/
2
3
/
2
0
0
2
2/
2
3
/
2
0
0
3
5/
2
3
/
2
0
0
3
8/
2
3
/
2
0
0
3
11
/
2
3
/
2
0
0
3
2/
2
3
/
2
0
0
4
5/
2
3
/
2
0
0
4
8/
2
3
/
2
0
0
4
11
/
2
3
/
2
0
0
4
2/
2
3
/
2
0
0
5
5/
2
3
/
2
0
0
5
8/
2
3
/
2
0
0
5
11
/
2
3
/
2
0
0
5
2/
2
3
/
2
0
0
6
5/
2
3
/
2
0
0
6
8/
2
3
/
2
0
0
6
11
/
2
3
/
2
0
0
6
2/
2
3
/
2
0
0
7
5/
2
3
/
2
0
0
7
8/
2
3
/
2
0
0
7
11
/
2
3
/
2
0
0
7
2/
2
3
/
2
0
0
8
5/
2
3
/
2
0
0
8
8/
2
3
/
2
0
0
8
11
/
2
3
/
2
0
0
8
2/
2
3
/
2
0
0
9
5/
2
3
/
2
0
0
9
8/
2
3
/
2
0
0
9
11
/
2
3
/
2
0
0
9
2/
2
3
/
2
0
1
0
t (f
t
.
)
TW4‐17 Water Level Over Time (ft. blmp)
75.0
76.0
77.0
78.0
79.0
80 0
8/
2
3
/
2
0
0
2
11
/
2
3
/
2
0
0
2
2/
2
3
/
2
0
0
3
5/
2
3
/
2
0
0
3
8/
2
3
/
2
0
0
3
11
/
2
3
/
2
0
0
3
2/
2
3
/
2
0
0
4
5/
2
3
/
2
0
0
4
8/
2
3
/
2
0
0
4
11
/
2
3
/
2
0
0
4
2/
2
3
/
2
0
0
5
5/
2
3
/
2
0
0
5
8/
2
3
/
2
0
0
5
11
/
2
3
/
2
0
0
5
2/
2
3
/
2
0
0
6
5/
2
3
/
2
0
0
6
8/
2
3
/
2
0
0
6
11
/
2
3
/
2
0
0
6
2/
2
3
/
2
0
0
7
5/
2
3
/
2
0
0
7
8/
2
3
/
2
0
0
7
11
/
2
3
/
2
0
0
7
2/
2
3
/
2
0
0
8
5/
2
3
/
2
0
0
8
8/
2
3
/
2
0
0
8
11
/
2
3
/
2
0
0
8
2/
2
3
/
2
0
0
9
5/
2
3
/
2
0
0
9
8/
2
3
/
2
0
0
9
11
/
2
3
/
2
0
0
9
2/
2
3
/
2
0
1
0
Mea
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐17 Water Level Over Time (ft. blmp)
75.0
76.0
77.0
78.0
79.0
80.0
81.0
82.0
8/
2
3
/
2
0
0
2
11
/
2
3
/
2
0
0
2
2/
2
3
/
2
0
0
3
5/
2
3
/
2
0
0
3
8/
2
3
/
2
0
0
3
11
/
2
3
/
2
0
0
3
2/
2
3
/
2
0
0
4
5/
2
3
/
2
0
0
4
8/
2
3
/
2
0
0
4
11
/
2
3
/
2
0
0
4
2/
2
3
/
2
0
0
5
5/
2
3
/
2
0
0
5
8/
2
3
/
2
0
0
5
11
/
2
3
/
2
0
0
5
2/
2
3
/
2
0
0
6
5/
2
3
/
2
0
0
6
8/
2
3
/
2
0
0
6
11
/
2
3
/
2
0
0
6
2/
2
3
/
2
0
0
7
5/
2
3
/
2
0
0
7
8/
2
3
/
2
0
0
7
11
/
2
3
/
2
0
0
7
2/
2
3
/
2
0
0
8
5/
2
3
/
2
0
0
8
8/
2
3
/
2
0
0
8
11
/
2
3
/
2
0
0
8
2/
2
3
/
2
0
0
9
5/
2
3
/
2
0
0
9
8/
2
3
/
2
0
0
9
11
/
2
3
/
2
0
0
9
2/
2
3
/
2
0
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐17 Water Level Over Time (ft. blmp)
75.0
76.0
77.0
78.0
79.0
80.0
81.0
82.0
83.0
84.0
8/
2
3
/
2
0
0
2
11
/
2
3
/
2
0
0
2
2/
2
3
/
2
0
0
3
5/
2
3
/
2
0
0
3
8/
2
3
/
2
0
0
3
11
/
2
3
/
2
0
0
3
2/
2
3
/
2
0
0
4
5/
2
3
/
2
0
0
4
8/
2
3
/
2
0
0
4
11
/
2
3
/
2
0
0
4
2/
2
3
/
2
0
0
5
5/
2
3
/
2
0
0
5
8/
2
3
/
2
0
0
5
11
/
2
3
/
2
0
0
5
2/
2
3
/
2
0
0
6
5/
2
3
/
2
0
0
6
8/
2
3
/
2
0
0
6
11
/
2
3
/
2
0
0
6
2/
2
3
/
2
0
0
7
5/
2
3
/
2
0
0
7
8/
2
3
/
2
0
0
7
11
/
2
3
/
2
0
0
7
2/
2
3
/
2
0
0
8
5/
2
3
/
2
0
0
8
8/
2
3
/
2
0
0
8
11
/
2
3
/
2
0
0
8
2/
2
3
/
2
0
0
9
5/
2
3
/
2
0
0
9
8/
2
3
/
2
0
0
9
11
/
2
3
/
2
0
0
9
2/
2
3
/
2
0
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐17 Water Level Over Time (ft. blmp)
75.0
76.0
77.0
78.0
79.0
80.0
81.0
82.0
83.0
84.0
8/
2
3
/
2
0
0
2
11
/
2
3
/
2
0
0
2
2/
2
3
/
2
0
0
3
5/
2
3
/
2
0
0
3
8/
2
3
/
2
0
0
3
11
/
2
3
/
2
0
0
3
2/
2
3
/
2
0
0
4
5/
2
3
/
2
0
0
4
8/
2
3
/
2
0
0
4
11
/
2
3
/
2
0
0
4
2/
2
3
/
2
0
0
5
5/
2
3
/
2
0
0
5
8/
2
3
/
2
0
0
5
11
/
2
3
/
2
0
0
5
2/
2
3
/
2
0
0
6
5/
2
3
/
2
0
0
6
8/
2
3
/
2
0
0
6
11
/
2
3
/
2
0
0
6
2/
2
3
/
2
0
0
7
5/
2
3
/
2
0
0
7
8/
2
3
/
2
0
0
7
11
/
2
3
/
2
0
0
7
2/
2
3
/
2
0
0
8
5/
2
3
/
2
0
0
8
8/
2
3
/
2
0
0
8
11
/
2
3
/
2
0
0
8
2/
2
3
/
2
0
0
9
5/
2
3
/
2
0
0
9
8/
2
3
/
2
0
0
9
11
/
2
3
/
2
0
0
9
2/
2
3
/
2
0
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐17 Water Level Over Time (ft. blmp)
TW4‐18 Water Level Over Time (ft. blmp)
48.0
8/
2
3
/
2
0
0
2
11
/
2
3
/
2
0
0
2
2/
2
3
/
2
0
0
3
5/
2
3
/
2
0
0
3
8/
2
3
/
2
0
0
3
11
/
2
3
/
2
0
0
3
2/
2
3
/
2
0
0
4
5/
2
3
/
2
0
0
4
8/
2
3
/
2
0
0
4
11
/
2
3
/
2
0
0
4
2/
2
3
/
2
0
0
5
5/
2
3
/
2
0
0
5
8/
2
3
/
2
0
0
5
11
/
2
3
/
2
0
0
5
2/
2
3
/
2
0
0
6
5/
2
3
/
2
0
0
6
8/
2
3
/
2
0
0
6
11
/
2
3
/
2
0
0
6
2/
2
3
/
2
0
0
7
5/
2
3
/
2
0
0
7
8/
2
3
/
2
0
0
7
11
/
2
3
/
2
0
0
7
2/
2
3
/
2
0
0
8
5/
2
3
/
2
0
0
8
8/
2
3
/
2
0
0
8
11
/
2
3
/
2
0
0
8
2/
2
3
/
2
0
0
9
5/
2
3
/
2
0
0
9
8/
2
3
/
2
0
0
9
11
/
2
3
/
2
0
0
9
2/
2
3
/
2
0
1
0
TW4‐18 Water Level Over Time (ft. blmp)
48.0
50.0
8/
2
3
/
2
0
0
2
11
/
2
3
/
2
0
0
2
2/
2
3
/
2
0
0
3
5/
2
3
/
2
0
0
3
8/
2
3
/
2
0
0
3
11
/
2
3
/
2
0
0
3
2/
2
3
/
2
0
0
4
5/
2
3
/
2
0
0
4
8/
2
3
/
2
0
0
4
11
/
2
3
/
2
0
0
4
2/
2
3
/
2
0
0
5
5/
2
3
/
2
0
0
5
8/
2
3
/
2
0
0
5
11
/
2
3
/
2
0
0
5
2/
2
3
/
2
0
0
6
5/
2
3
/
2
0
0
6
8/
2
3
/
2
0
0
6
11
/
2
3
/
2
0
0
6
2/
2
3
/
2
0
0
7
5/
2
3
/
2
0
0
7
8/
2
3
/
2
0
0
7
11
/
2
3
/
2
0
0
7
2/
2
3
/
2
0
0
8
5/
2
3
/
2
0
0
8
8/
2
3
/
2
0
0
8
11
/
2
3
/
2
0
0
8
2/
2
3
/
2
0
0
9
5/
2
3
/
2
0
0
9
8/
2
3
/
2
0
0
9
11
/
2
3
/
2
0
0
9
2/
2
3
/
2
0
1
0
t (f
t
.
)
TW4‐18 Water Level Over Time (ft. blmp)
48.0
50.0
52.0
54.0
8/
2
3
/
2
0
0
2
11
/
2
3
/
2
0
0
2
2/
2
3
/
2
0
0
3
5/
2
3
/
2
0
0
3
8/
2
3
/
2
0
0
3
11
/
2
3
/
2
0
0
3
2/
2
3
/
2
0
0
4
5/
2
3
/
2
0
0
4
8/
2
3
/
2
0
0
4
11
/
2
3
/
2
0
0
4
2/
2
3
/
2
0
0
5
5/
2
3
/
2
0
0
5
8/
2
3
/
2
0
0
5
11
/
2
3
/
2
0
0
5
2/
2
3
/
2
0
0
6
5/
2
3
/
2
0
0
6
8/
2
3
/
2
0
0
6
11
/
2
3
/
2
0
0
6
2/
2
3
/
2
0
0
7
5/
2
3
/
2
0
0
7
8/
2
3
/
2
0
0
7
11
/
2
3
/
2
0
0
7
2/
2
3
/
2
0
0
8
5/
2
3
/
2
0
0
8
8/
2
3
/
2
0
0
8
11
/
2
3
/
2
0
0
8
2/
2
3
/
2
0
0
9
5/
2
3
/
2
0
0
9
8/
2
3
/
2
0
0
9
11
/
2
3
/
2
0
0
9
2/
2
3
/
2
0
1
0
Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐18 Water Level Over Time (ft. blmp)
48.0
50.0
52.0
54.0
56.0
58.0
8/
2
3
/
2
0
0
2
11
/
2
3
/
2
0
0
2
2/
2
3
/
2
0
0
3
5/
2
3
/
2
0
0
3
8/
2
3
/
2
0
0
3
11
/
2
3
/
2
0
0
3
2/
2
3
/
2
0
0
4
5/
2
3
/
2
0
0
4
8/
2
3
/
2
0
0
4
11
/
2
3
/
2
0
0
4
2/
2
3
/
2
0
0
5
5/
2
3
/
2
0
0
5
8/
2
3
/
2
0
0
5
11
/
2
3
/
2
0
0
5
2/
2
3
/
2
0
0
6
5/
2
3
/
2
0
0
6
8/
2
3
/
2
0
0
6
11
/
2
3
/
2
0
0
6
2/
2
3
/
2
0
0
7
5/
2
3
/
2
0
0
7
8/
2
3
/
2
0
0
7
11
/
2
3
/
2
0
0
7
2/
2
3
/
2
0
0
8
5/
2
3
/
2
0
0
8
8/
2
3
/
2
0
0
8
11
/
2
3
/
2
0
0
8
2/
2
3
/
2
0
0
9
5/
2
3
/
2
0
0
9
8/
2
3
/
2
0
0
9
11
/
2
3
/
2
0
0
9
2/
2
3
/
2
0
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐18 Water Level Over Time (ft. blmp)
48.0
50.0
52.0
54.0
56.0
58.0
60.0
8/
2
3
/
2
0
0
2
11
/
2
3
/
2
0
0
2
2/
2
3
/
2
0
0
3
5/
2
3
/
2
0
0
3
8/
2
3
/
2
0
0
3
11
/
2
3
/
2
0
0
3
2/
2
3
/
2
0
0
4
5/
2
3
/
2
0
0
4
8/
2
3
/
2
0
0
4
11
/
2
3
/
2
0
0
4
2/
2
3
/
2
0
0
5
5/
2
3
/
2
0
0
5
8/
2
3
/
2
0
0
5
11
/
2
3
/
2
0
0
5
2/
2
3
/
2
0
0
6
5/
2
3
/
2
0
0
6
8/
2
3
/
2
0
0
6
11
/
2
3
/
2
0
0
6
2/
2
3
/
2
0
0
7
5/
2
3
/
2
0
0
7
8/
2
3
/
2
0
0
7
11
/
2
3
/
2
0
0
7
2/
2
3
/
2
0
0
8
5/
2
3
/
2
0
0
8
8/
2
3
/
2
0
0
8
11
/
2
3
/
2
0
0
8
2/
2
3
/
2
0
0
9
5/
2
3
/
2
0
0
9
8/
2
3
/
2
0
0
9
11
/
2
3
/
2
0
0
9
2/
2
3
/
2
0
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐18 Water Level Over Time (ft. blmp)
48.0
50.0
52.0
54.0
56.0
58.0
60.0
8/
2
3
/
2
0
0
2
11
/
2
3
/
2
0
0
2
2/
2
3
/
2
0
0
3
5/
2
3
/
2
0
0
3
8/
2
3
/
2
0
0
3
11
/
2
3
/
2
0
0
3
2/
2
3
/
2
0
0
4
5/
2
3
/
2
0
0
4
8/
2
3
/
2
0
0
4
11
/
2
3
/
2
0
0
4
2/
2
3
/
2
0
0
5
5/
2
3
/
2
0
0
5
8/
2
3
/
2
0
0
5
11
/
2
3
/
2
0
0
5
2/
2
3
/
2
0
0
6
5/
2
3
/
2
0
0
6
8/
2
3
/
2
0
0
6
11
/
2
3
/
2
0
0
6
2/
2
3
/
2
0
0
7
5/
2
3
/
2
0
0
7
8/
2
3
/
2
0
0
7
11
/
2
3
/
2
0
0
7
2/
2
3
/
2
0
0
8
5/
2
3
/
2
0
0
8
8/
2
3
/
2
0
0
8
11
/
2
3
/
2
0
0
8
2/
2
3
/
2
0
0
9
5/
2
3
/
2
0
0
9
8/
2
3
/
2
0
0
9
11
/
2
3
/
2
0
0
9
2/
2
3
/
2
0
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐18 Water Level Over Time (ft. blmp)
2 2 3 3 3 3 4 4 4 4 5 5 5 5 6 6 6 6 7 7 7 7 8 8 8 8 9 9 9 9 0
TW4‐19 Water Level Over Time (ft. blmp)
45.0
08
/
2
3
/
0
2
11
/
2
3
/
0
2
02
/
2
3
/
0
3
05
/
2
3
/
0
3
08
/
2
3
/
0
3
11
/
2
3
/
0
3
02
/
2
3
/
0
4
05
/
2
3
/
0
4
08
/
2
3
/
0
4
11
/
2
3
/
0
4
02
/
2
3
/
0
5
05
/
2
3
/
0
5
08
/
2
3
/
0
5
11
/
2
3
/
0
5
02
/
2
3
/
0
6
05
/
2
3
/
0
6
08
/
2
3
/
0
6
11
/
2
3
/
0
6
02
/
2
3
/
0
7
05
/
2
3
/
0
7
08
/
2
3
/
0
7
11
/
2
3
/
0
7
02
/
2
3
/
0
8
05
/
2
3
/
0
8
08
/
2
3
/
0
8
11
/
2
3
/
0
8
02
/
2
3
/
0
9
05
/
2
3
/
0
9
08
/
2
3
/
0
9
11
/
2
3
/
0
9
02
/
2
3
/
1
0
TW4‐19 Water Level Over Time (ft. blmp)
45.0
55.0
08
/
2
3
/
0
2
11
/
2
3
/
0
2
02
/
2
3
/
0
3
05
/
2
3
/
0
3
08
/
2
3
/
0
3
11
/
2
3
/
0
3
02
/
2
3
/
0
4
05
/
2
3
/
0
4
08
/
2
3
/
0
4
11
/
2
3
/
0
4
02
/
2
3
/
0
5
05
/
2
3
/
0
5
08
/
2
3
/
0
5
11
/
2
3
/
0
5
02
/
2
3
/
0
6
05
/
2
3
/
0
6
08
/
2
3
/
0
6
11
/
2
3
/
0
6
02
/
2
3
/
0
7
05
/
2
3
/
0
7
08
/
2
3
/
0
7
11
/
2
3
/
0
7
02
/
2
3
/
0
8
05
/
2
3
/
0
8
08
/
2
3
/
0
8
11
/
2
3
/
0
8
02
/
2
3
/
0
9
05
/
2
3
/
0
9
08
/
2
3
/
0
9
11
/
2
3
/
0
9
02
/
2
3
/
1
0
nt
 (f
t
.
)
TW4‐19 Water Level Over Time (ft. blmp)
45.0
55.0
65.0
75 0
08
/
2
3
/
0
2
11
/
2
3
/
0
2
02
/
2
3
/
0
3
05
/
2
3
/
0
3
08
/
2
3
/
0
3
11
/
2
3
/
0
3
02
/
2
3
/
0
4
05
/
2
3
/
0
4
08
/
2
3
/
0
4
11
/
2
3
/
0
4
02
/
2
3
/
0
5
05
/
2
3
/
0
5
08
/
2
3
/
0
5
11
/
2
3
/
0
5
02
/
2
3
/
0
6
05
/
2
3
/
0
6
08
/
2
3
/
0
6
11
/
2
3
/
0
6
02
/
2
3
/
0
7
05
/
2
3
/
0
7
08
/
2
3
/
0
7
11
/
2
3
/
0
7
02
/
2
3
/
0
8
05
/
2
3
/
0
8
08
/
2
3
/
0
8
11
/
2
3
/
0
8
02
/
2
3
/
0
9
05
/
2
3
/
0
9
08
/
2
3
/
0
9
11
/
2
3
/
0
9
02
/
2
3
/
1
0
Mea
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐19 Water Level Over Time (ft. blmp)
45.0
55.0
65.0
75.0
85.0
08
/
2
3
/
0
2
11
/
2
3
/
0
2
02
/
2
3
/
0
3
05
/
2
3
/
0
3
08
/
2
3
/
0
3
11
/
2
3
/
0
3
02
/
2
3
/
0
4
05
/
2
3
/
0
4
08
/
2
3
/
0
4
11
/
2
3
/
0
4
02
/
2
3
/
0
5
05
/
2
3
/
0
5
08
/
2
3
/
0
5
11
/
2
3
/
0
5
02
/
2
3
/
0
6
05
/
2
3
/
0
6
08
/
2
3
/
0
6
11
/
2
3
/
0
6
02
/
2
3
/
0
7
05
/
2
3
/
0
7
08
/
2
3
/
0
7
11
/
2
3
/
0
7
02
/
2
3
/
0
8
05
/
2
3
/
0
8
08
/
2
3
/
0
8
11
/
2
3
/
0
8
02
/
2
3
/
0
9
05
/
2
3
/
0
9
08
/
2
3
/
0
9
11
/
2
3
/
0
9
02
/
2
3
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐19 Water Level Over Time (ft. blmp)
45.0
55.0
65.0
75.0
85.0
95.0
08
/
2
3
/
0
2
11
/
2
3
/
0
2
02
/
2
3
/
0
3
05
/
2
3
/
0
3
08
/
2
3
/
0
3
11
/
2
3
/
0
3
02
/
2
3
/
0
4
05
/
2
3
/
0
4
08
/
2
3
/
0
4
11
/
2
3
/
0
4
02
/
2
3
/
0
5
05
/
2
3
/
0
5
08
/
2
3
/
0
5
11
/
2
3
/
0
5
02
/
2
3
/
0
6
05
/
2
3
/
0
6
08
/
2
3
/
0
6
11
/
2
3
/
0
6
02
/
2
3
/
0
7
05
/
2
3
/
0
7
08
/
2
3
/
0
7
11
/
2
3
/
0
7
02
/
2
3
/
0
8
05
/
2
3
/
0
8
08
/
2
3
/
0
8
11
/
2
3
/
0
8
02
/
2
3
/
0
9
05
/
2
3
/
0
9
08
/
2
3
/
0
9
11
/
2
3
/
0
9
02
/
2
3
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐19 Water Level Over Time (ft. blmp)
45.0
55.0
65.0
75.0
85.0
95.0
08
/
2
3
/
0
2
11
/
2
3
/
0
2
02
/
2
3
/
0
3
05
/
2
3
/
0
3
08
/
2
3
/
0
3
11
/
2
3
/
0
3
02
/
2
3
/
0
4
05
/
2
3
/
0
4
08
/
2
3
/
0
4
11
/
2
3
/
0
4
02
/
2
3
/
0
5
05
/
2
3
/
0
5
08
/
2
3
/
0
5
11
/
2
3
/
0
5
02
/
2
3
/
0
6
05
/
2
3
/
0
6
08
/
2
3
/
0
6
11
/
2
3
/
0
6
02
/
2
3
/
0
7
05
/
2
3
/
0
7
08
/
2
3
/
0
7
11
/
2
3
/
0
7
02
/
2
3
/
0
8
05
/
2
3
/
0
8
08
/
2
3
/
0
8
11
/
2
3
/
0
8
02
/
2
3
/
0
9
05
/
2
3
/
0
9
08
/
2
3
/
0
9
11
/
2
3
/
0
9
02
/
2
3
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐19 Water Level Over Time (ft. blmp)
5 5 6 6 6 6 7 7 7 7 8 8 8 8 9 9 9 9 0
TW4‐20 Water Level Over Time (ft. blmp)
45.0
07
/
2
9
/
0
5
10
/
2
9
/
0
5
01
/
2
9
/
0
6
04
/
2
9
/
0
6
07
/
2
9
/
0
6
10
/
2
9
/
0
6
01
/
2
9
/
0
7
04
/
2
9
/
0
7
07
/
2
9
/
0
7
10
/
2
9
/
0
7
01
/
2
9
/
0
8
04
/
2
9
/
0
8
07
/
2
9
/
0
8
10
/
2
9
/
0
8
01
/
2
9
/
0
9
04
/
2
9
/
0
9
07
/
2
9
/
0
9
10
/
2
9
/
0
9
01
/
2
9
/
1
0
TW4‐20 Water Level Over Time (ft. blmp)
45.0
55.0
65 0
07
/
2
9
/
0
5
10
/
2
9
/
0
5
01
/
2
9
/
0
6
04
/
2
9
/
0
6
07
/
2
9
/
0
6
10
/
2
9
/
0
6
01
/
2
9
/
0
7
04
/
2
9
/
0
7
07
/
2
9
/
0
7
10
/
2
9
/
0
7
01
/
2
9
/
0
8
04
/
2
9
/
0
8
07
/
2
9
/
0
8
10
/
2
9
/
0
8
01
/
2
9
/
0
9
04
/
2
9
/
0
9
07
/
2
9
/
0
9
10
/
2
9
/
0
9
01
/
2
9
/
1
0
nt (f
t
.
)
TW4‐20 Water Level Over Time (ft. blmp)
45.0
55.0
65.0
75.0
07
/
2
9
/
0
5
10
/
2
9
/
0
5
01
/
2
9
/
0
6
04
/
2
9
/
0
6
07
/
2
9
/
0
6
10
/
2
9
/
0
6
01
/
2
9
/
0
7
04
/
2
9
/
0
7
07
/
2
9
/
0
7
10
/
2
9
/
0
7
01
/
2
9
/
0
8
04
/
2
9
/
0
8
07
/
2
9
/
0
8
10
/
2
9
/
0
8
01
/
2
9
/
0
9
04
/
2
9
/
0
9
07
/
2
9
/
0
9
10
/
2
9
/
0
9
01
/
2
9
/
1
0
Mea
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐20 Water Level Over Time (ft. blmp)
45.0
55.0
65.0
75.0
85.0
07
/
2
9
/
0
5
10
/
2
9
/
0
5
01
/
2
9
/
0
6
04
/
2
9
/
0
6
07
/
2
9
/
0
6
10
/
2
9
/
0
6
01
/
2
9
/
0
7
04
/
2
9
/
0
7
07
/
2
9
/
0
7
10
/
2
9
/
0
7
01
/
2
9
/
0
8
04
/
2
9
/
0
8
07
/
2
9
/
0
8
10
/
2
9
/
0
8
01
/
2
9
/
0
9
04
/
2
9
/
0
9
07
/
2
9
/
0
9
10
/
2
9
/
0
9
01
/
2
9
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐20 Water Level Over Time (ft. blmp)
45.0
55.0
65.0
75.0
85.0
95.0
105.0
07
/
2
9
/
0
5
10
/
2
9
/
0
5
01
/
2
9
/
0
6
04
/
2
9
/
0
6
07
/
2
9
/
0
6
10
/
2
9
/
0
6
01
/
2
9
/
0
7
04
/
2
9
/
0
7
07
/
2
9
/
0
7
10
/
2
9
/
0
7
01
/
2
9
/
0
8
04
/
2
9
/
0
8
07
/
2
9
/
0
8
10
/
2
9
/
0
8
01
/
2
9
/
0
9
04
/
2
9
/
0
9
07
/
2
9
/
0
9
10
/
2
9
/
0
9
01
/
2
9
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐20 Water Level Over Time (ft. blmp)
45.0
55.0
65.0
75.0
85.0
95.0
105.0
07
/
2
9
/
0
5
10
/
2
9
/
0
5
01
/
2
9
/
0
6
04
/
2
9
/
0
6
07
/
2
9
/
0
6
10
/
2
9
/
0
6
01
/
2
9
/
0
7
04
/
2
9
/
0
7
07
/
2
9
/
0
7
10
/
2
9
/
0
7
01
/
2
9
/
0
8
04
/
2
9
/
0
8
07
/
2
9
/
0
8
10
/
2
9
/
0
8
01
/
2
9
/
0
9
04
/
2
9
/
0
9
07
/
2
9
/
0
9
10
/
2
9
/
0
9
01
/
2
9
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐20 Water Level Over Time (ft. blmp)
TW4‐21 Water Level Over Time (ft. blmp)
52.0
7/
2
9
/
2
0
0
5
10
/
2
9
/
2
0
0
5
1/
2
9
/
2
0
0
6
4/
2
9
/
2
0
0
6
7/
2
9
/
2
0
0
6
10
/
2
9
/
2
0
0
6
1/
2
9
/
2
0
0
7
4/
2
9
/
2
0
0
7
7/
2
9
/
2
0
0
7
10
/
2
9
/
2
0
0
7
1/
2
9
/
2
0
0
8
4/
2
9
/
2
0
0
8
7/
2
9
/
2
0
0
8
10
/
2
9
/
2
0
0
8
1/
2
9
/
2
0
0
9
4/
2
9
/
2
0
0
9
7/
2
9
/
2
0
0
9
10
/
2
9
/
2
0
0
9
1/
2
9
/
2
0
1
0
TW4‐21 Water Level Over Time (ft. blmp)
52.0
54.0
7/
2
9
/
2
0
0
5
10
/
2
9
/
2
0
0
5
1/
2
9
/
2
0
0
6
4/
2
9
/
2
0
0
6
7/
2
9
/
2
0
0
6
10
/
2
9
/
2
0
0
6
1/
2
9
/
2
0
0
7
4/
2
9
/
2
0
0
7
7/
2
9
/
2
0
0
7
10
/
2
9
/
2
0
0
7
1/
2
9
/
2
0
0
8
4/
2
9
/
2
0
0
8
7/
2
9
/
2
0
0
8
10
/
2
9
/
2
0
0
8
1/
2
9
/
2
0
0
9
4/
2
9
/
2
0
0
9
7/
2
9
/
2
0
0
9
10
/
2
9
/
2
0
0
9
1/
2
9
/
2
0
1
0
t (f
t
.
)
TW4‐21 Water Level Over Time (ft. blmp)
52.0
54.0
56.0
58.0
7/
2
9
/
2
0
0
5
10
/
2
9
/
2
0
0
5
1/
2
9
/
2
0
0
6
4/
2
9
/
2
0
0
6
7/
2
9
/
2
0
0
6
10
/
2
9
/
2
0
0
6
1/
2
9
/
2
0
0
7
4/
2
9
/
2
0
0
7
7/
2
9
/
2
0
0
7
10
/
2
9
/
2
0
0
7
1/
2
9
/
2
0
0
8
4/
2
9
/
2
0
0
8
7/
2
9
/
2
0
0
8
10
/
2
9
/
2
0
0
8
1/
2
9
/
2
0
0
9
4/
2
9
/
2
0
0
9
7/
2
9
/
2
0
0
9
10
/
2
9
/
2
0
0
9
1/
2
9
/
2
0
1
0
Mea
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐21 Water Level Over Time (ft. blmp)
52.0
54.0
56.0
58.0
60.0
7/
2
9
/
2
0
0
5
10
/
2
9
/
2
0
0
5
1/
2
9
/
2
0
0
6
4/
2
9
/
2
0
0
6
7/
2
9
/
2
0
0
6
10
/
2
9
/
2
0
0
6
1/
2
9
/
2
0
0
7
4/
2
9
/
2
0
0
7
7/
2
9
/
2
0
0
7
10
/
2
9
/
2
0
0
7
1/
2
9
/
2
0
0
8
4/
2
9
/
2
0
0
8
7/
2
9
/
2
0
0
8
10
/
2
9
/
2
0
0
8
1/
2
9
/
2
0
0
9
4/
2
9
/
2
0
0
9
7/
2
9
/
2
0
0
9
10
/
2
9
/
2
0
0
9
1/
2
9
/
2
0
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐21 Water Level Over Time (ft. blmp)
52.0
54.0
56.0
58.0
60.0
62.0
64.0
7/
2
9
/
2
0
0
5
10
/
2
9
/
2
0
0
5
1/
2
9
/
2
0
0
6
4/
2
9
/
2
0
0
6
7/
2
9
/
2
0
0
6
10
/
2
9
/
2
0
0
6
1/
2
9
/
2
0
0
7
4/
2
9
/
2
0
0
7
7/
2
9
/
2
0
0
7
10
/
2
9
/
2
0
0
7
1/
2
9
/
2
0
0
8
4/
2
9
/
2
0
0
8
7/
2
9
/
2
0
0
8
10
/
2
9
/
2
0
0
8
1/
2
9
/
2
0
0
9
4/
2
9
/
2
0
0
9
7/
2
9
/
2
0
0
9
10
/
2
9
/
2
0
0
9
1/
2
9
/
2
0
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐21 Water Level Over Time (ft. blmp)
52.0
54.0
56.0
58.0
60.0
62.0
64.0
7/
2
9
/
2
0
0
5
10
/
2
9
/
2
0
0
5
1/
2
9
/
2
0
0
6
4/
2
9
/
2
0
0
6
7/
2
9
/
2
0
0
6
10
/
2
9
/
2
0
0
6
1/
2
9
/
2
0
0
7
4/
2
9
/
2
0
0
7
7/
2
9
/
2
0
0
7
10
/
2
9
/
2
0
0
7
1/
2
9
/
2
0
0
8
4/
2
9
/
2
0
0
8
7/
2
9
/
2
0
0
8
10
/
2
9
/
2
0
0
8
1/
2
9
/
2
0
0
9
4/
2
9
/
2
0
0
9
7/
2
9
/
2
0
0
9
10
/
2
9
/
2
0
0
9
1/
2
9
/
2
0
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐21 Water Level Over Time (ft. blmp)
53.50
54.00
54.50
55.00
55.50
56.00
07
/
2
9
/
0
5
10
/
2
9
/
0
5
01
/
2
9
/
0
6
04
/
2
9
/
0
6
07
/
2
9
/
0
6
10
/
2
9
/
0
6
01
/
2
9
/
0
7
04
/
2
9
/
0
7
07
/
2
9
/
0
7
10
/
2
9
/
0
7
01
/
2
9
/
0
8
04
/
2
9
/
0
8
07
/
2
9
/
0
8
10
/
2
9
/
0
8
01
/
2
9
/
0
9
04
/
2
9
/
0
9
07
/
2
9
/
0
9
10
/
2
9
/
0
9
01
/
2
9
/
1
0
eas
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐22 Water Depth Over Time
53.50
54.00
54.50
55.00
55.50
56.00
56.50
57.00
57.50
58.00
58.50
07
/
2
9
/
0
5
10
/
2
9
/
0
5
01
/
2
9
/
0
6
04
/
2
9
/
0
6
07
/
2
9
/
0
6
10
/
2
9
/
0
6
01
/
2
9
/
0
7
04
/
2
9
/
0
7
07
/
2
9
/
0
7
10
/
2
9
/
0
7
01
/
2
9
/
0
8
04
/
2
9
/
0
8
07
/
2
9
/
0
8
10
/
2
9
/
0
8
01
/
2
9
/
0
9
04
/
2
9
/
0
9
07
/
2
9
/
0
9
10
/
2
9
/
0
9
01
/
2
9
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐22 Water Depth Over Time
65.00
65.50
66.00
66.50
67.00
09
/
1
3
/
0
7
10
/
1
3
/
0
7
11
/
1
3
/
0
7
12
/
1
3
/
0
7
01
/
1
3
/
0
8
02
/
1
3
/
0
8
03
/
1
3
/
0
8
04
/
1
3
/
0
8
05
/
1
3
/
0
8
06
/
1
3
/
0
8
07
/
1
3
/
0
8
08
/
1
3
/
0
8
09
/
1
3
/
0
8
10
/
1
3
/
0
8
11
/
1
3
/
0
8
12
/
1
3
/
0
8
01
/
1
3
/
0
9
02
/
1
3
/
0
9
03
/
1
3
/
0
9
04
/
1
3
/
0
9
05
/
1
3
/
0
9
06
/
1
3
/
0
9
07
/
1
3
/
0
9
08
/
1
3
/
0
9
09
/
1
3
/
0
9
10
/
1
3
/
0
9
11
/
1
3
/
0
9
12
/
1
3
/
0
9
01
/
1
3
/
1
0
02
/
1
3
/
1
0
ea
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐23 Water Depth Over Time (ft. blmp)
65.00
65.50
66.00
66.50
67.00
67.50
68.00
68.50
69.00
09
/
1
3
/
0
7
10
/
1
3
/
0
7
11
/
1
3
/
0
7
12
/
1
3
/
0
7
01
/
1
3
/
0
8
02
/
1
3
/
0
8
03
/
1
3
/
0
8
04
/
1
3
/
0
8
05
/
1
3
/
0
8
06
/
1
3
/
0
8
07
/
1
3
/
0
8
08
/
1
3
/
0
8
09
/
1
3
/
0
8
10
/
1
3
/
0
8
11
/
1
3
/
0
8
12
/
1
3
/
0
8
01
/
1
3
/
0
9
02
/
1
3
/
0
9
03
/
1
3
/
0
9
04
/
1
3
/
0
9
05
/
1
3
/
0
9
06
/
1
3
/
0
9
07
/
1
3
/
0
9
08
/
1
3
/
0
9
09
/
1
3
/
0
9
10
/
1
3
/
0
9
11
/
1
3
/
0
9
12
/
1
3
/
0
9
01
/
1
3
/
1
0
02
/
1
3
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐23 Water Depth Over Time (ft. blmp)
55.00
55.50
56.00
09
/
1
3
/
0
7
10
/
1
3
/
0
7
11
/
1
3
/
0
7
12
/
1
3
/
0
7
01
/
1
3
/
0
8
02
/
1
3
/
0
8
03
/
1
3
/
0
8
04
/
1
3
/
0
8
05
/
1
3
/
0
8
06
/
1
3
/
0
8
07
/
1
3
/
0
8
08
/
1
3
/
0
8
09
/
1
3
/
0
8
10
/
1
3
/
0
8
11
/
1
3
/
0
8
12
/
1
3
/
0
8
01
/
1
3
/
0
9
02
/
1
3
/
0
9
03
/
1
3
/
0
9
04
/
1
3
/
0
9
05
/
1
3
/
0
9
06
/
1
3
/
0
9
07
/
1
3
/
0
9
08
/
1
3
/
0
9
09
/
1
3
/
0
9
10
/
1
3
/
0
9
11
/
1
3
/
0
9
12
/
1
3
/
0
9
01
/
1
3
/
1
0
02
/
1
3
/
1
0
eas
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐24 Water Depth Over Time (ft. blmp)
55.00
55.50
56.00
56.50
57.00
57.50
09
/
1
3
/
0
7
10
/
1
3
/
0
7
11
/
1
3
/
0
7
12
/
1
3
/
0
7
01
/
1
3
/
0
8
02
/
1
3
/
0
8
03
/
1
3
/
0
8
04
/
1
3
/
0
8
05
/
1
3
/
0
8
06
/
1
3
/
0
8
07
/
1
3
/
0
8
08
/
1
3
/
0
8
09
/
1
3
/
0
8
10
/
1
3
/
0
8
11
/
1
3
/
0
8
12
/
1
3
/
0
8
01
/
1
3
/
0
9
02
/
1
3
/
0
9
03
/
1
3
/
0
9
04
/
1
3
/
0
9
05
/
1
3
/
0
9
06
/
1
3
/
0
9
07
/
1
3
/
0
9
08
/
1
3
/
0
9
09
/
1
3
/
0
9
10
/
1
3
/
0
9
11
/
1
3
/
0
9
12
/
1
3
/
0
9
01
/
1
3
/
1
0
02
/
1
3
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐24 Water Depth Over Time (ft. blmp)
40.0
45.0
50.0
09
/
1
3
/
0
7
10
/
1
3
/
0
7
11
/
1
3
/
0
7
12
/
1
3
/
0
7
01
/
1
3
/
0
8
02
/
1
3
/
0
8
03
/
1
3
/
0
8
04
/
1
3
/
0
8
05
/
1
3
/
0
8
06
/
1
3
/
0
8
07
/
1
3
/
0
8
08
/
1
3
/
0
8
09
/
1
3
/
0
8
10
/
1
3
/
0
8
11
/
1
3
/
0
8
12
/
1
3
/
0
8
01
/
1
3
/
0
9
02
/
1
3
/
0
9
03
/
1
3
/
0
9
04
/
1
3
/
0
9
05
/
1
3
/
0
9
06
/
1
3
/
0
9
07
/
1
3
/
0
9
08
/
1
3
/
0
9
09
/
1
3
/
0
9
10
/
1
3
/
0
9
11
/
1
3
/
0
9
12
/
1
3
/
0
9
01
/
1
3
/
1
0
02
/
1
3
/
1
0
Mea
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐25 Water Depth Over Time (ft. blmp)
40.0
45.0
50.0
55.0
60.0
65.0
09
/
1
3
/
0
7
10
/
1
3
/
0
7
11
/
1
3
/
0
7
12
/
1
3
/
0
7
01
/
1
3
/
0
8
02
/
1
3
/
0
8
03
/
1
3
/
0
8
04
/
1
3
/
0
8
05
/
1
3
/
0
8
06
/
1
3
/
0
8
07
/
1
3
/
0
8
08
/
1
3
/
0
8
09
/
1
3
/
0
8
10
/
1
3
/
0
8
11
/
1
3
/
0
8
12
/
1
3
/
0
8
01
/
1
3
/
0
9
02
/
1
3
/
0
9
03
/
1
3
/
0
9
04
/
1
3
/
0
9
05
/
1
3
/
0
9
06
/
1
3
/
0
9
07
/
1
3
/
0
9
08
/
1
3
/
0
9
09
/
1
3
/
0
9
10
/
1
3
/
0
9
11
/
1
3
/
0
9
12
/
1
3
/
0
9
01
/
1
3
/
1
0
02
/
1
3
/
1
0
De
p
t
h
 Be
l
o
w
 Me
a
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐25 Water Depth Over Time (ft. blmp)

Tab G
Depths to Groundwater and Elevations Over Time for Groundwater Monitoring Wells

Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,620.77 5,622.33 1.56 123.6
5,527.63 09/25/79 94.70 93.14
5,527.63 10/10/79 94.70 93.14
5,528.43 01/10/80 93.90 92.34
5,529.93 03/20/80 92.40 90.84
5,528.03 06/17/80 94.30 92.74
5,528.03 09/15/80 94.30 92.74
5,527.93 10/08/80 94.40 92.84
5,527.93 02/12/81 94.40 92.84
5,525.93 09/01/84 96.40 94.84
5,528.33 12/01/84 94.00 92.44
5,528.13 02/01/85 94.20 92.64
5,528.33 06/01/85 94.00 92.44
5,528.93 09/01/85 93.40 91.84
5,528.93 10/01/85 93.40 91.84
5,528.93 11/01/85 93.40 91.84
5,528.83 12/01/85 93.50 91.94
5,512.33 03/01/86 110.00 108.44
5,528.91 06/19/86 93.42 91.86
5,528.83 09/01/86 93.50 91.94
5,529.16 12/01/86 93.17 91.61
5,526.66 02/20/87 95.67 94.11
5 529 16 04/28/87 93 17 91 61
Water Levels and Data over Time
White Mesa Mill - Well MW4
5,529.16 04/28/87 93.17 91.61
5,529.08 08/14/87 93.25 91.69
5,529.00 11/20/87 93.33 91.77
5,528.75 01/26/88 93.58 92.02
5,528.91 06/01/88 93.42 91.86
5,528.25 08/23/88 94.08 92.52
5,529.00 11/02/88 93.33 91.77
5,528.33 03/09/89 94.00 92.44
5,529.10 06/21/89 93.23 91.67
5,529.06 09/01/89 93.27 91.71
5,529.21 11/15/89 93.12 91.56
5,529.22 02/16/90 93.11 91.55
5,529.43 05/08/90 92.90 91.34
5,529.40 08/07/90 92.93 91.37
5,529.53 11/13/90 92.80 91.24
5,529.86 02/27/91 92.47 90.91
5,529.91 05/21/91 92.42 90.86
5,529.77 08/27/91 92.56 91.00
5,529.79 12/03/91 92.54 90.98
5,530.13 03/17/92 92.20 90.64
5,529.85 06/11/92 92.48 90.92
5,529.90 09/13/92 92.43 90.87
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,620.77 5,622.33 1.56 123.6
Water Levels and Data over Time
White Mesa Mill - Well MW4
5,529.92 12/09/92 92.41 90.85
5,530.25 03/24/93 92.08 90.52
5,530.20 06/08/93 92.13 90.57
5,530.19 09/22/93 92.14 90.58
5,529.75 12/14/93 92.58 91.02
5,530.98 03/24/94 91.35 89.79
5,531.35 06/15/94 90.98 89.42
5,531.62 08/18/94 90.71 89.15
5,532.58 12/13/94 89.75 88.19
5,533.42 03/16/95 88.91 87.35
5,534.70 06/27/95 87.63 86.07
5,535.44 09/20/95 86.89 85.33
5,537.16 12/11/95 85.17 83.61
5,538.37 03/28/96 83.96 82.40
5,539.10 06/07/96 83.23 81.67
5,539.13 09/16/96 83.20 81.64
5,542.29 03/20/97 80.04 78.48
5,551.58 04/07/99 70.75 69.19
5,552.08 05/11/99 70.25 68.69
5,552.83 07/06/99 69.50 67.94
5,553.47 09/28/99 68.86 67.30
5 554 63 01/03/00 67 70 66 145,554.63 01/03/00 67.70 66.14
5,555.13 04/04/00 67.20 65.64
5,555.73 05/02/00 66.60 65.04
5,556.03 05/11/00 66.30 64.74
5,555.73 05/15/00 66.60 65.04
5,555.98 05/25/00 66.35 64.79
5,556.05 06/09/00 66.28 64.72
5,556.18 06/16/00 66.15 64.59
5,556.05 06/26/00 66.28 64.72
5,556.15 07/06/00 66.18 64.62
5,556.18 07/13/00 66.15 64.59
5,556.17 07/18/00 66.16 64.60
5,556.26 07/25/00 66.07 64.51
5,556.35 08/02/00 65.98 64.42
5,556.38 08/09/00 65.95 64.39
5,556.39 08/15/00 65.94 64.38
5,556.57 08/31/00 65.76 64.20
5,556.68 09/08/00 65.65 64.09
5,556.73 09/13/00 65.60 64.04
5,556.82 09/20/00 65.51 63.95
5,556.84 09/29/00 65.49 63.93
5,556.81 10/05/00 65.52 63.96
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,620.77 5,622.33 1.56 123.6
Water Levels and Data over Time
White Mesa Mill - Well MW4
5,556.89 10/12/00 65.44 63.88
5,556.98 10/19/00 65.35 63.79
5,557.01 10/23/00 65.32 63.76
5,557.14 11/09/00 65.19 63.63
5,557.17 11/14/00 65.16 63.60
5,556.95 11/21/00 65.38 63.82
5,557.08 11/30/00 65.25 63.69
5,557.55 12/07/00 64.78 63.22
5,557.66 01/14/01 64.67 63.11
5,557.78 02/09/01 64.55 62.99
5,558.28 03/29/01 64.05 62.49
5,558.23 04/30/01 64.10 62.54
5,558.31 05/31/01 64.02 62.46
5,558.49 06/22/01 63.84 62.28
5,558.66 07/10/01 63.67 62.11
5,559.01 08/20/01 63.32 61.76
5,559.24 09/19/01 63.09 61.53
5,559.26 10/02/01 63.07 61.51
5,559.27 11/08/01 63.06 61.50
5,559.77 12/03/01 62.56 61.00
5,559.78 01/03/02 62.55 60.99
5 559 96 02/06/02 62 37 60 815,559.96 02/06/02 62.37 60.81
5,560.16 03/26/02 62.17 60.61
5,560.28 04/09/02 62.05 60.49
5,560.76 05/23/02 61.57 60.01
5,560.58 06/05/02 61.75 60.19
5,560.43 07/08/02 61.90 60.34
5,560.44 08/23/02 61.89 60.33
5,560.71 09/11/02 61.62 60.06
5,560.89 10/23/02 61.44 59.88
5,557.86 11/22/02 64.47 62.91
5,561.10 12/03/02 61.23 59.67
5,561.39 01/09/03 60.94 59.38
5,561.41 02/12/03 60.92 59.36
5,561.93 03/26/03 60.40 58.84
5,561.85 04/02/03 60.48 58.92
5,536.62 05/01/03 85.71 84.15
5,528.56 06/09/03 93.77 92.21
5,535.28 07/07/03 87.05 85.49
5,534.44 08/04/03 87.89 86.33
5,537.10 09/11/03 85.23 83.67
5,539.96 10/02/03 82.37 80.81
5,535.91 11/07/03 86.42 84.86
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,620.77 5,622.33 1.56 123.6
Water Levels and Data over Time
White Mesa Mill - Well MW4
5,550.70 12/03/03 71.63 70.07
5,557.58 01/15/04 64.75 63.19
5,558.80 02/10/04 63.53 61.97
5,560.08 03/28/04 62.25 60.69
5,560.55 04/12/04 61.78 60.22
5,561.06 05/13/04 61.27 59.71
5,561.48 06/18/04 60.85 59.29
5,561.86 07/28/04 60.47 58.91
5,529.17 08/30/04 93.16 91.60
5,536.55 09/16/04 85.78 84.22
5,529.00 10/11/04 93.33 91.77
5,541.55 11/16/04 80.78 79.22
5,541.12 12/22/04 81.21 79.65
5,540.59 01/18/05 81.74 80.18
5,542.85 02/28/05 79.48 77.92
5,537.91 03/15/05 84.42 82.86
5,548.67 04/26/05 73.66 72.10
5,549.53 05/24/05 72.80 71.24
5,544.36 06/30/05 77.97 76.41
5,545.16 07/29/05 77.17 75.61
5,544.67 09/12/05 77.66 76.10
5 541 28 09/27/05 81 05 79 495,541.28 09/27/05 81.0579.49
5,536.96 12/07/05 85.37 83.81
5,546.49 03/08/06 75.84 74.28
5,546.15 06/13/06 76.18 74.62
5,545.15 07/18/06 77.18 75.62
5,545.91 11/17/06 76.42 74.86
5,545.90 02/27/07 76.43 74.87
5,548.16 05/02/07 74.17 72.61
5,547.20 08/13/07 75.13 73.57
5,547.20 10/10/07 75.13 73.57
5,547.79 03/26/08 74.54 72.98
5,545.09 06/25/08 77.24 75.68
5,550.36 08/26/08 71.97 70.41
5,550.39 10/14/08 71.94 70.38
5,542.25 03/03/09 80.08 78.52
5,542.25 06/24/09 80.08 78.52
5,550.19 09/10/09 72.14 70.58
5,550.94 12/11/09 71.39 69.83
5,546.08 03/11/10 76.25 74.69
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
z 5,620.77 5,622.33 1.02 111.04
5,540.98 11/08/99 81.35 80.33
5,541.13 11/09/99 81.20 80.18
5,541.23 01/02/00 81.10 80.08
5,541.23 01/10/00 81.10 80.08
5,540.98 01/17/00 81.35 80.33
5,541.03 01/24/00 81.30 80.28
5,541.03 02/01/00 81.30 80.28
5,540.93 02/07/00 81.40 80.38
5,541.23 02/14/00 81.10 80.08
5,541.23 02/23/00 81.10 80.08
5,541.33 03/01/00 81.00 79.98
5,541.43 03/08/00 80.90 79.88
5,541.73 03/15/00 80.60 79.58
5,541.43 03/20/00 80.90 79.88
5,541.43 03/29/00 80.90 79.88
5,541.18 04/04/00 81.15 80.13
5,540.93 04/13/00 81.40 80.38
5,541.23 04/21/00 81.10 80.08
5,541.43 04/28/00 80.90 79.88
5,541.33 05/01/00 81.00 79.98
5,541.63 05/11/00 80.70 79.68
5 541 33 05/15/00 81 00 79 98
Water Levels and Data over Time
White Mesa Mill - Well TW4-1
5,541.33 05/15/00 81.00 79.98
5,541.63 05/25/00 80.70 79.68
5,541.63 06/09/00 80.70 79.68
5,541.65 06/16/00 80.68 79.66
5,541.63 06/26/00 80.70 79.68
5,541.85 07/06/00 80.48 79.46
5,541.79 07/13/00 80.54 79.52
5,541.91 07/18/00 80.42 79.40
5,542.17 07/27/00 80.16 79.14
5,542.31 08/02/00 80.02 79.00
5,542.43 08/09/00 79.90 78.88
5,542.41 08/15/00 79.92 78.90
5,542.08 08/31/00 80.25 79.23
5,542.93 09/01/00 79.40 78.38
5,542.87 09/08/00 79.46 78.44
5,543.09 09/13/00 79.24 78.22
5,543.25 09/20/00 79.08 78.06
5,543.44 10/05/00 78.89 77.87
5,544.08 11/09/00 78.25 77.23
5,544.49 12/06/00 77.84 76.82
5,546.14 01/14/01 76.19 75.17
5,547.44 02/02/01 74.89 73.87
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
z 5,620.77 5,622.33 1.02 111.04
Water Levels and Data over Time
White Mesa Mill - Well TW4-1
5,548.71 03/29/01 73.62 72.60
5,549.20 04/30/01 73.13 72.11
5,549.64 05/31/01 72.69 71.67
5,549.94 06/22/01 72.39 71.37
5,550.25 07/10/01 72.08 71.06
5,550.93 08/10/01 71.40 70.38
5,551.34 09/19/01 70.99 69.97
5,551.59 10/02/01 70.74 69.72
5,549.64 05/31/01 72.69 71.67
5,549.94 06/21/01 72.39 71.37
5,550.25 07/10/01 72.08 71.06
5,550.93 08/20/01 71.40 70.38
5,551.34 09/19/01 70.99 69.97
5,551.59 10/02/01 70.74 69.72
5,551.87 11/08/01 70.46 69.44
5,552.40 12/03/01 69.93 68.91
5,552.62 01/03/02 69.71 68.69
5,553.12 02/06/02 69.21 68.19
5,553.75 03/26/02 68.58 67.56
5,553.97 04/09/02 68.36 67.34
5,554.56 05/23/02 67.77 66.75
5 554 54 06/05/02 67 79 66 775,554.54 06/05/02 67.79 66.77
5,554.83 07/08/02 67.50 66.48
5,555.29 08/23/02 67.04 66.02
5,555.54 09/11/02 66.79 65.77
5,555.94 10/23/02 66.39 65.37
5,556.02 11/22/02 66.31 65.29
5,556.23 12/03/02 66.10 65.08
5,556.49 01/09/03 65.84 64.82
5,556.67 02/12/03 65.66 64.64
5,557.15 03/26/03 65.18 64.16
5,557.23 04/02/03 65.10 64.08
5,556.07 05/01/03 66.26 65.24
5,554.28 06/09/03 68.05 67.03
5,553.84 07/07/03 68.49 67.47
5,553.39 08/04/03 68.94 67.92
5,553.06 09/11/03 69.27 68.25
5,553.33 10/02/03 69.00 67.98
5,553.25 11/07/03 69.08 68.06
5,553.82 12/03/03 68.51 67.49
5,555.61 01/15/04 66.72 65.70
5,556.32 02/10/04 66.01 64.99
5,557.38 03/28/04 64.95 63.93
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
z 5,620.77 5,622.33 1.02 111.04
Water Levels and Data over Time
White Mesa Mill - Well TW4-1
5,557.79 04/12/04 64.54 63.52
5,558.35 05/13/04 63.98 62.96
5,560.03 06/18/04 62.30 61.28
5,560.36 07/28/04 61.97 60.95
5,557.96 08/30/04 64.37 63.35
5,557.24 09/16/04 65.09 64.07
5,556.28 10/11/04 66.05 65.03
5,556.17 11/16/04 66.16 65.14
5,556.21 12/22/04 66.12 65.10
5,555.82 01/18/05 66.51 65.49
5,555.96 02/28/05 66.37 65.35
5,556.01 03/15/05 66.32 65.30
5,556.05 04/26/05 66.28 65.26
5,556.00 05/24/05 66.33 65.31
5,555.97 06/30/05 66.36 65.34
5,555.90 07/29/05 66.43 65.41
5,556.22 09/12/05 66.11 65.09
5,556.25 12/07/05 66.08 65.06
5,556.71 03/08/06 65.62 64.60
5,556.98 06/14/06 65.35 64.33
5,560.95 07/18/06 61.38 60.36
5 557 07 11/07/06 65 26 64 245,557.07 11/07/06 65.26 64.24
5,558.10 02/27/07 64.23 63.21
5,557.82 05/02/07 64.51 63.49
5,557.82 08/14/07 64.51 63.49
5,557.63 10/10/07 64.70 63.68
5,559.48 03/26/08 62.85 61.83
5,560.35 06/24/08 61.98 60.96
5,560.58 08/26/08 61.75 60.73
5,560.62 10/14/08 61.71 60.69
5,560.65 03/10/09 61.68 60.66
5,560.66 06/24/09 61.67 60.65
5,560.36 09/10/09 61.97 60.95
5,560.53 12/11/09 61.8 60.78
5,560.50 03/11/10 61.83 60.81
Water
Elevation
(z)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,623.10 5,625.00 1.90 121.125
5,548.85 11/08/99 76.15 74.25
5,548.85 11/09/99 76.15 74.25
5,548.60 01/02/00 76.40 74.50
5,548.80 01/10/00 76.20 74.30
5,548.60 01/17/00 76.40 74.50
5,549.00 01/24/00 76.00 74.10
5,548.90 02/01/00 76.10 74.20
5,548.90 02/07/00 76.10 74.20
5,549.30 02/14/00 75.70 73.80
5,549.40 02/23/00 75.60 73.70
5,549.50 03/01/00 75.50 73.60
5,549.60 03/08/00 75.40 73.50
5,549.50 03/15/00 75.50 73.60
5,550.20 03/20/00 74.80 72.90
5,550.00 03/29/00 75.00 73.10
5,549.70 04/04/00 75.30 73.40
5,549.80 04/13/00 75.20 73.30
5,550.00 04/21/00 75.00 73.10
5,550.10 04/28/00 74.90 73.00
5,550.10 05/01/00 74.90 73.00
5,550.40 05/11/00 74.60 72.70
5 550 10 05/15/00 74 90 73 00
Water Levels and Data over Time
White Mesa Mill - Well TW4-2
5,550.10 05/15/00 74.90 73.00
5,550.40 05/25/00 74.60 72.70
5,550.40 06/09/00 74.60 72.70
5,550.50 06/16/00 74.50 72.60
5,550.35 06/26/00 74.65 72.75
5,550.45 07/06/00 74.55 72.65
5,550.45 07/13/00 74.55 72.65
5,550.46 07/18/00 74.54 72.64
5,550.61 07/27/00 74.39 72.49
5,550.66 08/02/00 74.34 72.44
5,550.68 08/09/00 74.32 72.42
5,550.70 08/15/00 74.30 72.40
5,550.82 08/31/00 74.18 72.28
5,551.15 09/08/00 73.85 71.95
5,551.25 09/13/00 73.75 71.85
5,551.32 09/20/00 73.68 71.78
5,546.11 10/05/00 78.89 76.99
5,546.75 11/09/00 78.25 76.35
5,547.16 12/06/00 77.84 75.94
5,552.46 01/26/01 72.54 70.64
5,552.48 02/02/01 72.52 70.62
5,551.38 03/29/01 73.62 71.72
Water
Elevation
(z)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,623.10 5,625.00 1.90 121.125
Water Levels and Data over Time
White Mesa Mill - Well TW4-2
5,551.87 04/30/01 73.13 71.23
5,552.31 05/31/01 72.69 70.79
5,552.61 06/21/01 72.39 70.49
5,552.92 07/10/01 72.08 70.18
5,553.60 08/20/01 71.40 69.50
5,554.01 09/19/01 70.99 69.09
5,554.26 10/02/01 70.74 68.84
5,554.42 11/08/01 70.58 68.68
5,555.07 12/03/01 69.93 68.03
5,555.02 01/03/02 69.98 68.08
5,555.19 02/06/02 69.81 67.91
5,555.43 03/26/02 69.57 67.67
5,555.67 04/09/02 69.33 67.43
5,556.01 05/23/02 68.99 67.09
5,556.07 06/05/02 68.93 67.03
5,556.19 07/08/02 68.81 66.91
5,556.32 08/23/02 68.68 66.78
5,556.53 09/11/02 68.47 66.57
5,557.00 10/23/02 68.00 66.10
5,556.70 11/22/02 68.30 66.40
5,557.29 12/03/02 67.71 65.81
5 557 48 01/09/03 67 52 65 625,557.48 01/09/03 67.52 65.62
5,557.63 02/12/03 67.37 65.47
5,558.11 03/26/03 66.89 64.99
5,558.15 04/02/03 66.85 64.95
5,553.99 05/01/03 71.01 69.11
5,549.26 06/09/03 75.74 73.84
5,548.42 07/07/03 76.58 74.68
5,548.03 08/04/03 76.97 75.07
5,547.50 09/11/03 77.50 75.60
5,547.96 10/02/03 77.04 75.14
5,547.80 11/07/03 77.20 75.30
5,548.57 12/03/03 76.43 74.53
5,554.28 01/15/04 70.72 68.82
5,555.74 02/10/04 69.26 67.36
5,557.18 03/28/04 67.82 65.92
5,557.77 04/12/04 67.23 65.33
5,558.35 05/13/04 66.65 64.75
5,558.47 06/18/04 66.53 64.63
5,559.28 07/28/04 65.72 63.82
5,554.54 08/30/04 70.46 68.56
5,552.25 09/16/04 72.75 70.85
5,549.93 10/11/04 75.07 73.17
Water
Elevation
(z)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,623.10 5,625.00 1.90 121.125
Water Levels and Data over Time
White Mesa Mill - Well TW4-2
5,550.17 11/16/04 74.83 72.93
5,550.65 12/22/04 74.35 72.45
5,550.23 01/18/05 74.77 72.87
5,550.37 02/28/05 74.63 72.73
5,550.41 03/15/05 74.59 72.69
5,550.46 04/26/05 74.54 72.64
5,550.60 05/24/05 74.40 72.50
5,550.49 06/30/05 74.51 72.61
5,550.39 07/29/05 74.61 72.71
5,550.61 09/12/05 74.39 72.49
5,550.57 12/07/05 74.43 72.53
5,551.58 03/08/06 73.42 71.52
5,551.70 *06/14/06 73.3 71.40
5,550.80 07/18/06 74.20 72.30
5550.80 11/07/06 74.20 72.30
5553.17 02/27/07 71.83 69.93
5,552.34 05/02/07 72.66 70.76
5,552.30 08/14/07 72.7 70.80
5,552.48 10/10/07 72.52 70.62
5,554.86 03/26/08 70.14 68.24
5,555.51 06/24/08 69.49 67.59
5 555 57 08/26/08 69 43 67 535,555.57 08/26/08 69.43 67.53
5,555.71 10/14/08 69.29 67.39
5,556.01 03/10/09 68.99 67.09
5,556.53 06/24/09 68.47 66.57
5,556.22 09/10/09 68.78 66.88
5,556.81 12/11/09 68.19 66.29
5,558.15 03/11/10 66.85 64.95
Water
Elevation
(z)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,631.21 5,632.23 1.02 141
5,565.78 11/29/99 66.45 65.43
5,566.93 01/02/00 65.30 64.28
5,567.03 01/10/00 65.20 64.18
5,566.83 01/17/00 65.40 64.38
5,567.13 01/24/00 65.10 64.08
5,567.33 02/01/00 64.90 63.88
5,567.13 02/07/00 65.10 64.08
5,567.43 02/14/00 64.80 63.78
5,567.63 02/23/00 64.60 63.58
5,567.73 03/01/00 64.50 63.48
5,567.83 03/08/00 64.40 63.38
5,567.70 03/15/00 64.53 63.51
5,568.03 03/20/00 64.20 63.18
5,567.93 03/29/00 64.30 63.28
5,567.63 04/04/00 64.60 63.58
5,567.83 04/13/00 64.40 63.38
5,568.03 04/21/00 64.20 63.18
5,568.23 04/28/00 64.00 62.98
5,568.13 05/01/00 64.10 63.08
5,568.53 05/11/00 63.70 62.68
5,568.23 05/15/00 64.00 62.98
5 568 53 05/25/00 63 70 62 68
Water Levels and Data over Time
White Mesa Mill - Well TW4-3
5,568.53 05/25/00 63.70 62.68
5,568.61 06/09/00 63.62 62.60
5,568.69 06/16/00 63.54 62.52
5,568.45 06/26/00 63.78 62.76
5,568.61 07/06/00 63.62 62.60
5,568.61 07/06/00 63.62 62.60
5,568.49 07/13/00 63.74 62.72
5,568.55 07/18/00 63.68 62.66
5,568.65 07/27/00 63.58 62.56
5,568.73 08/02/00 63.50 62.48
5,568.77 08/09/00 63.46 62.44
5,568.76 08/16/00 63.47 62.45
5,568.95 08/31/00 63.28 62.26
5,568.49 09/08/00 63.74 62.72
5,568.67 09/13/00 63.56 62.54
5,568.96 09/20/00 63.27 62.25
5,568.93 10/05/00 63.3 62.28
5,569.34 11/09/00 62.89 61.87
5,568.79 12/06/00 63.44 62.42
5,569.11 01/03/01 63.12 62.10
5,569.75 02/09/01 62.48 61.46
5,570.34 03/28/01 61.89 60.87
Water
Elevation
(z)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,631.21 5,632.23 1.02 141
Water Levels and Data over Time
White Mesa Mill - Well TW4-3
5,570.61 04/30/01 61.62 60.60
5,570.70 05/31/01 61.53 60.51
5,570.88 06/21/01 61.35 60.33
5,571.02 07/10/01 61.21 60.19
5,571.70 08/20/01 60.53 59.51
5,572.12 09/19/01 60.11 59.09
5,572.08 10/02/01 60.15 59.13
5,570.70 05/31/01 61.53 60.51
5,570.88 06/21/01 61.35 60.33
5,571.02 07/10/01 61.21 60.19
5,571.70 08/20/01 60.53 59.51
5,572.12 09/19/01 60.11 59.09
5,572.08 10/02/01 60.15 59.13
5,572.78 11/08/01 59.45 58.43
5,573.27 12/03/01 58.96 57.94
5,573.47 01/03/02 58.76 57.74
5,573.93 02/06/02 58.30 57.28
5,574.75 03/26/02 57.48 56.46
5,574.26 04/09/02 57.97 56.95
5,575.39 05/23/02 56.84 55.82
5,574.84 06/05/02 57.39 56.37
5 575 33 07/08/02 56 90 55 885,575.33 07/08/02 56.90 55.88
5,575.79 08/23/02 56.44 55.42
5,576.08 09/11/02 56.15 55.13
5,576.30 10/23/02 55.93 54.91
5,576.35 11/22/02 55.88 54.86
5,576.54 12/03/02 55.69 54.67
5,576.96 01/09/03 55.27 54.25
5,577.11 02/12/03 55.12 54.10
5,577.61 03/26/03 54.62 53.60
5,572.80 04/02/03 59.43 58.41
5,577.89 05/01/03 54.34 53.32
5,577.91 06/09/03 54.32 53.30
5,577.53 07/07/03 54.70 53.68
5,577.50 08/04/03 54.73 53.71
5,577.71 09/11/03 54.52 53.50
5,577.31 10/02/03 54.92 53.90
5,577.33 11/07/03 54.90 53.88
5,577.34 12/03/03 54.89 53.87
5,578.24 01/15/04 53.99 52.97
5,578.38 02/10/04 53.85 52.83
5,578.69 03/28/04 53.54 52.52
5,579.15 04/12/04 53.08 52.06
Water
Elevation
(z)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,631.21 5,632.23 1.02 141
Water Levels and Data over Time
White Mesa Mill - Well TW4-3
5,579.47 05/13/04 52.76 51.74
5,579.53 06/18/04 52.70 51.68
5,580.17 07/28/04 52.06 51.04
5,580.20 08/30/04 52.03 51.01
5,580.26 09/16/04 51.97 50.95
5,580.12 10/11/04 52.11 51.09
5,579.93 11/16/04 52.30 51.28
5,580.07 12/22/04 52.16 51.14
5,579.80 01/18/05 52.43 51.41
5,580.35 02/28/05 51.88 50.86
5,580.57 03/15/05 51.66 50.64
5,580.86 04/26/05 51.37 50.35
5,581.20 05/24/05 51.03 50.01
5,581.51 06/30/05 50.72 49.70
5,581.55 07/29/05 50.68 49.66
5,581.68 09/12/05 50.55 49.53
5,581.83 12/07/05 50.4 49.38
5,564.92 03/08/06 67.31 66.29
5,582.73 06/13/06 49.50 48.48
5,582.33 07/18/06 49.90 48.88
5,582.75 11/07/06 49.48 48.46
5583 35 02/27/07 48 88 47 865583.35 02/27/07 48.88 47.86
5,559.57 05/02/07 72.66 71.64
5,583.29 08/14/07 48.94 47.92
5,583.49 10/10/07 48.74 47.72
5,584.95 03/26/08 47.28 46.26
5,584.59 06/24/08 47.64 46.62
5,584.55 08/26/08 47.68 46.66
5,584.03 10/14/08 48.2 47.18
5,583.64 03/03/09 48.59 47.57
5,587.34 06/24/09 44.89 43.87
5,582.90 09/10/09 49.33 48.31
5,583.27 12/11/09 48.96 47.94
5,583.63 03/11/10 48.6 47.58
Water
Elevation
(z)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,612.301 5,613.485 1.184 114.5
5,512.145 05/25/00 101.34 100.16
5,518.985 06/09/00 94.50 93.32
5,512.145 06/16/00 101.34 100.16
5,517.465 06/26/00 96.02 94.84
5,520.145 07/06/00 93.34 92.16
5,521.435 07/13/00 92.05 90.87
5,522.005 07/18/00 91.48 90.30
5,522.945 07/27/00 90.54 89.36
5,523.485 08/02/00 90.00 88.82
5,523.845 08/09/00 89.64 88.46
5,523.885 08/15/00 89.60 88.42
5,524.555 09/01/00 88.93 87.75
5,513.235 09/08/00 100.25 99.07
5,516.665 09/13/00 96.82 95.64
5,519.085 09/20/00 94.40 93.22
5,522.165 10/05/00 91.32 90.14
5,524.665 11/09/00 88.82 87.64
5,518.545 12/06/00 94.94 93.76
5,527.695 01/03/01 85.79 84.61
5,529.085 02/09/01 84.40 83.22
5,529.535 03/27/01 83.95 82.77
5 530 235 04/30/01 83 25 82 07
Water Levels and Data over Time
White Mesa Mill - Well TW4-4
5,530.235 04/30/01 83.25 82.07
5,530.265 05/31/01 83.22 82.04
5,534.405 06/22/01 79.08 77.90
5,533.145 07/10/01 80.34 79.16
5,534.035 08/20/01 79.45 78.27
5,534.465 09/19/01 79.02 77.84
5,533.285 10/02/01 80.20 79.02
5,530.265 05/31/01 83.22 82.04
5,534.405 06/21/01 79.08 77.90
5,533.145 07/10/01 80.34 79.16
5,534.035 08/20/01 79.45 78.27
5,534.465 09/19/01 79.02 77.84
5,533.285 10/02/01 80.20 79.02
5,533.865 11/08/01 79.62 78.44
5,534.275 12/03/01 79.21 78.03
5,534.715 01/03/02 78.77 77.59
5,535.435 02/06/02 78.05 76.87
5,536.445 03/26/02 77.04 75.86
5,536.405 04/09/02 77.08 75.90
5,537.335 05/23/02 76.15 74.97
5,537.325 06/05/02 76.16 74.98
5,537.975 07/08/02 75.51 74.33
Water
Elevation
(z)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,612.301 5,613.485 1.184 114.5
Water Levels and Data over Time
White Mesa Mill - Well TW4-4
5,538.825 08/23/02 74.66 73.48
5,539.275 09/11/02 74.21 73.03
5,539.765 10/23/02 73.72 72.54
5,540.205 11/22/02 73.28 72.10
5,540.295 12/03/02 73.19 72.01
5,540.795 01/09/03 72.69 71.51
5,540.985 02/12/03 72.50 71.32
5,541.675 03/26/03 71.81 70.63
5,541.765 04/02/03 71.72 70.54
5,541.885 05/01/03 71.60 70.42
5,542.025 06/09/03 71.46 70.28
5,541.925 07/07/03 71.56 70.38
5,541.885 08/04/03 71.60 70.42
5,541.825 09/11/03 71.66 70.48
5,541.885 10/02/03 71.60 70.42
5,541.995 11/07/03 71.49 70.31
5,542.005 12/03/03 71.48 70.30
5,542.555 01/15/04 70.93 69.75
5,542.705 02/10/04 70.78 69.60
5,543.225 03/28/04 70.26 69.08
5,543.555 04/12/04 69.93 68.75
5 543 865 05/13/04 69 62 68 445,543.865 05/13/04 69.62 68.44
5,543.915 06/18/04 69.57 68.39
5,544.655 07/28/04 68.83 67.65
5,544.795 08/30/04 68.69 67.51
5,544.845 09/16/04 68.64 67.46
5,544.705 10/11/04 68.78 67.60
5,544.525 11/16/04 68.96 67.78
5,544.625 12/22/04 68.86 67.68
5,544.305 01/18/05 69.18 68.00
5,544.585 02/28/05 68.90 67.72
5,544.685 03/15/05 68.80 67.62
5,544.675 04/26/05 68.81 67.63
5,544.785 05/24/05 68.70 67.52
5,544.795 06/30/05 68.69 67.51
5,544.775 07/29/05 68.71 67.53
5,545.005 09/12/05 68.48 67.30
5,545.225 12/07/05 68.26 67.08
5,545.735 03/08/06 67.75 66.57
5,545.785 06/14/06 67.70 66.52
5,545.855 07/18/06 67.63 66.45
5,545.805 11/07/06 67.68 66.50
5546.675 02/27/07 66.81 65.63
Water
Elevation
(z)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,612.301 5,613.485 1.184 114.5
Water Levels and Data over Time
White Mesa Mill - Well TW4-4
5,546.535 05/02/07 66.95 65.77
5,547.155 08/15/07 66.33 65.15
5,547.215 10/10/07 66.27 65.09
5,548.305 03/26/08 65.18 64.00
5,548.865 06/24/08 64.62 63.44
5,549.235 08/26/08 64.25 63.07
5,549.305 10/14/08 64.18 63.00
5,549.725 03/03/09 63.76 62.58
5,549.905 06/24/09 63.58 62.40
5,549.695 09/10/09 63.79 62.61
5,549.865 12/11/09 63.62 62.44
5,545.60 03/11/10 67.89 66.71
Water
Elevation
(z)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,638.75 5,640.70 1.95 121.75
5,579.30 01/02/00 61.40 59.45
5,579.60 01/10/00 61.10 59.15
5,579.35 01/17/00 61.35 59.40
5,579.60 01/24/00 61.10 59.15
5,579.50 02/01/00 61.20 59.25
5,579.50 02/07/00 61.20 59.25
5,579.90 02/14/00 60.80 58.85
5,579.90 02/23/00 60.80 58.85
5,580.20 03/01/00 60.50 58.55
5,580.00 03/08/00 60.70 58.75
5,580.04 03/15/00 60.66 58.71
5,580.70 03/20/00 60.00 58.05
5,580.30 03/29/00 60.40 58.45
5,580.00 04/04/00 60.70 58.75
5,580.20 04/13/00 60.50 58.55
5,580.40 04/21/00 60.30 58.35
5,580.50 04/28/00 60.20 58.25
5,580.50 05/01/00 60.20 58.25
5,580.90 05/11/00 59.80 57.85
5,580.50 05/15/00 60.20 58.25
5,580.75 05/25/00 59.95 58.00
5 580 80 06/09/00 59 90 57 95
Water Levels and Data over Time
White Mesa Mill - Well TW4-5
5,580.80 06/09/00 59.90 57.95
5,580.92 06/16/00 59.78 57.83
5,580.80 06/26/00 59.90 57.95
5,580.90 07/06/00 59.80 57.85
5,581.05 07/13/00 59.65 57.70
5,580.90 07/18/00 59.80 57.85
5,581.05 07/27/00 59.65 57.70
5,581.06 08/02/00 59.64 57.69
5,581.08 08/09/00 59.62 57.67
5,581.07 08/16/00 59.63 57.68
5,581.25 08/31/00 59.45 57.50
5,581.32 09/08/00 59.38 57.43
5,581.34 09/13/00 59.36 57.41
5,581.41 09/20/00 59.29 57.34
5,581.37 10/05/00 59.33 57.38
5,581.66 11/09/00 59.04 57.09
5,581.63 12/06/00 59.07 57.12
5,581.92 01/03/01 58.78 56.83
5,582.20 02/09/01 58.50 56.55
5,582.54 03/28/01 58.16 56.21
5,582.72 04/30/01 57.98 56.03
5,582.72 05/31/01 57.98 56.03
Water
Elevation
(z)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,638.75 5,640.70 1.95 121.75
Water Levels and Data over Time
White Mesa Mill - Well TW4-5
5,582.81 06/22/01 57.89 55.94
5,582.92 07/10/01 57.78 55.83
5,583.17 08/20/01 57.53 55.58
5,583.28 09/19/01 57.42 55.47
5,583.36 10/02/01 57.34 55.39
5,582.72 05/31/01 57.98 56.03
5,582.81 06/21/01 57.89 55.94
5,582.92 07/10/01 57.78 55.83
5,583.17 08/20/01 57.53 55.58
5,583.28 09/19/01 57.42 55.47
5,583.36 10/02/01 57.34 55.39
5,583.49 11/08/01 57.21 55.26
5,583.84 12/03/01 56.86 54.91
5,583.79 01/03/02 56.91 54.96
5,583.96 02/06/02 56.74 54.79
5,584.39 03/26/02 56.31 54.36
5,584.12 04/09/02 56.58 54.63
5,584.55 05/23/02 56.15 54.20
5,584.42 06/05/02 56.28 54.33
5,583.65 07/08/02 57.05 55.10
5,584.90 08/23/02 55.80 53.85
5 585 02 09/11/02 55 68 53 735,585.02 09/11/02 55.68 53.73
5,585.20 10/23/02 55.50 53.55
5,585.15 11/22/02 55.55 53.60
5,585.42 12/03/02 55.28 53.33
5,585.65 01/09/03 55.05 53.10
5,585.65 02/12/03 55.05 53.10
5,585.92 03/26/03 54.78 52.83
5,586.22 04/02/03 54.48 52.53
5,586.01 05/01/03 54.69 52.74
5,584.81 06/09/03 55.89 53.94
5,584.34 07/07/03 56.36 54.41
5,584.40 08/04/03 56.30 54.35
5,583.88 09/11/03 56.82 54.87
5,583.57 10/02/03 57.13 55.18
5,583.39 11/07/03 57.31 55.36
5,583.97 12/03/03 56.73 54.78
5,585.28 01/15/04 55.42 53.47
5,585.50 02/10/04 55.20 53.25
5,585.87 03/28/04 54.83 52.88
5,586.20 04/12/04 54.50 52.55
5,586.45 05/13/04 54.25 52.30
5,586.50 06/18/04 54.20 52.25
Water
Elevation
(z)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,638.75 5,640.70 1.95 121.75
Water Levels and Data over Time
White Mesa Mill - Well TW4-5
5,587.13 07/28/04 53.57 51.62
5,586.22 08/30/04 54.48 52.53
5,585.69 09/16/04 55.01 53.06
5,585.17 10/11/04 55.53 53.58
5,584.64 11/16/04 56.06 54.11
5,584.77 12/22/04 55.93 53.98
5,584.65 01/18/05 56.05 54.10
5,584.98 02/28/05 55.72 53.77
5,585.15 03/15/05 55.55 53.60
5,586.25 04/26/05 54.45 52.50
5,586.79 05/24/05 53.91 51.96
5,586.52 06/30/05 54.18 52.23
5,586.03 07/29/05 54.67 52.72
5,586.05 09/12/05 54.65 52.70
5,585.80 12/07/05 54.90 52.95
5,587.06 03/08/06 53.64 51.69
5,585.90 06/13/06 54.80 52.85
5,585.32 07/18/06 55.38 53.43
5,585.35 11/07/06 55.35 53.40
5585.81 02/27/07 54.89 52.94
5,585.20 05/02/07 55.50 53.55
5 586 66 08/14/07 54 04 52 095,586.66 08/14/0754.04 52.09
5,586.80 10/10/07 53.90 51.95
5,588.48 03/26/08 52.22 50.27
5,586.51 06/24/08 54.19 52.24
5,586.45 08/26/08 54.25 52.30
5,585.40 10/14/08 55.3 53.35
5,584.80 03/03/09 55.9 53.95
5,584.73 06/24/09 55.97 54.02
5,584.36 09/10/09 56.34 54.39
5,585.02 12/11/09 55.68 53.73
5,585.66 03/11/10 55.04 53.09
Water
Elevation
(z)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
(blw.LSD)
5,607.33 5,608.78 1.450 98.55
5,522.28 05/25/00 86.50 85.05
5,521.51 06/09/00 87.27 85.82
5,522.35 06/16/00 86.43 84.98
5,522.14 06/26/00 86.64 85.19
5,522.25 07/06/00 86.53 85.08
5,522.13 07/13/00 86.65 85.20
5,522.17 07/18/00 86.61 85.16
5,522.26 07/25/00 86.52 85.07
5,522.31 08/02/00 86.47 85.02
5,522.33 08/09/00 86.45 85.00
5,522.35 08/15/00 86.43 84.98
5,522.40 08/31/00 86.38 84.93
5,522.40 09/08/00 86.38 84.93
5,522.45 09/13/00 86.33 84.88
5,522.53 09/20/00 86.25 84.80
5,522.39 10/05/00 86.39 84.94
5,522.42 11/09/00 86.36 84.91
5,522.29 12/06/00 86.49 85.04
5,522.63 01/03/01 86.15 84.70
5,522.72 02/09/01 86.06 84.61
5,522.90 03/26/01 85.88 84.43
5 522 70 04/30/01 86 08 84 63
Water Levels and Data over Time
White Mesa Mill - Well TW4-6
5,522.70 04/30/01 86.08 84.63
5,522.89 05/31/01 85.89 84.44
5,522.88 06/20/01 85.90 84.45
5,522.96 07/10/01 85.82 84.37
5,523.10 08/20/01 85.68 84.23
5,523.23 09/19/01 85.55 84.10
5,523.21 10/02/01 85.57 84.12
5,522.89 05/31/01 85.89 84.44
5,522.88 06/21/01 85.90 84.45
5,522.96 07/10/01 85.82 84.37
5,523.10 08/20/01 85.68 84.23
5,523.23 09/19/01 85.55 84.10
5,523.21 10/02/01 85.57 84.12
5,523.25 11/08/01 85.53 84.08
5,523.46 12/03/01 85.32 83.87
5,523.36 01/03/02 85.42 83.97
5,523.50 02/06/02 85.28 83.83
5,523.94 03/26/02 84.84 83.39
5,523.75 04/09/02 85.03 83.58
5,524.23 05/23/02 84.55 83.10
5,523.98 06/05/02 84.80 83.35
5,524.31 07/08/02 84.47 83.02
Water
Elevation
(z)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
(blw.LSD)
5,607.33 5,608.78 1.450 98.55
Water Levels and Data over Time
White Mesa Mill - Well TW4-6
5,524.36 08/23/02 84.42 82.97
5,524.49 09/11/02 84.29 82.84
5,524.71 10/23/02 84.07 82.62
5,524.60 11/22/02 84.18 82.73
5,524.94 12/03/02 83.84 82.39
5,525.10 01/09/03 83.68 82.23
5,525.15 02/12/03 83.63 82.18
5,525.35 03/26/03 83.43 81.98
5,525.68 04/02/03 83.10 81.65
5,525.74 05/01/03 83.04 81.59
5,525.98 06/09/03 82.80 81.35
5,526.04 07/07/03 82.74 81.29
5,526.07 08/04/03 82.71 81.26
5,526.42 09/11/03 82.36 80.91
5,526.30 10/02/03 82.48 81.03
5,526.41 11/07/03 82.37 80.92
5,526.46 12/03/03 82.32 80.87
5,526.83 01/15/04 81.95 80.50
5,526.81 02/10/04 81.97 80.52
5,527.14 03/28/04 81.64 80.19
5,527.39 04/12/04 81.39 79.94
5 527 64 05/13/04 81 14 79 695,527.64 05/13/04 81.14 79.69
5,527.70 06/18/04 81.08 79.63
5,528.16 07/28/04 80.62 79.17
5,528.30 08/30/04 80.48 79.03
5,528.52 09/16/04 80.26 78.81
5,528.71 10/11/04 80.07 78.62
5,528.74 11/16/04 80.04 78.59
5,529.20 12/22/04 79.58 78.13
5,528.92 01/18/05 79.86 78.41
5,529.51 02/28/05 79.27 77.82
5,529.74 03/15/05 79.04 77.59
5,529.96 04/26/05 78.82 77.37
5,530.15 05/24/05 78.63 77.18
5,530.35 06/30/05 78.43 76.98
5,530.47 07/29/05 78.31 76.86
5,530.95 09/12/05 77.83 76.38
5,531.50 12/07/05 77.28 75.83
5,532.43 03/08/06 76.35 74.90
5,533.49 06/13/06 75.29 73.84
5,532.58 07/18/06 76.20 74.75
5,532.88 11/07/06 75.90 74.45
5534.09 02/27/07 74.69 73.24
Water
Elevation
(z)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
(blw.LSD)
5,607.33 5,608.78 1.450 98.55
Water Levels and Data over Time
White Mesa Mill - Well TW4-6
5,534.04 05/02/07 74.74 73.29
5,534.43 08/14/07 74.35 72.90
5,554.54 10/10/07 54.24 52.79
5,535.40 03/26/08 73.38 71.93
5,535.55 06/24/08 73.23 71.78
5,535.90 08/26/08 72.88 71.43
5,535.87 10/14/08 72.91 71.46
5,536.42 03/10/09 72.36 70.91
5,536.71 06/24/09 72.07 70.62
5,536.83 09/10/09 71.95 70.50
5,537.35 12/11/09 71.43 69.98
5,537.93 03/11/10 70.85 69.40
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total Depth
Of Well
(blw.LSD)
5,619.87 5,621.07 1.20 119.8
5,552.37 11/29/99 68.70 67.50
5,553.57 01/02/00 67.50 66.30
5,553.87 01/10/00 67.20 66.00
5,553.72 01/17/00 67.35 66.15
5,553.97 01/24/00 67.10 65.90
5,553.87 02/01/00 67.20 66.00
5,553.87 02/07/00 67.20 66.00
5,554.17 02/14/00 66.90 65.70
5,554.27 02/23/00 66.80 65.60
5,554.37 03/01/00 66.70 65.50
5,554.37 03/08/00 66.70 65.50
5,554.27 03/15/00 66.80 65.60
5,554.77 03/20/00 66.30 65.10
5,554.57 03/29/00 66.50 65.30
5,554.27 04/04/00 66.80 65.60
5,554.57 04/13/00 66.50 65.30
5,554.77 04/21/00 66.30 65.10
5,554.87 04/28/00 66.20 65.00
5,554.87 05/01/00 66.20 65.00
5,555.27 05/11/00 65.80 64.60
5,554.97 05/15/00 66.10 64.90
5 555 27 05/25/00 65 80 64 60
Water Levels and Data over Time
White Mesa Mill - Well TW4-7
5,555.27 05/25/00 65.80 64.60
5,555.33 06/09/00 65.74 64.54
5,555.45 06/16/00 65.62 64.42
5,555.22 06/26/00 65.85 64.65
5,555.45 07/06/00 65.62 64.42
5,555.40 07/13/00 65.67 64.47
5,555.45 07/18/00 65.62 64.42
5,555.59 07/27/00 65.48 64.28
5,555.65 08/02/00 65.42 64.22
5,555.70 08/09/00 65.37 64.17
5,555.74 08/16/00 65.33 64.13
5,555.96 08/31/00 65.11 63.91
5,555.87 09/08/00 65.20 64.00
5,555.95 09/13/00 65.12 63.92
5,556.05 09/20/00 65.02 63.82
5,556.06 10/05/00 65.01 63.81
5,556.17 10/12/00 64.90 63.70
5,556.20 10/19/00 64.87 63.67
5,556.22 10/23/00 64.85 63.65
5,556.36 11/09/00 64.71 63.51
5,556.42 11/14/00 64.65 63.45
5,556.45 11/30/00 64.62 63.42
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total Depth
Of Well
(blw.LSD)
5,619.87 5,621.07 1.20 119.8
Water Levels and Data over Time
White Mesa Mill - Well TW4-7
5,556.15 12/06/00 64.92 63.72
5,556.89 01/14/01 64.18 62.98
5,557.07 02/09/01 64.00 62.80
5,557.62 03/29/01 63.45 62.25
5,557.51 04/30/01 63.56 62.36
5,557.77 05/31/01 63.30 62.10
5,557.84 06/21/01 63.23 62.03
5,557.98 07/10/01 63.09 61.89
5,558.33 08/20/01 62.74 61.54
5,558.57 09/19/01 62.50 61.30
5,558.53 10/02/01 62.54 61.34
5,558.62 11/08/01 62.45 61.25
5,559.03 12/03/01 62.04 60.84
5,559.08 01/03/02 61.99 60.79
5,559.32 02/06/02 61.75 60.55
5,559.63 03/26/02 61.44 60.24
5,559.55 04/09/02 61.52 60.32
5,560.06 05/23/02 61.01 59.81
5,559.91 06/05/02 61.16 59.96
5,560.09 07/08/02 60.98 59.78
5,560.01 08/23/02 61.06 59.86
5 560 23 09/11/02 60 84 59 645,560.23 09/11/02 60.84 59.64
5,560.43 10/23/02 60.64 59.44
5,560.39 11/22/02 60.68 59.48
5,560.61 12/03/02 60.46 59.26
5,560.89 01/09/03 60.18 58.98
5,560.94 02/12/03 60.13 58.93
5,561.28 03/26/03 59.79 58.59
5,561.35 04/02/03 59.72 58.52
5,546.20 05/01/03 74.87 73.67
5,539.47 06/09/03 81.60 80.40
5,541.87 07/07/03 79.20 78.00
5,542.12 08/04/03 78.95 77.75
5,541.91 09/11/03 79.16 77.96
5,544.62 10/02/03 76.45 75.25
5,542.67 11/07/03 78.40 77.20
5,549.96 12/03/03 71.11 69.91
5,557.17 01/15/04 63.90 62.70
5,558.65 02/10/04 62.42 61.22
5,559.90 03/28/04 61.17 59.97
5,560.36 04/12/04 60.71 59.51
5,560.87 05/13/04 60.20 59.00
5,560.95 06/18/04 60.12 58.92
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total Depth
Of Well
(blw.LSD)
5,619.87 5,621.07 1.20 119.8
Water Levels and Data over Time
White Mesa Mill - Well TW4-7
5,561.64 07/28/04 59.43 58.23
5,543.00 08/30/04 78.07 76.87
5,541.91 09/16/04 79.16 77.96
5,540.08 10/11/04 80.99 79.79
5,546.92 11/16/04 74.15 72.95
5,546.97 12/22/04 74.10 72.90
5,546.51 01/18/05 74.56 73.36
5,546.66 02/28/05 74.41 73.21
5,546.81 03/15/05 74.26 73.06
5,548.19 04/26/05 72.88 71.68
5,547.11 05/24/05 73.96 72.76
5,546.98 06/30/05 74.09 72.89
5,546.92 07/29/05 74.15 72.95
5,547.26 09/12/05 73.81 72.61
5,547.26 12/07/05 73.81 72.61
5,548.86 03/08/06 72.21 71.01
5,548.62 06/13/06 72.45 71.25
5,550.04 07/18/06 71.03 69.83
5,548.32 11/07/06 72.75 71.55
5,550.44 02/27/07 70.63 69.43
5,549.69 05/02/07 71.38 70.18
5 549 97 08/14/07 71 10 69 905,549.97 08/14/07 71.10 69.90
5,550.30 10/10/07 70.77 69.57
5,551.92 03/26/08 69.15 67.95
5,552.94 06/24/08 68.13 66.93
5,552.34 08/26/08 68.73 67.53
5,552.61 10/14/08 68.46 67.26
5,552.81 03/10/09 68.26 67.06
5,553.11 06/24/09 67.96 66.76
5,552.55 09/10/09 68.52 67.32
5,553.06 12/11/09 68.01 66.81
5,554.64 03/11/10 66.43 65.23
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total Depth
to Water
(blw.LSD)
Total
Depth Of
Well
5,616.80 5,618.21 1.41 126.00
5,543.21 11/29/1999 75.00 73.59
5,543.01 01/02/2000 75.20 73.79
5,543.31 01/10/2000 74.90 73.49
5,543.11 01/17/2000 75.10 73.69
5,543.41 01/24/2000 74.80 73.39
5,543.31 02/01/2000 74.90 73.49
5,543.31 02/07/2000 74.90 73.49
5,543.71 02/14/2000 74.50 73.09
5,543.76 02/23/2000 74.45 73.04
5,543.86 03/01/2000 74.35 72.94
5,543.86 03/08/2000 74.35 72.94
5,543.91 03/15/2000 74.30 72.89
5,544.31 03/20/2000 73.90 72.49
5,544.21 03/29/2000 74.00 72.59
5,544.01 04/04/2000 74.20 72.79
5,544.21 04/13/2000 74.00 72.59
5,544.41 04/21/2000 73.80 72.39
5,544.51 04/28/2000 73.70 72.29
5,544.51 05/01/2000 73.70 72.29
5,544.81 05/11/2000 73.40 71.99
5,544.51 05/15/2000 73.70 72.29
5 544 71 05/25/2000 73 50 72 09
Water Levels and Data over Time
White Mesa Mill - Well TW4-8
5,544.71 05/25/2000 73.50 72.09
5,544.71 06/09/2000 73.50 72.09
5,544.81 06/16/2000 73.40 71.99
5,544.68 06/26/2000 73.53 72.12
5,544.76 07/06/2000 73.45 72.04
5,544.77 07/13/2000 73.44 72.03
5,544.76 07/18/2000 73.45 72.04
5,544.92 07/27/2000 73.29 71.88
5,544.96 08/02/2000 73.25 71.84
5,544.98 08/09/2000 73.23 71.82
5,544.97 08/15/2000 73.24 71.83
5,545.21 08/31/2000 73.00 71.59
5,545.31 09/08/2000 72.90 71.49
5,545.43 09/13/2000 72.78 71.37
5,545.56 09/20/2000 72.65 71.24
5,545.57 10/05/2000 72.64 71.23
5,545.81 11/09/2000 72.40 70.99
5,545.66 12/06/2000 72.55 71.14
5,546.28 01/03/2001 71.93 70.52
5,546.70 02/09/2001 71.51 70.10
5,547.18 03/27/2001 71.03 69.62
5,547.31 04/30/2001 70.90 69.49
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total Depth
to Water
(blw.LSD)
Total
Depth Of
Well
5,616.80 5,618.21 1.41 126.00
Water Levels and Data over Time
White Mesa Mill - Well TW4-8
5,547.49 05/31/2001 70.72 69.31
5,547.49 06/20/2001 70.72 69.31
5,547.83 07/10/2001 70.38 68.97
5,548.13 08/20/2001 70.08 68.67
5,548.30 09/19/2001 69.91 68.50
5,548.45 10/02/2001 69.76 68.35
5,547.49 05/31/2001 70.72 69.31
5,547.54 06/21/2001 70.67 69.26
5,547.83 07/10/2001 70.38 68.97
5,548.13 08/20/2001 70.08 68.67
5,548.30 09/19/2001 69.91 68.50
5,548.45 10/02/2001 69.76 68.35
5,548.62 11/08/2001 69.59 68.18
5,549.03 12/03/2001 69.18 67.77
5,548.97 01/03/2002 69.24 67.83
5,549.19 02/06/2002 69.02 67.61
5,549.66 03/26/2002 68.55 67.14
5,549.64 04/09/2002 68.57 67.16
5,550.01 05/23/2002 68.20 66.79
5,549.97 06/05/2002 68.24 66.83
5,550.13 07/08/2002 68.08 66.67
5 550 30 08/23/2002 67 91 66 505,550.30 08/23/2002 67.91 66.50
5,550.50 09/11/2002 67.71 66.30
5,550.90 10/23/2002 67.31 65.90
5,550.83 11/22/2002 67.38 65.97
5,551.04 12/03/2002 67.17 65.76
5,551.24 01/09/2003 66.97 65.56
5,551.23 02/12/2003 66.98 65.57
5,551.52 03/26/2003 66.69 65.28
5,551.64 04/02/2003 66.57 65.16
5,549.02 05/01/2003 69.19 67.78
5,544.74 06/09/2003 73.47 72.06
5,543.78 07/07/2003 74.43 73.02
5,543.39 08/04/2003 74.82 73.41
5,543.05 09/11/2003 75.16 73.75
5,543.19 10/02/2003 75.02 73.61
5,543.21 11/07/2003 75.00 73.59
5,543.40 12/03/2003 74.81 73.40
5,548.10 01/15/2004 70.11 68.70
5,549.50 02/10/2004 68.71 67.30
5,550.87 03/28/2004 67.34 65.93
5,551.33 04/12/2004 66.88 65.47
5,551.87 05/13/2004 66.34 64.93
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total Depth
to Water
(blw.LSD)
Total
Depth Of
Well
5,616.80 5,618.21 1.41 126.00
Water Levels and Data over Time
White Mesa Mill - Well TW4-8
5,551.92 06/18/2004 66.29 64.88
5,552.69 07/28/2004 65.52 64.11
5,549.78 08/30/2004 68.43 67.02
5,547.46 09/16/2004 70.75 69.34
5,545.21 10/11/2004 73.00 71.59
5,545.09 11/16/2004 73.12 71.71
5,545.61 12/22/2004 72.60 71.19
5,545.24 01/18/2005 72.97 71.56
5,545.42 02/28/2005 72.79 71.38
5,545.45 03/15/2005 72.76 71.35
5,545.46 04/26/2005 72.75 71.34
5,545.66 05/24/2005 72.55 71.14
5,545.54 06/30/2005 72.67 71.26
5,545.43 07/29/2005 72.78 71.37
5,545.61 09/12/2005 72.60 71.19
5,545.52 12/07/2005 72.69 71.28
5,546.53 03/08/2006 71.68 70.27
5,546.51 06/13/2006 71.70 70.29
5,546.51 07/18/2006 71.70 70.29
5,546.46 11/07/2006 71.75 70.34
5,547.92 02/27/2007 70.29 68.88
5 547 01 05/02/2007 71 20 69 795,547.01 05/02/200771.20 69.79
5,547.40 08/14/2007 70.81 69.40
5,547.57 10/10/2007 70.64 69.23
5,548.76 03/26/2008 69.45 68.04
5,549.17 06/24/2008 69.04 67.63
5,549.31 08/26/2008 68.9 67.49
5,549.37 10/14/2008 68.84 67.43
5,549.72 03/03/2009 68.49 67.08
5,550.08 06/24/2009 68.13 66.72
5,549.93 09/10/2009 68.28 66.87
5,550.44 12/11/2009 67.77 66.36
5,551.46 03/11/2010 66.75 65.34
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,636.11 5,637.59 1.48 121.33
5,577.09 12/20/1999 60.5 59.02
5,577.09 01/02/2000 60.5 59.02
5,577.29 01/10/2000 60.3 58.82
5,577.09 01/17/2000 60.5 59.02
5,577.39 01/24/2000 60.2 58.72
5,577.29 02/01/2000 60.3 58.82
5,577.19 02/07/2000 60.4 58.92
5,577.69 02/14/2000 59.9 58.42
5,577.69 02/23/2000 59.9 58.42
5,577.79 03/01/2000 59.8 58.32
5,577.79 03/08/2000 59.8 58.32
5,577.89 03/15/2000 59.7 58.22
5,568.49 03/20/2000 69.1 67.62
5,578.14 03/29/2000 59.45 57.97
5,577.84 04/04/2000 59.75 58.27
5,578.04 04/13/2000 59.55 58.07
5,578.24 04/21/2000 59.35 57.87
5,578.39 04/28/2000 59.2 57.72
5,578.39 05/01/2000 59.2 57.72
5,578.79 05/11/2000 58.8 57.32
5,578.39 05/15/2000 59.2 57.72
5 578 79 05/25/2000 58 8 57 32
Water Levels and Data over Time
White Mesa Mill - Well TW4-9
5,578.79 05/25/2000 58.8 57.32
5,578.81 06/09/2000 58.78 57.30
5,578.89 06/16/2000 58.7 57.22
5,578.74 06/26/2000 58.85 57.37
5,578.86 07/06/2000 58.73 57.25
5,578.87 07/13/2000 58.72 57.24
5,578.84 07/18/2000 58.75 57.27
5,579.03 07/27/2000 58.56 57.08
5,579.03 08/02/2000 58.56 57.08
5,579.05 08/09/2000 58.54 57.06
5,579.04 08/15/2000 58.55 57.07
5,579.25 08/31/2000 58.34 56.86
5,579.35 09/08/2000 58.24 56.76
5,579.40 09/13/2000 58.19 56.71
5,579.46 09/20/2000 58.13 56.65
5,579.44 10/05/2000 58.15 56.67
5,579.79 11/09/2000 57.8 56.32
5,579.73 12/06/2000 57.86 56.38
5,580.01 01/03/2001 57.58 56.10
5,580.30 02/09/2001 57.29 55.81
5,580.66 03/27/2001 56.93 55.45
5,580.75 04/30/2001 56.84 55.36
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,636.11 5,637.59 1.48 121.33
Water Levels and Data over Time
White Mesa Mill - Well TW4-9
5,581.04 05/31/2001 56.55 55.07
5,581.12 06/21/2001 56.47 54.99
5,581.15 07/10/2001 56.44 54.96
5,581.51 08/20/2001 56.08 54.60
5,581.70 09/19/2001 55.89 54.41
5,581.61 10/02/2001 55.98 54.50
5,581.04 05/31/2001 56.55 55.07
5,581.12 06/21/2001 56.47 54.99
5,581.15 07/10/2001 56.44 54.96
5,581.51 08/20/2001 56.08 54.60
5,581.70 09/19/2001 55.89 54.41
5,581.61 10/02/2001 55.98 54.50
5,581.83 11/08/2001 55.76 54.28
5,582.17 12/03/2001 55.42 53.94
5,582.21 01/03/2002 55.38 53.90
5,582.57 02/06/2002 55.02 53.54
5,583.12 03/26/2002 54.47 52.99
5,582.77 04/09/2002 54.82 53.34
5,583.21 05/23/2002 54.38 52.90
5,582.94 06/05/2002 54.65 53.17
5,582.71 07/08/2002 54.88 53.40
5 583 67 08/23/2002 53 92 52 445,583.67 08/23/2002 53.92 52.44
5,583.82 09/11/2002 53.77 52.29
5,584.01 10/23/2002 53.58 52.10
5,583.88 11/22/2002 53.71 52.23
5,583.81 12/03/2002 53.78 52.30
5,584.28 01/09/2003 53.31 51.83
5,584.41 02/12/2003 53.18 51.70
5,584.68 03/26/2003 52.91 51.43
5,584.49 04/02/2003 53.10 51.62
5,584.51 05/01/2003 53.08 51.60
5,583.59 06/09/2003 54.00 52.52
5,582.96 07/07/2003 54.63 53.15
5,582.98 08/04/2003 54.61 53.13
5,582.57 09/11/2003 55.02 53.54
5,582.25 10/02/2003 55.34 53.86
5,582.09 11/07/2003 55.50 54.02
5,582.48 12/03/2003 55.11 53.63
5,583.69 01/15/2004 53.90 52.42
5,583.89 02/10/2004 53.70 52.22
5,584.30 03/28/2004 53.29 51.81
5,584.59 04/12/2004 53.00 51.52
5,584.87 05/13/2004 52.72 51.24
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,636.11 5,637.59 1.48 121.33
Water Levels and Data over Time
White Mesa Mill - Well TW4-9
5,584.96 06/18/2004 52.63 51.15
5,585.50 07/28/2004 52.09 50.61
5,584.81 08/30/2004 52.78 51.30
5,584.40 09/16/2004 53.19 51.71
5,583.91 10/11/2004 53.68 52.20
5,583.39 11/16/2004 54.20 52.72
5,583.54 12/22/2004 54.05 52.57
5,583.34 01/18/2005 54.25 52.77
5,583.66 02/28/2005 53.93 52.45
5,583.87 03/15/2005 53.72 52.24
5,584.74 04/26/2005 52.85 51.37
5,585.26 05/24/2005 52.33 50.85
5,585.06 06/30/2005 52.53 51.05
5,584.67 07/29/2005 52.92 51.44
5,584.75 09/12/2005 52.84 51.36
5,584.51 12/07/2005 53.08 51.60
5,585.74 03/08/2006 51.85 50.37
5,584.74 06/13/2006 52.85 51.37
5,584.26 07/18/2006 53.33 51.85
5,584.21 11/07/2006 53.38 51.90
5,584.67 02/27/2007 52.92 51.44
5 584 06 05/02/2007 53 53 52 055,584.06 05/02/200753.53 52.05
5,585.33 08/14/2007 52.26 50.78
5,585.42 10/10/2007 52.17 50.69
5,587.01 03/26/2008 50.58 49.10
5,585.44 06/24/2008 52.15 50.67
5,585.23 08/26/2008 52.36 50.88
5,584.42 10/14/2008 53.17 51.69
5,583.59 03/03/2009 54 52.52
5,583.35 06/24/2009 54.24 52.76
5,582.91 09/10/2009 54.68 53.20
5,583.43 12/11/2009 54.16 52.68
5,584.00 03/11/2010 53.59 52.11
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total Depth
to Water
(blw.LSD)
Total
Depth Of
Well
5,631.99 5,634.24 2.25 121.33
5,576.75 01/03/2002 57.49 55.24
5,576.92 02/06/2002 57.32 55.07
5,577.43 03/26/2002 56.81 54.56
5,577.22 04/09/2002 57.02 54.77
5,577.80 05/23/2002 56.44 54.19
5,577.47 06/05/2002 56.77 54.52
5,577.55 07/08/2002 56.69 54.44
5,578.10 08/23/2002 56.14 53.89
5,578.24 09/11/2002 56.00 53.75
5,578.49 10/23/2002 55.75 53.50
5,578.43 11/22/2002 55.81 53.56
5,578.43 12/03/2002 55.81 53.56
5,578.66 01/09/2003 55.58 53.33
5,578.66 02/12/2003 55.58 53.33
5,578.78 03/26/2003 55.46 53.21
5,578.90 04/02/2003 55.34 53.09
5,578.83 05/01/2003 55.41 53.16
5,578.05 06/09/2003 56.19 53.94
5,577.38 07/07/2003 56.86 54.61
5,577.15 08/04/2003 57.09 54.84
5,576.76 09/11/2003 57.48 55.23
5 576 36 10/02/2003 57 88 55 63
Water Levels and Data over Time
White Mesa Mill - Well TW4-10
5,576.36 10/02/2003 57.88 55.63
5,576.05 11/07/2003 58.19 55.94
5,576.20 12/03/2003 58.04 55.79
5,577.43 01/15/2004 56.81 54.56
5,577.81 02/10/2004 56.43 54.18
5,578.47 03/28/2004 55.77 53.52
5,578.69 04/12/2004 55.55 53.30
5,578.93 05/13/2004 55.31 53.06
5,578.99 06/18/2004 55.25 53.00
5,579.18 07/28/2004 55.06 52.81
5,579.06 08/30/2004 55.18 52.93
5,578.78 09/16/2004 55.46 53.21
5,577.80 10/11/2004 56.44 54.19
5,577.13 11/16/2004 57.11 54.86
5,576.96 12/22/2004 57.28 55.03
5,576.63 01/18/2005 57.61 55.36
5,576.82 02/28/2005 57.42 55.17
5,576.86 03/15/2005 57.38 55.13
5,577.52 04/26/2005 56.72 54.47
5,578.01 05/24/2005 56.23 53.98
5,578.15 06/30/2005 56.09 53.84
5,577.90 07/29/2005 56.34 54.09
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total Depth
to Water
(blw.LSD)
Total
Depth Of
Well
5,631.99 5,634.24 2.25 121.33
Water Levels and Data over Time
White Mesa Mill - Well TW4-10
5,578.02 09/12/2005 56.22 53.97
5,577.56 12/07/2005 56.68 54.43
5,579.69 03/08/2006 54.55 52.30
5,578.34 06/13/2006 55.90 53.65
5,577.94 07/18/2006 56.30 54.05
5,578.01 11/07/2006 56.23 53.98
5578.43 02/27/2007 55.81 53.56
5,577.84 05/02/2007 56.40 54.15
5,578.74 08/14/2007 55.50 53.25
5,579.04 10/10/2007 55.20 52.95
5,580.69 03/26/2008 53.55 51.30
5,579.87 06/24/2008 54.37 52.12
5,579.47 08/26/2008 54.77 52.52
5,578.87 10/14/2008 55.37 53.12
5,578.01 03/10/2009 56.23 53.98
5,577.85 06/24/2009 56.39 54.14
5,577.49 09/10/2009 56.75 54.50
5,577.98 12/11/2009 56.26 54.01
5,578.38 03/11/2010 55.86 53.61
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,621.92 5,623.62 1.70 121.33
5,548.32 1/3/2002 75.30 73.60
5,548.73 2/6/2002 74.89 73.19
5,549.03 3/26/2002 74.59 72.89
5,548.84 4/9/2002 74.78 73.08
5,549.30 5/23/2002 74.32 72.62
5,549.01 6/5/2002 74.61 72.91
5,549.22 7/8/2002 74.40 72.70
5,549.44 8/23/2002 74.18 72.48
5,549.57 9/11/2002 74.05 72.35
5,549.64 10/23/2002 73.98 72.28
5,549.58 11/22/2002 74.04 72.34
5,549.62 12/3/2002 74.00 72.30
5,549.85 1/9/2003 73.77 72.07
5,549.91 2/12/2003 73.71 72.01
5,550.15 3/26/2003 73.47 71.77
5,550.01 4/2/2003 73.61 71.91
5,550.31 5/1/2003 73.31 71.61
5,550.44 6/9/2003 73.18 71.48
5,550.33 7/7/2003 73.29 71.59
5,550.35 8/4/2003 73.27 71.57
5,550.44 9/11/2003 73.18 71.48
5 550 47 10/2/2003 73 15 71 45
Water Levels and Data over Time
White Mesa Mill - Well TW4-11
5,550.47 10/2/2003 73.15 71.45
5,550.60 11/7/2003 73.02 71.32
5,550.60 12/3/2003 73.02 71.32
5,550.94 1/15/2004 72.68 70.98
5,551.00 2/10/2004 72.62 70.92
5,550.34 3/28/2004 73.28 71.58
5,551.54 4/12/2004 72.08 70.38
5,551.89 5/13/2004 71.73 70.03
5,551.94 6/18/2004 71.68 69.98
5,552.49 7/28/2004 71.13 69.43
5,552.74 8/30/2004 70.88 69.18
5,553.01 9/16/2004 70.61 68.91
5,553.11 10/11/2004 70.51 68.81
5,553.19 11/16/2004 70.43 68.73
5,553.53 12/22/2004 70.09 68.39
5,553.31 1/18/2005 70.31 68.61
5,553.84 2/28/2005 69.78 68.08
5,554.04 3/15/2005 69.58 67.88
5,554.23 4/26/2005 69.39 67.69
5,553.87 5/24/2005 69.75 68.05
5,554.46 6/30/2005 69.16 67.46
5,554.57 7/29/2005 69.05 67.35
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,621.92 5,623.62 1.70 121.33
Water Levels and Data over Time
White Mesa Mill - Well TW4-11
5,553.86 9/12/2005 69.76 68.06
5,555.30 12/7/2005 68.32 66.62
5,556.20 3/8/2006 67.42 65.72
5,556.48 6/14/2006 67.14 65.44
5,556.37 7/18/2006 67.25 65.55
5,556.94 11/7/2006 66.68 64.98
5557.92 2/27/2007 65.7 64
5,557.84 5/2/2007 65.78 64.08
5,558.02 8/15/2007 65.60 63.90
5,557.13 10/10/2007 66.49 64.79
5,569.74 3/26/2008 53.88 52.18
5,561.01 6/24/2008 62.61 60.91
5,562.07 8/26/2008 61.55 59.85
5,562.47 10/14/2008 61.15 59.45
5,563.80 3/10/2009 59.82 58.12
5,564.27 6/24/2009 59.35 57.65
5,564.32 9/10/2009 59.3 57.60
5,564.70 12/11/2009 58.92 57.22
5,565.14 3/11/2010 58.48 56.78
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,622.38 5,624.03 1.65 121.33
5,580.71 8/23/2002 43.32 41.67
5,581.34 9/11/2002 42.69 41.04
5,581.13 10/23/2002 42.90 41.25
5,581.27 11/22/2002 42.76 41.11
5,581.35 12/3/2002 42.68 41.03
5,582.38 1/9/2003 41.65 40.00
5,582.27 2/12/2003 41.76 40.11
5,582.51 3/26/2003 41.52 39.87
5,581.91 4/2/2003 42.12 40.47
5,582.72 5/1/2003 41.31 39.66
5,582.93 6/9/2003 41.10 39.45
5,583.01 7/7/2003 41.02 39.37
5,583.11 8/4/2003 40.92 39.27
5,583.35 9/11/2003 40.68 39.03
5,583.52 10/2/2003 40.51 38.86
5,583.57 11/7/2003 40.46 38.81
5,583.81 12/3/2003 40.22 38.57
5,584.17 1/15/2004 39.86 38.21
5,584.19 2/10/2004 39.84 38.19
5,584.31 3/28/2004 39.72 38.07
5,584.70 4/12/2004 39.33 37.68
Water Levels and Data over Time
White Mesa Mill - Well TW4-12
,.7 //9.7.
5,584.68 5/13/2004 39.35 37.70
5,584.73 6/18/2004 39.30 37.65
5,585.16 7/28/2004 38.87 37.22
5,585.18 8/30/2004 38.85 37.20
5,585.29 9/16/2004 38.74 37.09
5,585.65 10/11/2004 38.38 36.73
5,585.71 11/16/2004 38.32 36.67
5,586.15 12/22/2004 37.88 36.23
5,585.94 1/18/2005 38.09 36.44
5,586.36 2/28/2005 37.67 36.02
5,586.75 3/15/2005 37.28 35.63
5,587.00 4/26/2005 37.03 35.38
5,587.15 5/24/2005 36.88 35.23
5,587.38 6/30/2005 36.65 35.00
5,587.38 7/29/2005 36.65 35.00
5,587.74 9/12/2005 36.29 34.64
5,588.23 12/7/2005 35.80 34.15
5,588.72 3/8/2006 35.31 33.66
5,588.14 6/13/2006 35.89 34.24
5,588.13 7/18/2006 35.90 34.25
5,584.50 11/7/2006 39.53 37.88
5588.65 2/27/2007 35.38 33.73
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,622.38 5,624.03 1.65 121.33
Water Levels and Data over Time
White Mesa Mill - Well TW4-12
5,588.33 5/2/2007 35.70 34.05
5,586.29 8/14/2007 37.74 36.09
5,586.48 10/10/2007 37.55 35.90
5,587.56 3/26/2008 36.47 34.82
5,587.39 6/24/2008 36.64 34.99
5,587.15 8/26/2008 36.88 35.23
5,586.64 10/14/2008 37.39 35.74
5,585.97 3/3/2009 38.06 36.41
5,585.54 6/24/2009 38.49 36.84
5,585.34 9/10/2009 38.69 37.04
5,585.57 12/11/2009 38.46 36.81
5,585.68 03/11/2010 38.35 36.70
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,618.09 5,619.94 1.85 121.33
5,529.66 8/23/2002 90.28 88.43
5,530.66 9/11/2002 89.28 87.43
5,529.10 10/23/2002 90.84 88.99
5,530.58 11/22/2002 89.36 87.51
5,530.61 12/3/2002 89.33 87.48
5,529.74 1/9/2003 90.20 88.35
5,531.03 2/12/2003 88.91 87.06
5,531.82 3/26/2003 88.12 86.27
5,524.63 4/2/2003 95.31 93.46
5,531.54 5/1/2003 88.40 86.55
5,538.46 6/9/2003 81.48 79.63
5,539.38 7/7/2003 80.56 78.71
5,540.72 8/4/2003 79.22 77.37
5,541.25 9/11/2003 78.69 76.84
5,541.34 10/2/2003 78.60 76.75
5,541.69 11/7/2003 78.25 76.40
5,541.91 12/3/2003 78.03 76.18
5,542.44 1/15/2004 77.50 75.65
5,542.47 2/10/2004 77.47 75.62
5,542.84 3/28/2004 77.10 75.25
5,543.08 4/12/2004 76.86 75.01
5 543 34 5/13/2004 76 60 74 75
Water Levels and Data over Time
White Mesa Mill - Well TW4-13
5,543.34 5/13/2004 76.60 74.75
5,543.40 6/18/2004 76.54 74.69
5,544.06 7/28/2004 75.88 74.03
5,544.61 8/30/2004 75.33 73.48
5,545.23 9/16/2004 74.71 72.86
5,546.20 10/11/2004 73.74 71.89
5,547.43 11/16/2004 72.51 70.66
5,548.96 12/22/2004 70.98 69.13
5,549.02 1/18/2005 70.92 69.07
5,550.66 2/28/2005 69.28 67.43
5,551.26 3/15/2005 68.68 66.83
5,552.23 4/26/2005 67.71 65.86
5,552.87 5/24/2005 67.07 65.22
5,553.42 6/30/2005 66.52 64.67
5,554.00 7/29/2005 65.94 64.09
5,555.21 9/12/2005 64.73 62.88
5,558.13 12/7/2005 61.81 59.96
5,562.93 3/8/2006 57.01 55.16
5,564.39 6/13/2006 55.55 53.70
5,562.09 7/18/2006 57.85 56.00
5,565.49 11/7/2006 54.45 52.60
5571.08 2/27/2007 48.86 47.01
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,618.09 5,619.94 1.85 121.33
Water Levels and Data over Time
White Mesa Mill - Well TW4-13
5,570.63 5/2/2007 49.31 47.46
5,565.24 8/14/2007 54.7 52.85
5,565.83 10/10/2007 54.11 52.26
5,569.29 3/26/2008 50.65 48.80
5,570.00 6/24/2008 49.94 48.09
5,570.41 8/26/2008 49.53 47.68
5,570.64 10/14/2008 49.3 47.45
5,570.43 3/3/2009 49.51 47.66
5,570.56 6/24/2009 49.38 47.53
5,570.42 9/10/2009 49.52 47.67
5,571.15 12/11/2009 48.79 46.94
5,572.01 03/11/2010 47.93 46.08
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,610.92 5,612.77 1.85 121.33
5,518.90 8/23/2002 93.87 92.02
5,519.28 9/11/2002 93.49 91.64
5,519.95 10/23/2002 92.82 90.97
5,520.32 11/22/2002 92.45 90.60
5,520.42 12/3/2002 92.35 90.50
5,520.70 1/9/2003 92.07 90.22
5,520.89 2/12/2003 91.88 90.03
5,521.12 3/26/2003 91.65 89.80
5,521.12 4/2/2003 91.65 89.80
5,521.24 5/1/2003 91.53 89.68
5,521.34 6/9/2003 91.43 89.58
5,521.36 7/7/2003 91.41 89.56
5,521.35 8/4/2003 91.42 89.57
5,521.30 9/11/2003 91.47 89.62
5,521.35 10/2/2003 91.42 89.57
5,521.36 11/7/2003 91.41 89.56
5,521.16 12/3/2003 91.61 89.76
5,521.29 1/15/2004 91.48 89.63
5,521.36 2/10/2004 91.41 89.56
5,521.46 3/28/2004 91.31 89.46
5,521.54 4/12/2004 91.23 89.38
5 521 59 5/13/2004 91 18 89 33
Water Levels and Data over Time
White Mesa Mill - Well TW4-14
5,521.59 5/13/2004 91.18 89.33
5,521.69 6/18/2004 91.08 89.23
5,521.71 7/28/2004 91.06 89.21
5,521.76 8/30/2004 91.01 89.16
5,521.77 9/16/2004 91.00 89.15
5,521.79 10/11/2004 90.98 89.13
5,521.80 11/16/2004 90.97 89.12
5,521.82 12/22/2004 90.95 89.10
5,521.82 1/18/2005 90.95 89.10
5,521.86 2/28/2005 90.91 89.06
5,521.85 3/15/2005 90.92 89.07
5,521.91 4/26/2005 90.86 89.01
5,521.93 5/24/2005 90.84 88.99
5,521.94 6/30/2005 90.83 88.98
5,521.84 7/29/2005 90.93 89.08
5,521.99 9/12/2005 90.78 88.93
5,522.04 12/7/2005 90.73 88.88
5,522.05 3/8/2006 90.72 88.87
5,522.27 6/13/2006 90.50 88.65
5,521.92 7/18/2006 90.85 89.00
5,520.17 11/7/2006 92.60 90.75
5522.24 2/27/2007 90.53 88.68
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,610.92 5,612.77 1.85 121.33
Water Levels and Data over Time
White Mesa Mill - Well TW4-14
5,522.47 5/2/2007 90.30 88.45
5,520.74 8/14/2007 92.03 90.18
5,518.13 10/10/2007 94.64 92.79
5,522.85 3/26/2008 89.92 88.07
5,522.91 6/24/2008 89.86 88.01
5,523.01 8/26/2008 89.76 87.91
5,522.96 10/14/2008 89.81 87.96
5,523.20 3/3/2009 89.57 87.72
5,523.33 6/24/2009 89.44 87.59
5,523.47 9/10/2009 89.3 87.45
5,523.54 12/11/2009 89.23 87.38
5,522.98 03/11/2010 89.79 87.94
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,624.15 5,625.45 1.30 121.33
5,574.75 8/23/2002 50.70 49.40 TRUE
5,574.97 9/11/2002 50.48 49.18
5,575.10 10/23/2002 50.35 49.05
5,574.99 11/22/2002 50.46 49.16
5,575.28 12/3/2002 50.17 48.87
5,575.41 1/9/2003 50.04 48.74
5,575.43 2/12/2003 50.02 48.72
5,575.63 3/26/2003 49.82 48.52
5,575.91 4/2/2003 49.54 48.24
5,575.81 5/1/2003 49.64 48.34
5,572.36 6/9/2003 53.09 51.79
5,570.70 7/7/2003 54.75 53.45
5,570.29 8/4/2003 55.16 53.86
5,560.94 9/11/2003 64.51 63.21
5,560.63 10/2/2003 64.82 63.52
5,560.56 11/7/2003 64.89 63.59
5,564.77 12/3/2003 60.68 59.38
5,570.89 1/15/2004 54.56 53.26
5,572.55 2/10/2004 52.90 51.60
5,574.25 3/28/2004 51.20 49.90
5,574.77 4/12/2004 50.68 49.38
5 575 53 5/13/2004 49 92 48 62
Water Levels and Data over Time
White Mesa Mill - Well TW4-15 (MW-26)
5,575.53 5/13/2004 49.92 48.62
5,575.59 6/18/2004 49.86 48.56
5,576.82 7/28/2004 48.63 47.33
5,527.47 9/16/2004 97.98 96.68
5,553.97 11/16/2004 71.48 70.18
5,562.33 12/22/2004 63.12 61.82
5,550.00 1/18/2005 75.45 74.15
5,560.02 4/26/2005 65.43 64.13
5,546.11 5/24/2005 79.34 78.04
5,556.71 6/30/2005 68.74 67.44
5,554.95 7/29/2005 70.50 69.20
5,555.48 9/12/2005 69.97 68.67
5,551.09 12/7/2005 74.36 73.06
5,552.85 3/8/2006 72.60 71.30
5,554.30 6/13/2006 71.15 69.85
5,554.87 7/18/2006 70.58 69.28
5,550.88 11/7/2006 74.57 73.27
5558.77 2/27/2007 66.68 65.38
5,548.54 5/2/2007 76.91 75.61
5,551.33 10/10/2007 74.12 72.82
5,545.56 3/26/2008 79.89 78.59
5,545.56 6/25/2008 79.89 78.59
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,624.15 5,625.45 1.30 121.33
Water Levels and Data over Time
White Mesa Mill - Well TW4-15 (MW-26)
5,545.82 8/26/2008 79.63 78.33
5,545.64 10/14/2008 79.81 78.51
5,544.45 3/3/2009 81.00 79.70
5,545.32 6/24/2009 80.13 78.83
5,544.61 9/10/2009 80.84 79.54
5,549.33 12/11/2009 76.12 74.82
5,543.78 03/11/2010 81.67 80.37
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,622.19 5,624.02 1.83 121.33
5,562.91 8/23/2002 61.11 59.28
5,563.45 9/11/2002 60.57 58.74
5,563.75 10/23/2002 60.27 58.44
5,563.68 11/22/2002 60.34 58.51
5,563.68 12/3/2002 60.34 58.51
5,564.16 1/9/2003 59.86 58.03
5,564.25 2/12/2003 59.77 57.94
5,564.53 3/26/2003 59.49 57.66
5,564.46 4/2/2003 59.56 57.73
5,564.79 5/1/2003 59.23 57.40
5,564.31 6/9/2003 59.71 57.88
5,563.29 7/7/2003 60.73 58.90
5,562.76 8/4/2003 61.26 59.43
5,561.73 9/11/2003 62.29 60.46
5,561.04 10/2/2003 62.98 61.15
5,560.39 11/7/2003 63.63 61.80
5,559.79 12/3/2003 64.23 62.40
5,561.02 1/15/2004 63.00 61.17
5,561.75 2/10/2004 62.27 60.44
5,562.98 3/28/2004 61.04 59.21
5,563.29 4/12/2004 60.73 58.90
5 564 03 5/13/2004 59 99 58 16
Water Levels and Data over Time
White Mesa Mill - Well TW4-16
5,564.03 5/13/2004 59.99 58.16
5,564.09 6/18/2004 59.93 58.10
5,565.08 7/28/2004 58.94 57.11
5,564.56 8/30/2004 59.46 57.63
5,563.55 9/16/2004 60.47 58.64
5,561.79 10/11/2004 62.23 60.40
5,560.38 11/16/2004 63.64 61.81
5,559.71 12/22/2004 64.31 62.48
5,559.14 1/18/2005 64.88 63.05
5,558.65 2/28/2005 65.37 63.54
5,558.54 3/15/2005 65.48 63.65
5,558.22 4/26/2005 65.80 63.97
5,558.54 5/24/2005 65.48 63.65
5,559.24 6/30/2005 64.78 62.95
5,559.38 7/29/2005 64.64 62.81
5,559.23 9/12/2005 64.79 62.96
5,557.67 12/7/2005 66.35 64.52
5,557.92 3/8/2006 66.10 64.27
5,558.47 6/13/2006 65.55 63.72
5,558.42 7/18/2006 65.60 63.77
5,558.09 11/7/2006 65.93 64.10
5557.34 2/27/2007 66.68 64.85
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,622.19 5,624.02 1.83 121.33
Water Levels and Data over Time
White Mesa Mill - Well TW4-16
5,547.11 5/2/2007 76.91 75.08
5,558.52 8/14/2007 65.5 63.67
5,559.02 10/10/2007 65.00 63.17
5,561.04 3/26/2008 62.98 61.15
5,560.06 6/24/2008 63.96 62.13
5,559.32 8/26/2008 64.7 62.87
5,558.89 10/14/2008 65.13 63.30
5,558.40 3/3/2009 65.62 63.79
5,558.32 6/24/2009 65.7 63.87
5,558.03 9/10/2009 65.99 64.16
5,558.81 12/11/2009 65.21 63.38
5,559.80 03/11/2010 64.22 62.39
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,623.41 5,625.24 1.83 121.33
5,542.17 8/23/2002 83.07 81.24
5,542.39 9/11/2002 82.85 81.02
5,542.61 10/23/2002 82.63 80.80
5,542.49 11/22/2002 82.75 80.92
5,542.82 12/3/2002 82.42 80.59
5,543.03 1/9/2003 82.21 80.38
5,543.04 2/12/2003 82.20 80.37
5,543.41 3/26/2003 81.83 80.00
5,543.69 4/2/2003 81.55 79.72
5,543.77 5/1/2003 81.47 79.64
5,544.01 6/9/2003 81.23 79.40
5,544.05 7/7/2003 81.19 79.36
5,543.99 8/4/2003 81.25 79.42
5,544.17 9/11/2003 81.07 79.24
5,544.06 10/2/2003 81.18 79.35
5,544.03 11/7/2003 81.21 79.38
5,543.94 12/3/2003 81.30 79.47
5,543.98 1/15/2004 81.26 79.43
5,543.85 2/10/2004 81.39 79.56
5,544.05 3/28/2004 81.19 79.36
5,544.33 4/12/2004 80.91 79.08
5 544 55 5/13/2004 80 69 78 86
Water Levels and Data over Time
White Mesa Mill - Well TW4-17 (MW-32)
5,544.55 5/13/2004 80.69 78.86
5,544.59 6/18/2004 80.65 78.82
5,545.08 7/28/2004 80.16 78.33
5,545.26 8/30/2004 79.98 78.15
5,545.48 9/16/2004 79.76 77.93
5,545.61 10/11/2004 79.63 77.80
5,545.46 11/16/2004 79.78 77.95
5,545.66 12/22/2004 79.58 77.75
5,545.33 1/18/2005 79.91 78.08
5,545.51 2/28/2005 79.73 77.90
5,545.57 3/15/2005 79.67 77.84
5,545.46 4/26/2005 79.78 77.95
5,545.45 5/24/2005 79.79 77.96
5,545.33 6/30/2005 79.91 78.08
5,545.16 7/29/2005 80.08 78.25
5,545.54 9/12/2005 79.70 77.87
5,545.77 12/7/2005 79.47 77.64
5,546.09 3/8/2006 79.15 77.32
5,545.94 6/13/2006 79.30 77.47
5,545.94 7/18/2006 79.30 77.47
5,546.24 11/7/2006 79.00 77.17
5546.81 2/27/2007 78.43 76.6
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,623.41 5,625.24 1.83 121.33
Water Levels and Data over Time
White Mesa Mill - Well TW4-17 (MW-32)
5546.56 5/2/2007 78.68 76.85
5546.81 8/15/2007 78.43 76.6
5546.96 10/10/2007 78.28 76.45
5547.9 3/26/2008 77.34 75.51
5548.08 6/25/2008 77.16 75.33
5548.42 8/26/2008 76.82 74.99
5548.05 10/14/2008 77.19 75.36
5548.29 3/3/2009 76.95 75.12
5548.09 6/24/2009 77.15 75.32
5547.79 9/10/2009 77.45 75.62
5548.09 12/11/2009 77.15 75.32
5,548.50 03/11/2010 76.74 74.91
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,639.13 5,641.28 2.15 121.33
5,585.13 8/23/2002 56.15 54.00
5,585.41 9/11/2002 55.87 53.72
5,585.47 10/23/2002 55.81 53.66
5,585.40 11/22/2002 55.88 53.73
5,585.68 12/3/2002 55.60 53.45
5,585.90 1/9/2003 55.38 53.23
5,590.79 2/12/2003 50.49 48.34
5,586.18 3/26/2003 55.10 52.95
5,586.36 4/2/2003 54.92 52.77
5,586.24 5/1/2003 55.04 52.89
5,584.93 6/9/2003 56.35 54.20
5,584.46 7/7/2003 56.82 54.67
5,584.55 8/4/2003 56.73 54.58
5,584.01 9/11/2003 57.27 55.12
5,583.67 10/2/2003 57.61 55.46
5,583.50 11/7/2003 57.78 55.63
5,584.08 12/3/2003 57.20 55.05
5,585.45 1/15/2004 55.83 53.68
5,585.66 2/10/2004 55.62 53.47
5,586.13 3/28/2004 55.15 53.00
5,586.39 4/12/2004 54.89 52.74
5 586 66 5/13/2004 54 62 52 47
Water Levels and Data over Time
White Mesa Mill - Well TW4-18
5,586.66 5/13/2004 54.62 52.47
5,586.77 6/18/2004 54.51 52.36
5,587.35 7/28/2004 53.93 51.78
5,586.34 8/30/2004 54.94 52.79
5,585.85 9/16/2004 55.43 53.28
5,585.22 10/11/2004 56.06 53.91
5,584.70 11/16/2004 56.58 54.43
5,584.81 12/22/2004 56.47 54.32
5,584.68 1/18/2005 56.60 54.45
5,585.02 2/28/2005 56.26 54.11
5,585.25 3/15/2005 56.03 53.88
5,586.31 4/26/2005 54.97 52.82
5,586.97 5/24/2005 54.31 52.16
5,586.58 6/30/2005 54.70 52.55
5,586.10 7/29/2005 55.18 53.03
5,586.05 9/12/2005 55.23 53.08
5,585.86 12/7/2005 55.42 53.27
5,587.13 3/8/2006 54.15 52.00
5,585.93 6/13/2006 55.35 53.20
5,585.40 7/18/2006 55.88 53.73
5,585.38 11/7/2006 55.90 53.75
5585.83 2/27/2007 55.45 53.30
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,639.13 5,641.28 2.15 121.33
Water Levels and Data over Time
White Mesa Mill - Well TW4-18
5585.15 5/2/2007 56.13 53.98
5586.47 6/24/2008 54.81 52.66
5586.3 8/26/2008 54.98 52.83
5585.21 10/14/2008 56.07 53.92
5584.47 3/3/2009 56.81 54.66
5584.35 6/24/2009 56.93 54.78
5583.88 9/10/2009 57.4 55.25
5584.43 12/11/2009 56.85 54.70
5,585.26 03/11/2010 56.02 53.87
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total Depth
to Water
(blw.LSD)
Total Depth Of
Well
5,629.53 5,631.39 1.86 121.33
5,581.88 8/23/2002 49.51 47.65
5,582.14 9/11/2002 49.25 47.39
5,582.06 10/23/2002 49.33 47.47
5,582.07 11/22/2002 49.32 47.46
5,582.16 12/3/2002 49.23 47.37
5,582.28 1/9/2003 49.11 47.25
5,582.29 2/12/2003 49.10 47.24
5,582.74 3/26/2003 48.65 46.79
5,582.82 4/2/2003 48.57 46.71
5,548.47 5/1/2003 82.92 81.06
5,564.76 6/9/2003 66.63 64.77
5,562.53 7/7/2003 68.86 67.00
5,564.10 8/4/2003 67.29 65.43
5,566.01 8/30/2004 65.38 63.52
5,555.16 9/16/2004 76.23 74.37
5,549.80 10/11/2004 81.59 79.73
5,546.04 11/16/2004 85.35 83.49
5,547.34 12/22/2004 84.05 82.19
5,548.77 1/18/2005 82.62 80.76
5,551.18 2/28/2005 80.21 78.35
5,556.81 3/15/2005 74.58 72.72
5 562 63 4/26/2005 68 76 66 90
Water Levels and Data over Time
White Mesa Mill - Well TW4-19
5,562.63 4/26/2005 68.76 66.90
5,573.42 5/24/2005 57.97 56.11
5,552.94 7/29/2005 78.45 76.59
5,554.00 9/12/2005 77.39 75.53
5,555.98 12/7/2005 75.41 73.55
5,552.00 3/8/2006 79.39 77.53
5,545.74 6/13/2006 85.65 83.79
5,544.06 7/18/2006 87.33 85.47
5,548.81 11/7/2006 82.58 80.72
5543.59 2/27/2007 87.8 85.94
5544.55 5/2/2007 86.84 84.98
5558.97 8/15/2007 72.42 70.56
5559.73 10/10/2007 71.66 69.8
5569.26 3/26/2008 62.13 60.27
5535.47 6/25/2008 95.92 94.06
5541.41 8/26/2008 89.98 88.12
5558.45 10/14/2008 72.94 71.08
5536.9 3/3/2009 94.49 92.63
5547.76 6/24/2009 83.63 81.77
5561.48 9/10/2009 69.91 68.05
5548.14 12/11/2009 83.25 81.39
5,570.58 03/11/2010 60.81 58.95
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,628.52 5,629.53 1.01 106.0
Water Levels and Data over Time
White Mesa Mill - Well TW4-20
5,565.70 7/29/2005 63.83
5,546.53 8/30/2005 83.00
5,540.29 9/12/2005 89.24
5,541.17 12/7/2005 88.36
5,540.33 3/8/2006 89.20
5,530.43 6/13/2006 99.10
5,569.13 7/18/2006 60.40
5,547.95 11/7/2006 81.58
5,549.25 2/27/2007 80.28
5,550.58 5/2/2007 78.95
5,563.60 8/14/2007 65.93
5,555.85 10/10/2007 73.68
5,569.10 3/26/2008 60.43
5,560.00 6/25/2008 69.53
5,539.64 8/26/2008 89.89
5,539.51 10/14/2008 90.02
5,553.00 3/3/2009 76.53
5,534.18 6/24/2009 95.35
5,558.39 9/10/2009 71.14
5,560.99 12/11/2009 68.54
5,564.09 3/11/2010 65.44
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,638.20 5,639.35 1.15 120.92
5,582.98 7/29/2005 56.37
5,583.43 8/30/2005 55.92
5,581.87 9/12/2005 57.48
5,580.50 12/7/2005 58.85
5,583.64 3/8/2006 55.71
5,580.55 6/13/2006 58.80
5,578.95 7/18/2006 60.40
5,578.47 11/7/2006 60.88
5,579.53 2/27/2007 59.82
5,578.07 5/2/2007 61.28
5,583.41 8/15/2007 55.94
5,583.45 10/10/2007 55.9
5,586.47 3/26/2008 52.88
5,579.16 6/24/2008 60.19
5,579.92 8/26/2008 59.43
5,577.37 10/14/2008 61.98
5,578.00 3/10/2009 61.35
5,580.14 6/24/2009 59.21
5,578.72 9/10/2009 60.63
5,579.99 12/11/2009 59.36
5 582 81 3/11/2010 56 54
Water Levels and Data over Time
White Mesa Mill - Well TW4-21
5,582.81 3/11/2010 56.54
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,627.83 5,629.00 1.17 113.5
5,571.89 7/29/2005 57.11
5,572.20 8/30/2005 56.80
5,572.08 9/12/2005 56.92
5,571.61 12/7/2005 57.39
5,571.85 3/8/2006 57.15
5,571.62 6/13/2006 57.38
5,571.42 7/18/2006 57.58
5,571.02 11/7/2006 57.98
5571.24 2/27/2007 57.76
5,570.75 6/29/2007 58.25
5,571.82 8/14/2007 57.18
5,571.99 10/10/2007 57.01
5,573.05 3/26/2008 55.95
5,573.04 6/24/2008 55.96
5,573.04 8/26/2008 55.96
5,573.02 10/14/2008 55.98
5,573.19 3/10/2009 55.81
5,573.32 6/24/2009 55.68
5,573.17 9/10/2009 55.83
5,573.52 12/11/2009 55.48
Water Levels and Data over Time
White Mesa Mill - Well TW4-22
,
5,573.88 3/11/2010 55.12
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,627.83 5,629.00 1.17 113.5
5,560.52 9/13/2007 68.48 5,539.12
5,560.43 10/10/2007 68.57 5,539.04
5,560.88 11/30/2007 68.12 5,539.49
5,561.12 12/11/2007 67.88 5,539.73
5,560.82 1/8/2008 68.18 5,539.43
5,561.07 2/18/2008 67.93 5,539.68
5,561.17 3/26/2008 67.83 5,539.78
5,561.34 4/23/2008 67.66 5,539.95
5561.11 5/30/2008 67.89 5,539.72
5,561.16 6/24/2008 67.84 5,539.77
5,561.07 7/16/2008 67.93 5,539.68
5,561.31 8/26/2008 67.69 5,539.92
5,562.81 9/10/2008 66.19 5,541.42
5,561.20 10/14/2008 67.8 5,539.81
5,560.92 11/26/2008 68.08 5,539.53
5,561.18 12/29/2008 67.82 5,539.79
5,561.78 1/26/2009 67.22 5,540.39
5,561.37 2/24/2009 67.63 5,539.98
5,561.49 3/6/2009 67.51 5,540.10
5,561.35 4/7/2009 67.65 5,539.96
Water Levels and Data over Time
White Mesa Mill - Well TW4-23
,,
5,561.47 5/29/2009 67.53 5,540.08
5,561.75 6/30/2009 67.25 5,540.36
5,561.75 7/31/2009 67.25 5,540.36
5,561.90 8/31/2009 67.1 5,540.51
5,561.76 9/10/2009 67.24 5,540.37
5,562.27 12/11/2009 66.73 5,540.37
5,562.78 3/11/2010 66.22 5,540.37
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,627.83 5,625.70 -2.13 113.5
5,568.48 9/13/2007 57.22 59.35
5,568.40 10/10/2007 57.30 59.43
5,569.03 11/30/2007 56.67 58.80
5,569.17 12/11/2007 56.53 58.66
5,568.90 1/8/2008 56.80 58.93
5,569.09 2/18/2008 56.61 58.74
5,569.30 3/26/2008 56.40 58.53
5,569.55 4/23/2008 56.15 58.28
5569.39 5/30/2008 56.31 58.44
5,569.21 6/24/2008 56.49 58.62
5,569.15 7/16/2008 56.55 58.68
5,569.21 8/26/2008 56.49 58.62
5,569.10 9/10/2008 56.60 58.73
5,568.99 10/14/2008 56.71 58.84
5,568.82 11/26/2008 56.88 59.01
5,568.79 12/29/2008 56.91 59.04
5,569.52 1/26/2009 56.18 58.31
5,569.18 2/24/2009 56.52 58.65
5,569.24 3/6/2009 56.46 58.59
5,569.08 4/7/2009 56.62 58.75
Water Levels and Data over Time
White Mesa Mill - Well TW4-24
,
5,569.10 5/29/2009 56.60 58.73
5,569.29 6/30/2009 56.41 58.54
5,569.25 7/31/2009 56.45 58.58
5,569.35 8/31/2009 56.35 58.48
5,569.15 9/10/2009 56.55 58.68
5,569.51 12/11/2009 56.19 58.32
5,569.73 3/11/2010 55.97 58.10
Water
Elevation
(WL)
Land
Surface
(LSD)
Measuring
Point
Elevation
(MP)
Length Of
Riser (L)
Date Of
Monitoring
Total or
Measured
Depth to
Water
(blw.MP)
Total
Depth to
Water
(blw.LSD)
Total
Depth Of
Well
5,627.83 5,644.91 17.08 113.5
5,601.86 09/13/2007 43.05
5,601.89 10/10/2007 43.02
5,602.57 11/30/2007 42.34
5,602.82 12/11/2007 42.09
5,601.94 01/08/2008 42.97
5,599.13 02/18/2008 45.78
5,597.11 03/26/2008 47.80
5,595.51 04/23/2008 49.40
5594.42 05/30/2008 50.49
5,594.26 06/24/2008 50.65
5,586.67 07/16/2008 58.24
5,594.17 08/26/2008 50.74
5,594.23 09/10/2008 50.68
5,594.12 10/14/2008 50.79
5,594.06 11/26/2008 50.85
5,594.87 12/29/2008 50.04
5,595.89 01/26/2009 49.02
5,596.27 02/24/2009 48.64
5,596.47 03/06/2009 48.44
5,596.74 04/07/2009 48.17
Water Levels and Data over Time
White Mesa Mill - Well TW4-25
,
5,597.55 05/29/2009 47.36
5,598.11 06/30/2009 46.8
5,598.22 07/31/2009 46.69
5,598.52 08/31/2009 46.39
5,598.49 09/10/2009 46.42
5,599.48 12/11/2009 45.43
5,599.75 03/11/2010 45.16

Tab H
Laboratory Analytical Reports

ENERGY LABORATORIE~ INC. ·2393 Salt Creek Highway (82601) • P.D. Box 3258 • Casper, WY 82602 'U"{f27 Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
f ANONA TORIES
LABORATORY ANALYTICAL REPORT
Client: Denison Mines USA Corp
Project: 1 st Quarter Chloroform
Lab ID: C10020658-004
Client Sample ID: MW-4
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Surr: 1,2-0ichlorobenzene-d4
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
45
4.0
1.2
1600
NO
NO
114
114
99.0
108
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.2
1.0
100
1.0
1.0
70-130
80-120
80-120
80-120
Report Date: 03/02/10
Collection Date: 02/17/10 15:03
DateReceived: 02/19/10
Matrix: Aqueous
MCU
QCL Method Analysis Date 1 By
A4500-CI B 03/01/1010:241 dvg
E353.2 03/01/10 11 :051 jal
SW8260B 02120/10 00:23 1 wen
SW8260B 02/23/10 20:38 1 wen
SW8260B 02/20/10 00:23 1 wen
SW8260B 02/20/10 00:23 1 wen
SW8260B 02/20/10 00:23 1 wen
SW8260B 02/20/10 00:23 1 wen
SW8260B 0212011 0 00:23 1 wen
SW8260B 02/2011 0 00:23 1 wen
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC. ·2393 Salt Creek Highway (82601) • P.o. Box 3258 • Casper, WY 82602 lUgl{f27 Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
L ABORA TORIES ----
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Choloform
Lab 10: C 10030236-014
Client Sample 10: TW4-1
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result
35
7.1
NO
1300
NO
NO
102
98.0
94.0
100
Units
mg/L
mg/L
ug/L
ug/L
ug/L
ug/L
%REC
%REC
%REC
%REC
Qualifier RL
0.2
1.0
100
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/15/10
Collection Date: 03/03/10 10: 17
DateReceived: 03/05/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/12/1012:091 dvg
E353.2 03/10/1016:121 jal
SW8260B 03/0611 0 07:59 1 jlr
SW8260B 03/05/10 18:32 1 jlr
SW8260B 03/06/1007:591 jlr
SW8260B 03/06/10 07:59 1 jlr
SW8260B 03/06/10 07:59 1 jlr
SW8260B 03/06/1007:591 jlr
SW8260B 03/06/10 07:591 jlr
SW8260B 03/06/10 07:59 1 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC. • 2393 Salt Creek Highway (82601) • P.o. Box 3258 • Caspe!; WY 82602 199m{f27 Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail] • www.energylab.com
LABORATORlE5
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Choloform
LablD: C 10030236-005
Client Sample 10: TW4-1R
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-dB
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
NO
NO
NO
7.B
NO
NO
96.0
90.0
BB.O
101
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.1
1.0
1.0
1.0
1.0
BO-120
70-130
BO-120
BO-120
Report Date: 03/15/10
Collection Date: 03/02/10 13:28
DateReceived: 03/05/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/12/10 11 :32 1 dvg
E353.2 03/10/1015:141 jal
SWB260B 03/06/10 01 :36 1 jlr
SWB260B 03/06/10 01 :36 1 jlr
SWB260B 03/06/10 01 :36 1 jlr
SWB260B 03/06/1001 :361 jlr
SWB260B 03/06/10 01 :36 1 jlr
SWB260B 03/06/10 01 :36 1 jlr
SWB260B 03/06/10 01 :36 1 jlr
SWB260B 03/06/10 01 :36 I jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC. ·2393 Salt Greek Highway (82601) • P.D. Box 3258 • Gaspe!; WY 82602 lGG;{({f'lY Toll Free 888.2350515 • 307.2350515 • Fax [phone] • [e-mail]· www.energylab.com
LABORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Choloform
Lab 10: C 10030236-015
Client Sample 10: TW4-2
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
42
6.8
2.0
2600
NO
NO
96.0
99.0
90.0
99.0
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.2
1.0
100
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/15/10
Collection Date: 03/03/10 09:58
DateReceived: 03/05/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/12/1012:121 dvg
E353.2 03/10/1016:141 jal
SW8260B 03/06/10 08:37 1 jlr
SW8260B 03/05/1019:121 jlr
SW8260B 03/06/1008:37 1 jlr
SW8260B 03/06/10 08:37 1 jlr
SW8260B 03/06/10 08:37 1 jlr
SW8260B 03/06/10 08:37 1 jlr
SW8260B 03/06/10 08:37 1 jlr
SW8260B 03/06/10 08:37 1 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC. • 2393 Salt Creek Highway (82601) • PO. Box 3258 • Casper, WY 82602 1999f{f)Y Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail] • www.energylab.com
I ABORA lOmES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Choloform
Lab 10: C 10030236-006
Client Sample 10: TW4-2R
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
NO
NO
NO
16
NO
NO
94.0
94.0
88.0
102
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.1
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/15/10
Collection Date: 03/02/10 14:15
DateReceived: 03/05/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/12/10 11 :36 1 dvg
E353.2 03/10/10 15:24 1 jal
SW8260B 03/06/10 02: 15 1 jlr
SW8260B 03/06/10 02: 15 1 jlr
SW8260B 03/06/10 02: 15 1 jlr
SW8260B 03/06/1002:151 jlr
SW8260B 03/06/1002:151 jlr
SW8260B 03/06/1002:151 jlr
SW8260B 03/06/10 02: 15 1 jlr
SW8260B 03/0611002:151 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC •• 2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602 199B{f27 Toll Free 888.235.0515 • 307235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
Lab 10: C 10020848-014
Client Sample 10: TW4-3
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-dB
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
23
2.B
NO
NO
NO
NO
95.0
79.0
91.0
105
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.1
1.0
1.0
1.0
1.0
BO-120
70-130
BO-120
BO-120
Report Date: 03/05/10
Collection Date: 02/23/10 08:52
DateReceived: 02/26/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/01/10 11 :451 dvg
E353.2 03/03/10 11 :30 1 jal
SWB260B 03/01/1015:371 jlr
SWB260B 03/01/1015:371 jlr
SWB260B 03/01/1015:371 jlr
SWB260B 03/01/10 15:37 1 jlr
SWB260B 03/01/1015:371 jlr
SWB260B 03/01/1015:371 jlr
SWB260B 03/01/10 15:37 1 jlr
SWB260B 03/0111015:371 jlr
MCl -Maximum contaminant Jevel.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC. ·2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602 lUm{f27 Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LA BORA TomES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
LablD: C 10020848-001
Client Sample ID: TW4-3R
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-dB
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
NO
NO
NO
1.2
NO
NO
96.0
90.0
B7.0
101
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.1
1.0
1.0
1.0
1.0
BO-120
70-130
BO-120
BO-120
Report Date: 03/05/10
Collection Date: 02/22/10 09:45
DateReceived: 02/26/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/01/1010:501 dvg
E353.2 03/02/1016:531 jal
SWB260B 02/27/1005:071 jJr
SWB260B 02/27/1005:071 jlr
SWB260B 02/27/1005:071 jlr
SWB260B 02/27/1005:071 jlr
SWB260B 02/2711005:071 jlr
SWB260B 02/27/1005:071 jlr
SWB260B 02/27/1005:071 jlr
SWB260B 02127/1005:071 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC. ·2393 Salt Creek Highway (82601) • po. Box 3258 • Casper, WY 82602 Igg:tf{f27 Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
Lab 10: C 10020658-002
Client Sample 10: TW4-4
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Surr: 1 ,2-0ichlorobenzene-d4
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result
48
6.6
1.0
1700
NO
NO
106
112
99.0
105
Units
mg/L
mg/L
ug/L
ug/L
ug/L
ug/L
%REC
%REC
%REC
%REC
Qualifier Rl
1
0.2
1.0
100
1.0
1.0
70-130
80-120
80-120
80-120
Report Date: 03/02/10
Collection Date: 02/17/1015:10
DateReceived: 02119/10
Matrix: Aqueous
MCU
QCl Method Analysis Date I By
A4500-CI B 03/01/1010:181 dvg
E353.2 03/01/10 11 :00 1 jal
SW8260B 02119/10 23: 12 1 wen
SW8260B 02/23/10 21 :491 wen
SW8260B 02/19/10 23: 12 1 wen
SW8260B 02119/10 23: 12 1 wen
SW8260B 02/19/10 23: 12 1 wen
SW8260B 02119/10 23: 12 1 wen
SW8260B 02119/10 23: 12 1 wen
SW8260B 02119/10 23: 12 1 wen
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC. • 2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602 lUgf{f27 Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABORA TORIES
LASORA TORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
Lab 10: C 10020848-024
Client Sample 10: TW4-5
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-dB
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
43
6.B
NO
13
NO
NO
93.0
90.0
91.0
104
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier Rl
1
0.2
1.0
1.0
1.0
1.0
BO-120
70-130
BO-120
BO-120
Report Date: 03/05/10
Collection Date: 02/25/10 08:22
DateReceived: 02/26/10
Matrix: Aqueous
MCU
QCl Method Analysis Date I By
A4500-CI B 03/01/10 12:2BI dvg
E353.2 03/03/10 12:0B 1 jal
SWB260B 03/02/10 17:06 1 jlr
SWB260B 03/02110 17:061 jlr
SWB260B 03/02/10 17:06 1 jlr
SWB260B 03/02/10 17:06 1 jlr
SWB260B 03/02/10 17:06 1 jlr
SWB260B 03/02/10 17:06 1 jlr
SWB260B 03/02/10 17:06 1 jlr
SWB260B 03/02/10 17:061 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC •• 2393 Salt Creek Highway (82601) • P.o. Box 3258 • Casper, WY 82602
Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Denison Mines USA Corp
1 st Quarter Chloroform
C10020848-011
Client Sample 10: TW4-5R
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
2
NO
NO
3.4
NO
NO
96.0
97.0
85.0
101
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
1
0.1
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/05/10
Collection Date: 02/24/10 12:30
DateReceived: 02/26/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/0111 0 11 :401 dvg
E353.2 03/03/10 11 :23 1 jal
SW8260B 03/02/10 04:59 1 jlr
SW8260B 03/02/1004:591 jlr
SW8260B 03/02/10 04:59 1 jlr
SW8260B 03/02/10 04:591 jlr
SW8260B 03/02/10 04:59 1 jlr
SW8260B 03/02/1004:591 jlr
SW8260B 03/02/10 04:59 1 jlr
SW8260B 03/02/10 04:59 1 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
l '..-:v:t ~T..i ENERG Y LABORATORIE~ INC •• 2393 Salt Creek Highway (82601) • P. 0. Box 3258 • Casper, WY 82602 _ .. ,-t\"7 Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LA BORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1st Quarter Chloroform
LabID: C 10020848-026
Client Sample ID: TW4-6
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Ch loromethane
Methylene chloride
Surr: 1,2-Dichlorobenzene-d4
Surr: Dibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
45
1.6
NO
1000
NO
NO
98.0
103
91.0
98.0
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifiers RL
0.1
1.0
100
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/05/10
Collection Date: 02/25/10 08:33
DateReceived: 02/26/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/01/1012:341 dvg
E353.2 03/03/10 12:23 1 jal
SW8260B 03/02/10 08: 1 0 1 jlr
SW8260B 03/02/10 06:54 1 jlr
SW8260B 03/02/10 08: 1 0 1 jlr
SW8260B 03/02/1008:101 jlr
SW8260B 03/0211 0 08: 1 0 1 jlr
SW8260B 03/02/10 08: 1 0 1 jlr
SW8260B 03/02/10 08: 1 0 1 jlr
SW8260B 03/0211008:101 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC .• 2393 Salt Creek Highway (82601) • po. Box 3258 • Casper, WY 82602 1999r{f27 Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LAHORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
LablD: C 10020848-013
Client Sample 10: TW4-6R
Analyses
MAJOR IONS
Chloride
Nitrogen. Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1.2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-dS
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
NO
NO
NO
12
NO
NO
9S.0
94.0
S3.0
102
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.1
1.0
1.0
1.0
1.0
SO-120
70-130
SO-120
SO-120
Report Date: 03/05/10
Collection Date: 02/24/10 15:00
DateReceived: 02/26/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/01/10 11 :441 dvg
E353.2 03/03/10 11 :2S 1 jal
SWS260B 03/02/10 06: 161 jlr
SWS260B 03/02/10 06: 16 1 jlr
SWS260B 03/02/10 06: 16 1 jlr
SWS260B 03/02/10 06: 16 1 jlr
SWS260B 03/02/10 06: 16 1 jlr
SWS260B 03/02110 06: 16 1 jlr
SWS260B 03/02/10 06: 16 1 jlr
SWS260B 03/02/1006:161 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC. • 2393 Salt Creek Highway (82601) • P.D. Box 3258 • Casper, WY 82602 Igg;{({f27 70// Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Choloform
Lab 10: C 1 0030236-013
Client Sample 10: TW4-7
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
36
3.8
NO
1200
NO
NO
100
90.0
89.0
101
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.2
1.0
100
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/15/10
Collection Date: 03/03/10 10:06
DateReceived: 03/05/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/12/10 12:08 1 dvg
E353.2 03/10/10 16:09 1 jal
SW8260B 03/06/10 07:20 1 jlr
SW8260B 03/0511 0 17:54 1 jlr
SW8260B 03/06/10 07:20 1 jlr
SW8260B 03/06/10 07:20 1 jlr
SW8260B 03/06/10 07:20 1 jlr
SW8260B 03/06/10 07:20 1 jlr
SW8260B 03/06/10 07:20 1 jlr
SW8260B 03/06/10 07:20 1 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC. • 2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602 Igggf{f2Y lOll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail] • www.energylab.com
LABOI?A !ORlES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Choloform
Lab 10: C 10030236-004
Client Sample 10: TW4-7R
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
NO
NO
NO
10
NO
NO
95.0
94.0
86.0
100
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier Rl
0.1
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/15/10
Collection Date: 03/02/10 11: 17
DateReceived: 03/05/10
Matrix: Aqueous
MCU
QCl Method Analysis Date 1 By
A4500-CI B 03/12/10 11 :30 1 dvg
E353.2 03/10/1015:121 jal
SW8260B 03/05/1021 :091 jlr
SW8260B 03/05/1021:091 jlr
SW8260B 03/05/1021 :091 jlr
SW8260B 03/05/1021 :091 jlr
SW8260B 03/05/10 21 :091 jlr
SW8260B 03/05/1021 :091 jlr
SW8260B 03/0511021 :091 jlr
SW8260B 03/05/1021:091 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC. • 2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602
Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABORA TORlE5
LASORA TORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
Lab 10: C 10020848-019
Client Sample 10: TW4-8
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Dibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
57
NO
NO
NO
NO
NO
98.0
99.0
85.0
100
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.1
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/05/10
Collection Date: 02/24/10 08:35
DateReceived: 02126/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/01/1012:011 dvg
E353.2 03/03/10 11 :48 1 jal
SW8260B 03/02/10 00:32 1 jlr
SW8260B 03/0211000:321 jlr
SW8260B 03/02/10 00:32 1 jlr
SW8260B 03/02/10 00:32 1 jlr
SW8260B 03/02110 00:32 1 jlr
SW8260B 03/02110 00:32 1 jlr
SW8260B 03/02/10 00:32 1 jlr
SW8260B 03/02/10 00:32 1 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC. ·2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602 Igggf{f2Y Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABORA TORIES
LASORA TORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
Lab 10: C 10020848-007
Client Sample 10: TW4-8R
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
NO
NO
NO
1.7
NO
NO
95.0
97.0
90.0
100
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.1
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/05/10
Collection Date: 02/23/10 09:40
DateReceived: 02/26/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/01/10 11:19/dvg
E353.2 03/03/10 11 :05 1 jal
SW8260B 02/27/1008:551 jlr
SW8260B 02/27/1008:551 jlr
SW8260B 02/27/1008:551 jlr
SW8260B 02/27/1008:551 jlr
SW8260B 02/2711008:551 jlr
SW8260B 02/27/1008:551 jlr
SW8260B 02/27/1008:551 jlr
SW8260B 02/27/1008:551 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC. • 2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602
Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
Lab 10: C 1 0020848-020
Client Sample 10: TW4-9
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
47
1.4
NO
NO
NO
NO
96.0
88.0
89.0
97.0
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifiers Rl
0.1
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/05/10
Collection Date: 02/23/10 09:05
DateReceived: 02/26/10
Matrix: Aqueous
MCU
QCl Method Analysis Date 1 By
A4500-CI B 03/01/10 12:041 dvg
E353.2 03/03/10 11 :50 1 jal
SW8260B 03/02/10 01: 1 0 1 jlr
SW8260B 03/02110 01: 1 0 1 jlr
SW8260B 03/02/10 01: 1 0 1 jlr
SW8260B 03/02/10 01: 1 0 1 jlr
SW8260B 03/02/10 01: 1 0 1 jlr
SW8260B 03/02110 01: 1 0 1 jlr
SW8260B 03/02/10 01: 1 0 1 jlr
SW8260B 03/02/10 01: 1 0 1 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC. ·2393 Salt Creek Highway (82601) • P.O Box 3258 • Casper, WY 82602 1999f{f!1Y Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABOI?A TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
Lab 10: C 10020848-008
Client Sample 10: TW4-9R
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
Qel -Quality control limit.
Result
NO
NO
NO
NO
NO
NO
97.0
95.0
88.0
101
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.1
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/05/10
Collection Date: 02/22/10 12:25
DateReceived: 02/26/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/01/10 11 :241 dvg
E353.2 03/03/10 11 :08 1 jal
SW8260B 02/27/1009:341 jlr
SW8260B 02/27/1009:341 jlr
SW8260B 02/27/1009:341 jlr
SW8260B 02/27/1009:341 jlr
SW8260B 02/27/1009:341 jlr
SW8260B 02/27/1009:341 jlr
SW8260B 02/27/1009:341 jlr
SW8260B 02127/1009:341 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC .• 2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602 1999f{f2Y Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail] • www.energylab.com
LAflORA TORIES
LABORATORY ANALYTICAL REPORT
Client: Denison Mines USA Corp
Project: 1 st Quarter Choloform
Lab 10: C10030236-010
Client Sample 10: TW4-10
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: T oluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
aCl -Quality control limit.
Result
49
5.0
NO
460
NO
NO
99.0
91.0
88.0
100
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
1
0.2
1.0
100
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/15/10
Collection Date: 03/03/10 09:37
DateReceived: 03/05/10
Matrix: Aqueous
MCU
QCL Method Analysis Date 1 By
A4500-CI B 03/12/10 11:54 1 dvg
E353.2 03/10/10 15:34 1 jal
SW8260B 03/0611 0 05:25 1 jlr
SW8260B 03/05/10 16:00 1 jlr
SW8260B 03/06/10 05:25 1 jlr
SW8260B 03/06/10 05:25 1 jlr
SW8260B 03/06/10 05:25 1 jlr
SW8260B 03/06/10 05:25 1 jlr
SW8260B 03/0611 0 05:25 1 jlr
SW8260B 03/06/10 05:25 1 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC. ·2393 Salt Creek Highway (82601) • P.o. Box 3258 • Casper, WY 82602 1999({'D7 Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail] • www.energylab.com
LARORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Choloform
Lab 10: C 10030236-001
Client Sample 10: TW4-10R
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-Dichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
NO
NO
NO
12
NO
NO
95.0
92.0
90.0
101
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.1
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/15/10
Collection Date: 03/02/10 08:20
DateReceived: 03/05/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/12/10 11 :20 1 dvg
E353.2 03/10/10 15:04 1 jal
SW8260B 03/06/10 04:09 1 jlr
SW8260B 03/06/10 04:09 1 jlr
SW8260B 03/06/10 04:09 1 jlr
SW8260B 03/06/10 04:09 1 jlr
SW8260B 03/06/10 04:09 1 jlr
SW8260B 03/06/10 04:09 1 jlr
SW8260B 03/06/10 04:09 1 jlr
SW8260B 03/06/10 04:09 1 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC •• 2393 Salt Creek Highway (82601) • po. Box 3258 • Casper, WY 82602 199;{({f2Y Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
I AUOf?ATORlES
LASORA TORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Choloform
LablD: C 10030236-012
Client Sample ID: TW4-11
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: T oluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
42
6.8
NO
820
NO
NO
96.0
102
83.0
102
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.2
1.0
100
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/15/10
Collection Date: 03/03/10 09:49
DateReceived: 03/05/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/12/1012:061 dvg
E353.2 03/10/10 16:07 1 jal
SW8260B 03/06/10 06:42 1 jlr
SW8260B 03/05110 17:161 jlr
SW8260B 03/06/10 06:42 1 jlr
SW8260B 03/06/10 06:42 1 jlr
SW8260B 03/06/10 06:42 1 jlr
SW8260B 03/06/10 06:42 1 jlr
SW8260B 03/06/10 06:42 1 jlr
SW8260B 03/06/10 06:42 1 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC. • 2393 Salt Creek Highway (82601) • P.o. Box 3258 • Casper, WY 82602 199m{f)Y Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail] • www.energylab.com
LABORA TORIES
LASORA TORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Choloform
LablD: C 10030236-003
Client Sample 10: TW4-11 R
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
NO
NO
NO
17
NO
NO
103
93.0
91.0
101
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.1
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/15/10
Collection Date: 03/02/10 10:35
DateReceived: 03/05/10
Matrix: Aqueous
MCU
QCL Method Analysis Date' By
A4500-CI B 03/12/10 11 :28 1 dvg
E353.2 03/10/10 15:09 1 jal
SW8260B 03/05/10 20:30 1 jlr
SW8260B 03/05/10 20:30 1 jlr
SW8260B 03/05/10 20:30 1 jlr
SW8260B 03/05/10 20:30 1 jlr
SW8260B 03/05/10 20:30 1 jlr
SW8260B 03/05/10 20:30 1 jlr
SW8260B 03/05/10 20:30 1 jlr
SW8260B 03/05/10 20:30 1 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC. ·2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602 Iggg({f27 Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
LablD: C 10020848-015
Client Sample ID: TW4-12
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
RL -Analyte reporting limit.
QCl -Quality control limit.
Result
22
4.0
NO
NO
NO
NO
91.0
91.0
91 .0
104
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.2
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/05/10
Collection Date: 02/23/1008:20
DateReceived: 02/26/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/01/10 11 :47 1 dvg
E353.2 03/03/10 11 :33 1 jal
SW8260B 03/01/1016:141 jlr
SW8260B 03/01/1016:141 jlr
SW8260B 03/0111016:141 jlr
SW8260B 03/0111016:141 jlr
SW8260B 03/01/1016:141 jlr
SW8260B 03/01/1016:141 jlr
SW8260B 03/0111016:141 jlr
SW8260B 03/01/1016:141 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC. ·2393 Salt Creek Highway (82601) • po. Box 3258 • Casper, WY 82602 'UB{f)Y Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LASaRA TomES
LASORA TORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
LablD: C 10020848-002
Client Sample 10: TW4-12R
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
NO
NO
NO
1.4
NO
NO
102
95.0
94.0
100
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.1
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/05/10
Collection Date: 02/22/10 14:27
DateReceived: 02/26/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/01/1010:531 dvg
E353.2 03/02110 16:56 1 jal
SW8260B 02/27/1005:451 jlr
SW8260B 02/27/1005:451 jlr
SW8260B 02/2711005:451 jlr
SW8260B 02/27/1005:451 jlr
SW8260B 02127/1005:451 jlr
SW8260B 02/27/1005:451 jlr
SW8260B 02/27/1005:451 jlr
SW8260B 02/27/1005:451 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC. • 2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602 Iggg({f>Y Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • casper@energy/ab.com· www.energy/ab.com
LABORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
Lab 10: C 10020848-016
Client Sample 10: TW4-13
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Dibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: T oluene-dS
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
53
4.3
NO
NO
NO
NO
9S.0
97.0
90.0
9S.0
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.2
1.0
1.0
1.0
1.0
SO-120
70-130
SO-120
SO-120
Report Date: 03/05/10
Collection Date: 02/24/10 07:45
DateReceived: 02/26/10
Matrix: Aqueous
MCU
QCL Method Analysis Date 1 By
A4500-CI B 03/01/10 11 :491 dvg
E353.2 03/0311 0 11 :40 1 jal
SWS260B 03/01/1022:351 jlr
SWS260B 03/01/10 22:351 jlr
SWS260B 03/01/1022:351 jlr
SWS260B 03/01/10 22:351 jlr
SWS260B 03/01/1022:351 jlr
SWS260B 03/01/1022:351 jlr
SWS260B 03/01/10 22:351 jlr
SWS260B 03/0111022:351 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC. ·2393 Salt Creek Highway (82601)' po. Box 3258 • Casper, WY 82602
Toll Free 888.235.0515 • 307235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
LablD: C 10020848-003
Client Sample 10: TW4-13R
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
NO
NO
NO
3.0
NO
NO
99.0
96.0
90.0
101
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.1
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/05/10
Collection Date: 02/23/10 13:02
OateReceived: 02/26/10
Matrix: Aqueous
MCU
QCL Method Analysis Date 1 By
A4500-CI B 03/01/1011 :12/ dvg
E353.2 03/02/10 16:581 jal
SW8260B 02/27/1006:231 jlr
SW8260B 02/27/1006:231 jlr
SW8260B 02/27/1006:231 jlr
SW8260B 02/2711006:231 jlr
SW8260B 02/27/1006:231 jlr
SW8260B 02/2711006:231 jlr
SW8260B 02/27/1006:231 jlr
SW8260B 02/27/1006:231 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC •• 2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602 199m{f27 Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail] • www.energylab.com
LASaRA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Choloform
Lab 10: C 10030236-009
Client Sample 10: TW4-14
Analyses
MAJOR IONS
Chloride
Nitrogen. Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1.2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
33
2.5
NO
NO
NO
NO
102
92.0
89.0
99.0
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.1
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/15/10
Collection Date: 03/03/1010:42
DateReceived: 03/05/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/1211 0 11 :52 1 dvg
E353.2 03/10/10 15:32 1 jal
SW8260B 03/06/1003:31 1 jlr
SW8260B 03/06/1003:31 1 jlr
SW8260B 03/0611003:31 1 jlr
SW8260B 03/06/1003:311 jlr
SW8260B 03/06/1003:311 jlr
SW8260B 03/06/1003:311 jlr
SW8260B 03/06/1003:311 jlr
SW8260B 03/06/1003:311 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC. ·2393 Salt Creek Highway (82601) • po. Box 3258 • Casper, WY 82602 1999r{f2Y Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LAHORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
Lab 10: C 10020848-004
Client Sample 10: TW4-14R
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
NO
NO
NO
3.3
NO
NO
97.0
108
90.0
103
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.1
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/05/10
Collection Date: 02/23/10 14:08
DateReceived: 02/26/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/01/10 11:14/dvg
E353.2 03/02110 17:25 1 jal
SW8260B 02/27/1007:021 jlr
SW8260B 02/27/1007:021 jlr
SW8260B 02/27/1007:021 jlr
SW8260B 02/2711007:021 jlr
SW8260B 02/27/1007:021 jlr
SW8260B 02/27/1007:021 jlr
SW8260B 02/27/1007:021 jlr
SW8260B 02/27/1007:021 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC. ·2393 Salt Creek Highway (82601) • po. Box 3258 • Casper, WY 82602 Iggg({f2Y Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • casper@energy/ab.com· www.energy/ab.com
LAHORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
LablD: C 10020658-003
Client Sample ID: TW4-15
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Surr: 1,2-0ichlorobenzene-d4
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
57
0.2
NO
780
NO
19
110
110
99.0
109
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
1
0.1
1.0
100
1.0
1.0
70-130
80-120
80-120
80-120
Report Date: 03/02/10
Collection Date: 02/17/1014:52
DateReceived: 02/19/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/01/1010:221 dvg
E353.2 03/01/10 11 :031 jal
SW8260B 02119/1023:471 wen
SW8260B 02/23/10 22:24 1 wen
SW8260B 02/19/1023:471 wen
SW8260B 02/19/10 23:47 1 wen
SW8260B 02/19/1023:471 wen
SW8260B 02/19/1023:471 wen
SW8260B 02/19/1023:471 wen
SW8260B 02119/1023:471 wen
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC. ·2393 Salt Creek Highway (82601) • po. Box 3258 • Casper, WY 82602
Toll Free 888.2350515 • 307.2350515 • Fax [phone] • [e-mail]· www.energylab.com
LABORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
Lab 10: C 10020848-021
Client Sample 10: TW4-16
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
77
4.2
NO
NO
NO
NO
96.0
106
91.0
94.0
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.1
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/05/10
Collection Date: 02/24/1008:15
DateReceived: 02/26/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/01/1012:061 dvg
E353.2 03/03/1012:001 jal
SW8260B 03/02/10 01 :48 1 jlr
SW8260B 03/02/10 01 :48 1 jlr
SW8260B 03/02/10 01 :48 1 jlr
SW8260B 03/02/1001 :481 jlr
SW8260B 03/02/10 01 :48 1 jlr
SW8260B 03/02110 01 :48 1 jlr
SW8260B 03/02/10 01 :48 1 jlr
SW8260B 03/02/10 01 :48 1 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC. • 2393 Salt Creek Highway (82601) • AD. Box 3258 • Casper, WY 82602 199m{r,y Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
Lab 10: C 10020848-009
Client Sample 10: TW4-16R
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
NO
NO
NO
3.2
NO
NO
100
96.0
97.0
99.0
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.1
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/05/10
Collection Date: 02/23/10 10:35
DateReceived: 02/26/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/01/10 11:37/dvg
E353.2 03/03/10 11 :101 jal
SW8260B 02/27/1010:121 jlr
SW8260B 02/27/10 10:121 jlr
SW8260B 02/27/1010:121 jlr
SW8260B 02/27/1010:121 jlr
SW8260B 02/27/1010:121 jlr
SW8260B 02/2711010:121 jlr
SW8260B 02/27/1010:121 jlr
SW8260B 02/27/10 10: 121 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC •• 2393 Salt Creek Highway (82601) • po. Box 3258 • Casper, WY 82602 ,g~g({"7 lOll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
'ABOf?A 70mES
LABORA TORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
LablD: C 10020658-001
Client Sample ID: TW4-17
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Surr: 1,2-0ichlorobenzene-d4
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
38
NO
NO
NO
NO
NO
102
110
97.0
107
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier Rl
0.1
1.0
1.0
1.0
1.0
70-130
80-120
80-120
80-120
Report Date: 03/02/10
Collection Date: 02/17/1013:34
DateReceived: 02/19/10
Matrix: Aqueous
MCU
QCl Method Analysis Date I By
A4500-CI B 03/01/1010:161 dvg
E353.2 03/01/10 10:53 1 jal
SW8260B 02/19/1022:361 wen
SW8260B 02119/1022:361 wen
SW8260B 02/19/10 22:36 1 wen
SW8260B 02/19/10 22:36 1 wen
SW8260B 02/1911 0 22:36 1 wen
SW8260B 02/19/10 22:36 1 wen
SW8260B 02/19/10 22:36 1 wen
SW8260B 02119/10 22:36 1 wen
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC. ·2393 Salt Creek Highway (82601) • P.o. Box 3258 • Casper, WY 82602 ,gg;{({"y Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
l ABORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
Lab 10: C 1 0020848-023
Client Sample 10: TW4-18
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
41
5.1
NO
69
NO
NO
92.0
92.0
86.0
102
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.1
1.0
10
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/05/10
Collection Date: 02/24/10 10:50
DateReceived: 02/26/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/0111 0 12:23 1 dvg
E353.2 03/03/10 12:05 1 jal
SW8260B 03/02110 18:22 1 jlr
SW8260B 03/0211017:441 jlr
SW8260B 03/02/10 18:22 1 jlr
SW8260B 03/02/10 18:22 1 jlr
SW8260B 03/02/10 18:22 1 jlr
SW8260B 03/02/10 18:22 1 jlr
SW8260B 03/02/10 18:22 1 jlr
SW8260B 03/02/10 18:221 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC. • 2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602 1999f{f27 Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LA BORA TORIES
LASORA TORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
Lab 10: C 10020658-005
Client Sample 10: TW4-19
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Surr: 1,2-0ichlorobenzene-d4
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
144
2.0
1.3
940
NO
NO
111
108
98.0
106
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier Rl
0.1
1.0
100
1.0
1.0
70-130
80-120
80-120
80-120
Report Date: 03/02/10
Collection Date: 02/17/10 14:30
DateReceived: 02/19/10
Matrix: Aqueous
MCU
QCl Method Analysis Date I By
A4500-CI B 03/01/1010:261 dvg
E353.2 03/01/10 11 :08 1 jal
SW8260B 02/20/10 00:58 1 wen
SW8260B 02/23/1021 :131 wen
SW8260B 02/20/10 00:58 1 wen
SW8260B 02/20/10 00:58 1 wen
SW8260B 02120/10 00:58 1 wen
SW8260B 02/20/10 00:58 1 wen
SW8260B 02/20/10 00:58 1 wen
SW8260B 02/20/10 00:58 1 wen
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC. ·2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602 199m{"Y lOll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABORATORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
LablD: C 1 0020658-006
Client Sample ID: TW4-20
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-dB
Surr: 1,2-0ichlorobenzene-d4
Report
Definitions:
Rl -Analyte reporting limit.
Qel -Quality control limit.
Result
179
2.0
2.7
3500
NO
3.2
119
10B
9B.0
10B
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.1
1.0
200
1.0
1.0
70-130
BO-120
BO-120
BO-120
Report Date: 03/02/10
Collection Date: 02/17/1014:42
DateReceived: 02119/10
Matrix: Aqueous
MCU
QCL Method Analysis Date 1 By
A4500-CI B 03/01/1010:301 dvg
E353.2 03/01/10 11:1B/jal
SWB260B 02/20/10 01 :34 1 wen
SWB260B 02/2411 0 02:30 1 wen
SWB260B 02/20/10 01 :34 1 wen
SWB260B 02120/10 01 :34 1 wen
SWB260B 02/20/10 01 :34 1 wen
SWB260B 0212011001 :341 wen
SWB260B 02120/1001 :341 wen
SWB260B 02120/10 01 :34 1 wen
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC. • 2393 Salt Creek Highway (82601) • P.o. Box 3258 • Casper, WY 82602 IU;{({f27 lOll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
Lab 10: C 10020848-025
Client Sample 10: TW4-21
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
228
8.4
NO
170
NO
NO
98.0
102
88.0
99.0
Units
mg/L
mg/L
ug/L
ug/L
ug/L
ug/L
%REC
%REC
%REC
%REC
Qualifier Rl
0.2
1.0
10
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/05/10
Collection Date: 02/25/10 08:05
DateReceived: 02/26/10
Matrix: Aqueous
MCU
QCl Method Analysis Date I By
A4500-CI B 03/01/1012:311 dvg
E353.2 03/03/1012:101 jal
SW8260B 03/02/10 07:32 1 jlr
SW8260B 03/01/1014:141 jlr
SW8260B 03/02/10 07:32 1 jlr
SW8260B 03/02/10 07:32 1 jlr
SW8260B 03/02/10 07:32 1 jlr
SW8260B 03/02/10 07:32 1 jlr
SW8260B 03/02/1007:321 jlr
SW8260B 03/02/10 07:321 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC. ·2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602
Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Denison Mines USA Corp
1st Quarter Chloroform
C10020848-012
Client Sample 10: TW4-21 R
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-dB
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
NO
NO
NO
2.5
NO
NO
96.0
92.0
BB.O
96.0
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier Rl
1
0.1
1.0
1.0
1.0
1.0
BO-120
70-130
BO-120
BO-120
Report Date: 03/05/10
Collection Date: 02/24/10 13:25
DateReceived: 02/26/10
Matrix: Aqueous
MCU
QCl Method Analysis Date I By
A4500-CI B 03/01/1011 :421 dvg
E353.2 03/03/10 11 :25 1 jal
SWB260B 03/02/10 05:37 1 jlr
SWB260B 03/02/10 05:37 1 jlr
SWB260B 03/02/10 05:37 1 jlr
SWB260B 03/02/10 05:37 1 jlr
SWB260B 03/02/10 05:37 1 jlr
SWB260B 03/02/10 05:37 1 jlr
SWB260B 03/0211005:371 jlr
SWB260B 03/02/1005:371 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC •• 2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602 1991{({f2Y Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail] • www.energylab.com
LAHORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Choloform
Lab 10: C 10030236-011
Client Sample 10: TW4-22
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-dB
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
427
36.6
NO
2200
NO
NO
93.0
100
B7.0
100
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
0-Rl increased due to sample matrix interference.
Report Date: 03/15/10
Collection Date: 03/03/10 09:24
DateReceived: 03/05/10
Matrix: Aqueous
MCU
Qualifier RL QCL Method Analysis Date I By
A4500-CI B 03/12/1012:031 dvg
0 0.3 E353.2 03/10/10 16:04 1 jal
1.0 SWB260B 03/06/10 06:04 1 jlr
100 SWB260B 03/05/10 16:3B 1 jlr
1.0 SWB260B 03/0611 0 06:04 1 jlr
1.0 SWB260B 03/06/10 06:04 1 jlr
BO-120 SWB260B 03/06/10 06:04 1 jlr
70-130 SWB260B 03/06/10 06:04 1 jlr
BO-120 SWB260B 03/06/10 06:04 1 jlr
BO-120 SWB260B 03/06/10 06:04 1 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC. ·2393 Salt Creek Highway (82601) • P.o. Box 3258 • Casper, WY 82602 lugf{f27 70// Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail] • www.energylab.com
LA BOI?A TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Choloform
Lab 10: C 10030236-002
Client Sample 10: TW4-22R
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
NO
NO
NO
13
NO
NO
96.0
87.0
87.0
102
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.1
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/15/10
Collection Date: 03/02/10 09:32
DateReceived: 03/05/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/12/10 11 :26 1 dvg
E353.2 03/1011 0 15:07 1 jal
SW8260B 03/05/1019:511 jlr
SW8260B 03/05/1019:511 jlr
SW8260B 03/05/10 19:51 1 jlr
SW8260B 03/05/1019:511 jlr
SW8260B 03/05/1019:511 jlr
SW8260B 03/0511019:511 jlr
SW8260B 03/05/10 19:51 1 jlr
SW8260B 03/05/1019:511 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC. • 2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602 1999({e27 Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
LablD: C 10020848-017
Client Sample ID: TW4-23
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result
45
NO
NO
NO
NO
NO
93.0
97.0
85.0
98.0
Units
mg/L
mg/L
ug/L
ug/L
ug/L
ug/L
%REC
%REC
%REC
%REC
Qualifier RL
1
0.1
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/05/10
Collection Date: 02/24/10 08:05
DateReceived: 02/26/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/01/10 11 :501 dvg
E353.2 03/03/10 11 :43 1 jal
SW8260B 03/01110 23: 151 jlr
SW8260B 03/01/1023:151 jlr
SW8260B 03/01/1023:151 jlr
SW8260B 03/01/1023:151 jlr
SW8260B 03/01/1023:151 jlr
SW8260B 03/01/1023:151 jlr
SW8260B 03/0111 023: 151 jlr
SW8260B 03/01/1023:151 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORATORIE5, INC. ·2393 Salt Creek Highway (82601j • po. Box3258 • Casper, WY82602 1999({"y Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABOf?A TORrES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
Lab 10: C 10020848-005
Client Sample 10: TW4-23R
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
NO
NO
NO
2.9
NO
NO
98.0
93.0
89.0
102
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.1
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/05/10
Collection Date: 02/23/10 11 :21
DateReceived: 02/26/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/01/10 11:16/dvg
E353.2 03/0211 0 17:28 1 jal
SW8260B 02127/1007:391 jlr
SW8260B 02/27/1007:391 jlr
SW8260B 02/27/1007:391 jlr
SW8260B 02/2711007:391 jlr
SW8260B 02/27/1007:391 jlr
SW8260B 02/27/1007:391 jlr
SW8260B 02/27/1007:391 jlr
SW8260B 02/27/1007:391 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC •• 2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602 1999f{f2Y Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABORA TOmES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
Lab 10: C 1 0020848-022
Client Sample 10: TW4-24
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-Dichlorobenzene-d4
Surr: Dibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
896
33.1
ND
1.3
ND
ND
99.0
103
88.0
97.0
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
D -Rl increased due to sample matrix interference.
Report Date: 03/05/10
Collection Date: 02/25/10 08: 11
DateReceived: 02126/10
Matrix: Aqueous
MCU
Qualifier RL QCL Method Analysis Date I By
A4500-CI B 03/01/1012:201 dvg
D 0.3 E353.2 03/03/10 12:201 jal
1.0 SW8260B 03/02/10 02:26 1 jlr
1.0 SW8260B 03/02/10 02:26 1 jlr
1.0 SW8260B 03/02/10 02:26 1 jlr
1.0 SW8260B 03/02/10 02:26 1 jlr
80-120 SW8260B 03/02/10 02:26 1 jlr
70-130 SW8260B 03/02110 02:26 1 jlr
80-120 SW8260B 03/02/1002:261 jlr
80-120 SW8260B 03/02/10 02:26 1 jlr
MCl -Maximum contaminant level.
ND -Not detected at the reporting limit.
ENERGY LABORATORIES, INC .• 2393 Salt Creek Highway (82601) • po. Box 3258 • Casper, WY 82602 lUgf{f)7 lOll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
Lab 10: C 1 0020848-01 0
Client Sample 10: TW4-24R
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
NO
NO
NO
2.9
NO
NO
90.0
85.0
91.0
101
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.1
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/05/10
Collection Date: 02/24/10 09:35
DateReceived: 02126/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/01/1011 :381 dvg
E353.2 03/03/10 11: 13 1 jal
SW8260B 02/2711010:501 jlr
SW8260B 02127/1010:501 jlr
SW8260B 02/27/1010:501 jlr
SW8260B 02/27/1010:501 jlr
SW8260B 02/27/1010:501 jlr
SW8260B 02/27/1010:501 jlr
SW8260B 02/27/1010:501 jlr
SW8260B 02/27/1010:501 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC •• 2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602 'ugr{f)7 Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
Lab 10: C 10020848-018
Client Sample 10: TW4-25
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-dB
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
296
14.4
NO
NO
NO
NO
99.0
96.0
B7.0
99.0
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.2
1.0
1.0
1.0
1.0
BO-120
70-130
BO-120
BO-120
Report Date: 03/05/10
Collection Date: 02/23/10 07:35
DateReceived: 02/26/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/01/10 11 :531 dvg
E353.2 03/03/10 11 :45 1 jal
SWB260B 03/01/10 23:54 1 jlr
SWB260B 03/01/1023:541 jlr
SWB260B 03/01/1023:541 jlr
SWB260B 03/01/1023:541 jlr
SWB260B 03/01/1023:541 jlr
SWB260B 03/01/1023:541 jlr
SWB260B 03/01/10 23:54 1 jlr
SWB260B 03/01/10 23:54 1 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC. ·2393 Salt Creek Highway (82601) • po. Box 3258 • Casper, WY 82602
Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • casper@energy/ab.com· www.energy/ab.com
LABORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
Lab 10: C 10020848-006
Client Sample 10: TW4-25R
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
NO
NO
NO
1.2
NO
NO
98.0
88.0
90.0
100
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier Rl
0.1
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/05/10
Collection Date: 02/22/10 11 :20
DateReceived: 02/26/10
Matrix: Aqueous
MCU
QCl Method Analysis Date I By
A4500-CI B 03/01/1011:171 dvg
E353.2 03/03/10 11 :03 1 jal
SW8260B 02/27/1008:17 1 jlr
SW8260B 02/27/1008:17 1 jlr
SW8260B 02/27/1008:17 1 jlr
SW8260B 02/27/1008:171 jlr
SW8260B 02/27/1008:17 1 jlr
SW8260B 02127/1008:171 jlr
SW8260B 02/27/1008:171 jlr
SW8260B 02/27/1008:171 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC. ·2393 Salt Creek Highway (82601) • P.D. Box 3258 • Casper, WY 82602 199m{!2Y TOil Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail] • www.energylab.com
LABO/?A T OR/E 5
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Choloform
Lab 10: C 10030236-007
Client Sample 10: TW4-60
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: T oluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
NO
NO
NO
5.4
NO
NO
96.0
88.0
83.0
99.0
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.1
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/15/10
Collection Date: 03/02/10 08:25
DateReceived: 03/05/10
Matrix: Aqueous
MCU
QCL Method Analysis Date 1 By
A4500-CI B 03/12/10 11 :381 dvg
E353.2 03/10/10 15:27 1 jal
SW8260B 03/06/10 02:531 jlr
SW8260B 03/06/10 02:53 1 jlr
SW8260B 03/06/10 02:53 1 jlr
SW8260B 03/0611 0 02:53 1 jlr
SW8260B 03/06/10 02:53 1 jlr
SW8260B 03/06/10 02:53 1 jlr
SW8260B 03/06/10 02:53 1 jlr
SW8260B 03/06/10 02:53 1 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC •• 2393 Salt Creek Highway (82601) • AD. Box 3258 • Casper, WY 82602 lum{f)7 Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LAl/ORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Denison Mines USA Corp
1 st Quarter Chloroform
C10020658-007
Client Sample 10: TW4-65
Analyses Result
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Surr: 1,2-0ichlorobenzene-d4
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
38
NO
NO
NO
NO
NO
132
112
98.0
109
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
S -Spike recovery outside of advisory limits.
Report Date: 03/02/10
Collection Date: 02/17/1013:34
DateReceived: 02/19/10
Matrix: Aqueous
MCU
Qualifier Rl QCl Method Analysis Date I By
A4500-CI B 03/01/1010:321 dvg
0.1 E353.2 03/01/10 11 :20 1 jal
1.0 SW8260B 02120/10 02:09 1 wen
1.0 SW8260B 02/24/10 01 :55 1 wen
1.0 SW8260B 02/20/10 02:09 1 wen
1.0 SW8260B 02/20/10 02:09 1 wen
S 70-130 SW8260B 02/20/10 02:09 1 wen
80-120 SW8260B 02120/10 02:09 1 wen
80-120 SW8260B 02120/10 02:09 1 wen
80-120 SW8260B 02/20/10 02:09 1 wen
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC •• 2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602 1999f(#!27 To// Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail] • www.energy/ab.com
LABOI?AfORlE5
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Choloform
LablD: C 10030236-008
Client Sample ID: TW4-70
Analyses
MAJOR IONS
Chloride
Nitrogen, Nitrate+Nitrite as N
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
55
5.0
NO
480
NO
NO
98.0
9S.0
89.0
104
Units
mg/l
mg/l
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier RL
0.2
1.0
100
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/15/10
Collection Date: 03/03/10 09:37
DateReceived: 03/05/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
A4500-CI B 03/12/10 11 :501 dvg
E353.2 03/10/10 15:29 1 jal
SW82S0B 03/06/1004:471 jlr
SW82S0B 03/05/10 15:22 1 jlr
SW82S0B 03/0SI10 04:471 jlr
SW82S0B 03/0S/10 04:47 1 jlr
SW82S0B 03/0S/10 04:47 1 jlr
SW82S0B 03/06/1004:471 jlr
SW82S0B 03/06/10 04:47 1 jlr
SW82S0B 03/06/1004:471 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC. • 2393 Salt Creek Highway (82601) • P.o. Box 3258 • Casper, WY 82602 'GGB{"7 Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LASORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
Lab 10: C 10020658-008
Client Sample 10: Trip Blank
Analyses
VOLA TILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Surr: 1,2-0ichlorobenzene-d4
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
NO
NO
NO
NO
114
110
98.0
107
Units
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier Rl
1.0
1.0
1.0
1.0
70-130
80-120
80-120
80-120
Report Date: 03/02/10
Collection Date: 02117110
DateReceived: 02119/10
Matrix: Aqueous
MCU
QCl Method Analysis Date I By
SW8260B 02/20/1002:451 wen
SW8260B 02124/10 01 :20 1 wen
SW8260B 02/20/10 02:45 1 wen
SW8260B 02/20/10 02:45 1 wen
SW8260B 02/20/10 02:45 1 wen
SW8260B 02120/10 02:45 1 wen
SW8260B 02/20/10 02:45 1 wen
SW8260B 02/20/1002:451 wen
Mel -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC. ·2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602 1999r{fa7 Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LAflORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Chloroform
LablD: C 1 0020848-027
Client Sample 10: Trip Blank
Analyses
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result
NO
NO
NO
NO
97.0
87.0
85.0
100
Units
ug/L
ug/L
ug/L
ug/L
%REC
%REC
%REC
%REC
Qualifier RL
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/05/10
Collection Date: 02/25/10 08:33
DateReceived: 02/26/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
SW8260B 03/0211 004:21 1 jlr
SW8260B 03/02/1004:211 jlr
SW8260B 03/02/10 04:21 1 jlr
SW8260B 03/02/1004:21 1 jlr
SW8260B 03/0211 0 04:21 1 jlr
SW8260B 03/0211004:21 1 jlr
SW8260B 03/02/1004:211 jlr
SW8260B 03/02/10 04:21 1 jlr
MCL -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC. ·2393 Salt Creek Highway (82601) • P.o. Box 3258 • Casper, WY 82602 'UB(f>Y Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABORA TORIES
LABORATORY ANALYTICAL REPORT
Client:
Project:
Denison Mines USA Corp
1 st Quarter Choloform
Lab 10: C 10030236-016
Client Sample 10: Trip Blank
Analyses
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
Result
NO
NO
NO
NO
106
91.0
89.0
99.0
Units
ug/l
ug/l
ug/l
ug/l
%REC
%REC
%REC
%REC
Qualifier Rl
1.0
1.0
1.0
1.0
80-120
70-130
80-120
80-120
Report Date: 03/15/10
Collection Date: 03/03/10
DateReceived: 03/05/10
Matrix: Aqueous
MCU
QCl Method Analysis Date I By
SW8260B 03/06/10 00:58 1 jlr
SW8260B 03/06/1000:581 jlr
SW8260B 03/06/1000:581 jlr
SW8260B 03/06/10 00:58 1 jlr
SW8260B 03/06/10 00:58 1 jlr
SW8260B 03/06/10 00:58 1 jlr
SW8260B 03/06/10 00:58 1 jlr
SW8260B 03/06/10 00:58 1 jlr
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORATORIE~ INC .• 2393 Salt Creek Highway (82601j • Po. Box3258 • Casper, WY82602 1999f{f'l7 Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • casper@energy/ab.com· www.energy/ab.com
LABORA TORIES -----
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Denison Mines USA Corp
1 st Quarter Choloform
C 10030236-017
Client Sample 10: Temp Blank
Analyses Result Units
PHYSICAL PROPERTIES
Temperature
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
2.0
Qualifier RL
Report Date: 03/15/10
Collection Date: 03/03/10
DateReceived: 03/05/10
Matrix: Aqueous
MCU
QCL Method Analysis Date I By
E170.1 03/05/10 09: 15 1 kbh
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC. ·2393 Salt Creek Highway (82601) • po. Box 3258 • Casper, WY 82602 1999f{f27 To// Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
I ABORA TORIES
ANALYTICAL SUMMARY REPORT
March 02, 2010
Denison Mines USA Corp
6425 S Hwy 191
Blanding, UT 84511
Workorder No.: C10020658
Project Name: 1 st Quarter Chloroform
Quote 10: C2975 -Chloroform Sampling
Energy Laboratories, Inc. received the following 8 samples for Denison Mines USA Corp on 2119/2010 for analysis.
Sample ID Client Sample ID Collect Date Receive Date Matrix Test
C10020658-001 TW4-17 02117/10 13:34 02/19/10 Aqueous Chloride
Nitrogen, Nitrate + Nitrite
SW8260B VOCs, Standard List
C 10020658-002 TW4-4 02/17/1015:10 02/19/10 Aqueous Same As Above
C 10020658-003 TW4-15 02117/1014:52 02/19/10 Aqueous Same As Above
C10020658-004 MW-4 02/17/10 15:03 02/19/10 Aqueous Same As Above
C 10020658-005 TW4-19 02/17/10 14:30 02/19/10 Aqueous Same As Above
C10020658-006 TW4-20 02/17/10 14:42 02/19/10 Aqueous Same As Above
C 10020658-007 TW4-65 02/17/10 13:34 02/19/10 Aqueous Same As Above
C10020658-008 Trip Blank 02/17/10 00:00 02/19/10 Aqueous SW8260B VOCs, Standard List
Any exceptions or problems with the analyses are noted in the Laboratory Analytical Report, the QA/QC Summary
Report, or the Case Narrative.
The results as reported relate only to the item(s) submitted for testing.
If you have any questions regarding these test results, please call.
Report Approved By:
Reporting Supervisor
ENERGY LABORATORIES, INC •• 2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602 lU,f{f27 lOll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABORA TORIES
QAlQC Summary Report
Client: Denison Mines USA Corp
Project: 1 st Quarter Chloroform
Analyte Count Result Units
Method: A4500-C1 B
Sample 10: MBLK9-100301A
Chloride
Sample 10: C10020667-001AMS
Chloride
Sample 10: C10020667-001AMSO
Chloride
Sample 10: LCS35-100301A
Chloride
Qualifiers:
RL -Analyte reporting limit.
Method Blank
ND mg/L
Sample Matrix Spike
211 mg/L
Sample Matrix Spike Duplicate
211 mg/L
Laboratory Control Sample
3720 mg/L
Report Date: 03/02/10
Work Order: C10020658
RL O/OREC Low Limit High Limit RPO RPOLimit Qual
Batch: 100301A-CL-TIR-W
Run: TITRATION_100301A 03/01/1009:47
0.4
Run: TITRATION_100301A 03/01/1010:39
3.0 99 90 110
Run: TITRATION_100301A 03/01/1010:40
3.0 99 90 110 0 10
Run: TITRATION_100301A 03/01/10 11 :32
1.0 105 90 110
ND -Not detected at the reporting limit.
ENERGY LABORATORIES, INC •• 2393 Salt Creek Highway (82601) • P.o. Box 3258 • Casper, WY 82602 lUgf{f2Y lOll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
I AflORA TORIES
QAlQC Summary Report
Client: Denison Mines USA Corp Report Date: 03/02/10
Project: 1 st Quarter Chloroform Work Order: C10020658
Analyte Count Result Units RL %REC Low Limit High Limit RPD RPDLimit Qual
Method: E353.2 Batch: R130143
Sample 10: MBLK-1 Method Blank Run: TECHNICON_100301A 03/01/1007:56
Nitrogen, Nitrate+Nitrite as N NO mg/L 0.03
Sample 10: LCS-2 Laboratory Control Sample Run: TECHNICON_100301A 03/01/1007:59
Nitrogen, Nitrate+Nitrite as N 2.74 mg/L 0.10 110 90 110
Sample 10: C10020806-007AMS Sample Matrix Spike Run: TECHNICON_100301A 03/01/1010:08
Nitrogen, Nitrate+Nitrite as N 2.46 mg/L 0.10 98 90 110
Sample 10: C1 0020806-007 AMSO Sample Matrix Spike Duplicate Run: TECHNICON_100301A 03/01/1010:10
Nitrogen, Nitrate+Nitrite as N 2.58 mg/L 0.10 104 90 110 4.8 10
Sample 10: C10020850-0030MS Sample Matrix Spike Run: TECHNICON_100301A 03/01110 12:08
Nitrogen, Nitrate+Nitrite as N 2.53 mg/L 0.10 107 90 110
Sample 10: C10020850-0030MSO Sample Matrix Spike Duplicate Run: TECHNICON_1 00301 A 03/01/1012:10
Nitrogen, Nitrate+Nitrite as N 2.55 mg/L 0.10 108 90 110 0.8 10
Qualifiers:
RL -Analyte reporting limit. NO -Not detected at the reporting limit.
lili,lflI ENERGY LABORATORIES, INC. ·2393 Salt Creek Highway (82601) • P.o. Box 3258 • Casper, WY 82602
Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • casper@energy/ab.com· www.energy/ab.com
'.Jlj·U&fi!##/4.
QAlQC Summary Report
Client: Denison Mines USA Corp Report Date: 02/25/10
Project: 1 st Quarter Chloroform Work Order: C10020658
I I
I Analyte Result Units RL %REC Low Limit High Limit RPO RPOLimit Qual
Method: SW8260B Batch: R129882
Sample 10: 19-Feb-10_LCS_3 Laboratory Control Sample Run: GCMS2_100219A 02/19/1010:47
Carbon tetrachloride 11 ug/L 1.0 106 70 130
Chloroform 10 ug/L 1.0 104 70 130
Chloromethane 7.6 ug/L 1.0 76 70 130
Methylene chloride 9.2 ug/L 1.0 92 70 130
Surr: Dibromofluoromethane 1.0 112 70 130
Surr: p-Bromofluorobenzene 1.0 107 80 130
Surr: Toluene-d8 1.0 99 80 120
Surr: 1 ,2-Dichlorobenzene-d4 1.0 110 80 120
Sample 10: 19-Feb_MBLK_6 Method Blank Run: GCMS2_ 100219A 02/19/10 12:37
Carbon tetrachloride ND ug/L 1.0
Chloroform ND ug/L 1.0
Chloromethane ND ug/L 1.0
Methylene chloride ND ug/L 1.0
Surr: Dibromofluoromethane 1.0 108 70 130
Surr: p-Bromofluorobenzene 1.0 110 80 120
Surr: Toluene-d8 1.0 97 80 120
Surr: 1 ,2-Dichlorobenzene-d4 1.0 108 80 120
Sample 10: C1 0020458-001 EMS Sample Matrix Spike Run: GCMS2_100219A 02/19/1018:30
Carbon tetrachloride 190 ug/L 20 95 70 130
Chloroform 190 ug/L 20 97 70 130
Chloromethane 160 ug/L 20 78 70 130
Methylene chloride 190 ug/L 20 96 70 130
Surr: Dibromofluoromethane 20 100 70 130
Surr: p-Bromofluorobenzene 20 103 80 120
Surr: Toluene-d8 20 100 80 120
Surr: 1,2-Dichlorobenzene-d4 20 106 80 120
Sample 10: C1 0020458-001 EMSO Sample Matrix Spike Duplicate Run: GCMS2_ 100219A 02/19/10 19:05
Carbon tetrachloride 190 ug/L 20 97 70 130 2.5 20
Chloroform 200 ug/L 20 98 70 130 0.8 20
Chloromethane 160 ug/L 20 79 70 130 20
Methylene chloride 200 ug/L 20 100 70 130 3.7 20
Surr: Dibromofluoromethane 20 99 70 130 0 10
Surr: p-Bromofluorobenzene 20 104 80 120 0 10
Surr: Toluene-d8 20 99 80 120 0 10
Surr: 1,2-Dichlorobenzene-d4 20 106 80 120 0 10
Qualifiers:
RL -Analyte reporting limit. ND -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC. • 2393 Salt Creek Highway (82601) • P.O. Box 3258 • Casper, WY 82602 199m{f2Y Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail] • www.energylab.com
LAHORA TORIES
QAlQC Summary Report
Client: Denison Mines USA Corp Report Date: 02/25/10
Project: 1 st Quarter Chloroform Work Order: C10020658
I I~nalyte Result Units RL %REC Low Limit High Limit RPO RPOLimit Qual
Method: SW8260B Batch: R 129944
Sample 10: 23-Feb-10_LCS_3 Laboratory Control Sample Run: GCMS2_100223A 02/23/1013:37
Chloroform 11 ug/L 1.0 110 70 130
Surr: Dibromofluoromethane 1.0 103 70 130
Surr: p-Bromofluorobenzene 1.0 98 80 130
Surr: Toluene-d8 1.0 102 80 120
Surr: 1,2-Dichlorobenzene-d4 1.0 109 80 120
Sample 10: 23-Feb_MBLK_6 Method Blank Run: GCMS2_100223A 02/23/1015:22
Chloroform NO ug/L 1.0
Surr: Dibromofluoromethane 1.0 101 70 130
Surr: p-Bromofluorobenzene 1.0 104 80 120
Surr: Toluene-d8 1.0 97 80 120
Surr: 1,2-Dichlorobenzene-d4 1.0 108 80 120
Sample 10: C10020658-003CMS Sample Matrix Spike Run: GCMS2_100223A 02/23/10 22:59
Chloroform 1800 ug/L 100 101 70 130
Surr: Dibromofluoromethane 100 103 70 130
Surr: p-Bromofluorobenzene 100 96 80 120
Surr: Toluene-d8 100 99 80 120
Surr: 1,2-Dichlorobenzene-d4 100 110 80 120
Sample 10: C10020658-003CMSO Sample Matrix Spike Duplicate Run: GCMS2_100223A 02/23/10 23:34
Chloroform 1800 ug/L 100 103 70 130 1.1 20
Surr: Dibromofluoromethane 100 102 70 130 0 10
Surr: p-Bromofluorobenzene 100 98 80 120 0 10
Surr: Toluene-d8 100 99 80 120 0 10
Surr: 1 ,2-Dichlorobenzene-d4 100 111 80 120 0 10
-------------------------------_._--_._----------
Qualifiers:
RL -Analyte reporting limit. NO -Not detected at the reporting limit.
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Date/Time:
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Receipt Temp
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On Cooler ~ N
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Signature
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Flecord ~~~~~~~~~~~~~~~~L-----~~~~~~~==-+~R~~-e~iVed~b-y~(p~rin~t):--------~D~a~te~~~im-e:---------------=si-gn~at~ur-e:------------~
MUSTbe~----------------------~~------~~~~~ ____ ~~ ________ ~~~~~~
Signed Return to Client:
In certain circumstances, samples submitted to Energy Laboratories, Inc. may be subcontracted to other certified laboratories in order to complete the ana.
This serves as notice of this possibility. All sub-contract data will be clearly notated on your analytical report.
Visit our web site at www.energylab.com for additional information, downloadable fee schedule, forms, and links.
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Denison Mines USA Corp
Login completed by: Halley Ackerman
Reviewed by:
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Shipping container/cooler in good condition?
Custody seals intact on shipping container/cooler?
Custody seals intact on sample bottles?
Chain of custody present?
Chain of custody signed when relinquished and received?
Chain of custody agrees with sample labels?
Samples in proper container/bottle?
Sample containers intact?
Sufficient sample volume for indicated test?
All samples received within holding time?
ContainerfTemp Blank temperature:
Water -VOA vials have zero headspace?
Water -pH acceptable upon receipt?
Contact and Corrective Action Comments:
None
Yes 0
Yes 0
Yes 0
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Yes 0
Yes 0
Yes 0
Yes 0
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2°C On Ice
Yes 0
Yes 0
C10020658
Date and Time Received: 2/19/20109:30 AM
Received by: al
No D
No 0
No D
No D
No D
No D
No 0
No D
No 0
No D
No 0
No D
Carrier name: FedEx
Not Present D
Not Present 0
Not Present 0
No VOA vials submitted D
Not Applicable D
ENERGY LABORATORIES, INC. ·2393 Salt Creek Highway (82601) • P.o. Box 3258 • Casper, WY 82602 '6gB {""? Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LARORA lomES
ANALYTICAL SUMMARY REPORT
March 05, 2010
Denison Mines USA Corp
6425 S Hwy 191
Blanding, UT 84511
Workorder No.: C10020848
Project Name: 1 st Quarter Chloroform
Quote 10: C2975 -Chloroform Sampling
Energy Laboratories, Inc. received the following 27 samples for Denison Mines USA Corp on 2/26/2010 for analysis.
Sample 10 Client Sample 10 Collect Date Receive Date Matrix Test
C10020848-001 TW4-3R 02/22/10 09:45 02/26/10 Aqueous Chloride
Nitrogen, Nitrate + Nitrite
SW8260B VOCs, Standard List
C 10020848-002 TW4-12R 02122/10 14:27 02126/10 Aqueous Same As Above
C 10020848-003 TW4-13R 02123/10 13:02 02126/10 Aqueous Same As Above
C 1 0020848-004 TW4-14R 02/23/10 14:08 02/26/10 Aqueous Same As Above
C 10020848-005 TW4-23R 02/23/10 11 :21 02/26/1 0 Aqueous Same As Above
C10020848-006 TW4-25R 02/22/10 11 :20 02/26/10 Aqueous Same As Above
C 10020848-007 TW4-8R 02123/10 09:40 02/26/10 Aqueous Same As Above
C10020848-008 TW4-9R 02122110 12:25 02/26/10 Aqueous Same As Above
C 10020848-009 TW4-16R 02/23/10 10:35 02/26/10 Aqueous Same As Above
C10020848-010 TW4-24R 02/24/10 09:35 02/26/10 Aqueous Same As Above
C 10020848-011 TW4-5R 02/24/10 12:30 02/26/10 Aqueous Same As Above
C10020848-012 TW4-21R 02124/10 13:25 02/26/10 Aqueous Same As Above
C 10020848-013 TW4-6R 02124/10 15:00 02126/10 Aqueous Same As Above
C10020848-014 TW4-3 02123/1008:52 02/26/10 Aqueous Same As Above
C10020848-015 TW4-12 02/23/10 08:20 02/26/10 Aqueous Same As Above
C10020848-016 TW4-13 02/24/10 07:45 02/26/10 Aqueous Same As Above
C10020848-017 TW4-23 02124/10 08:05 02/26/10 Aqueous Same As Above
C 10020848-018 TW4-25 02/23/1007:35 02/26/10 Aqueous Same As Above
C10020848-019 TW4-8 02/24/1008:35 02/26/10 Aqueous Same As Above
C 10020848-020 TW4-9 02/23/10 09:05 02/26/10 Aqueous Same As Above
C 10020848-021 TW4-16 02/24/10 08: 15 02/26/10 Aqueous Same As Above
C 10020848-022 TW4-24 02/25/1008:11 02/26/10 Aqueous Same As Above
C 10020848-023 TW4-18 02124/10 10:50 02126/10 Aqueous Same As Above
ENERGY LABORATORIE~ INC •• 2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602
Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
ANALYTICAL SUMMARY REPORT
C 10020848-024 TW4-5 02/25/10 08:22 02126/10 Aqueous Same As Above
C 10020848-025 TW4-21 02/25/1008:05 02/26/10 Aqueous Same As Above
C 10020848-026 TW4-6 02/25/10 08:33 02/26/10 Aqueous Same As Above
C10020848-027 Trip Blank 02/25/10 08:33 02/26/10 Aqueous SW8260B VOCs, Standard List
Any exceptions or problems with the analyses are noted in the Laboratory Analytical Report, the QA/QC Summary
Report, or the Case Narrative.
The results as reported relate only to the item(s) submitted for testing.
If you have any questions regarding these test results, please call.
Report Approved By:
ENERGY LABORATORIES, INC. • 2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602 199m{e'lW Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LAHORA TORIES
QA/QC Summary Report
Client: Denison Mines USA Corp Report Date: 03/05/10
Project: 1 st Quarter Chloroform Work Order: C10020848
Analyte Count Result Units RL %REC Low Limit High Limit RPO RPOLimit Qual
Method: A4500-CI B Batch: 100301 A-CL-TTR-W
Sample 10: MBLK9-100301A Method Blank Run: TITRATION_100301A 03/01/1009:47
Chloride NO mg/L 0.4
Sample 10: C10020667-001AMS Sample Matrix Spike Run: TITRATION_100301A 03/01/10 10:39
Chloride 211 mg/L 3.0 99 90 110
Sample 10: C10020667-001AMSO Sample Matrix Spike Duplicate Run: TITRATION_100301A 03/01/10 10:40
Chloride 211 mg/L 3.0 99 90 110 0 10
Sample 10: C10020667-002AMS Sample Matrix Spike Run: TITRATION_100301A 03/01/10 11 :29
Chloride 214 mg/L 3.0 101 90 110
Sample 10: C1 0020667 -002AMSO Sample Matrix Spike Duplicate Run: TITRATION_100301A 03/0111 0 11 :30
Chloride 213 mg/L 3.0 100 90 110 0.8 10
Sample 10: LCS35-100301A Laboratory Control Sample Run: TITRATION_100301A 03/01/10 11 :32
Chloride 3720 mg/L 1.0 105 90 110
Sample 10: C10020848-017AMS Sample Matrix Spike Run: TITRATION_100301A 03/01110 11 :57
Chloride 225 mg/L 1.0 101 90 110
Sample 10: C10020848-017AMSO Sample Matrix Spike Duplicate Run: TITRATION_100301A 03/0111011 :58
Chloride 223 mg/L 1.0 100 90 110 0.8 10
Sample 10: C10020848-020A Sample Matrix Spike Run: TITRATION_100301A 03/01/1014:47
Chloride 407 mg/L 1.0 102 90 110
Sample 10: C10020848-020A Sample Matrix Spike Duplicate Run: TITRATION_100301A 03/0111014:49
Chloride 415 mg/L 1.0 104 90 110 1.7 10
Qualifiers:
RL -Analyte reporting limit. NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC. • 2393 Salt Creek Highway (82601) • P.o. Box 3258 • Casper, WY 82602 199;{({f'l7 Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABORA TORIES
QA/QC Summary Report
Client: Denison Mines USA Corp Report Date: 03/05/10
Project: 1 st Quarter Chloroform Work Order: C10020848
Analyte Count Result Units RL %REC Low Limit High Limit RPO RPOLimit Qual
Method: E353.2 Batch: R130213
Sample 10: MBLK-1 Method Blank Run: TECHNICON_100302B 03/0211 0 16:43
Nitrogen, Nitrate+Nitrite as N NO mg/L 0.03
Sample 10: LCS-2 Laboratory Control Sample Run: TECHNICON_100302B 03/02/10 16:46
Nitrogen, Nitrate+Nitrite as N 2.42 mg/L 0.10 97 90 110
Sample 10: C10020B4B-003BMS Sample Matrix Spike Run: TECHNICON_100302B 03/02/10 17:01
Nitrogen, Nitrate+Nitrite as N 1.80 mg/L 0.10 90 90 110
Sample 10: C1002084B-003BMSO Sample Matrix Spike Duplicate Run: TECHNICON_100302B 03/02/1017:03
Nitrogen, Nitrate+Nitrite as N 1.82 mg/L 0.10 91 90 110 1.1 10
Method: E353.2 Batch: R130242
Sample 10: MBLK-1 Method Blank Run: TECHNICON_100303A 03/03/10 10:58
Nitrogen, Nitrate+Nitrite as N NO mg/L 0.03
Sample 10: LCS-2 Laboratory Control Sample Run: TECHNICON_100303A 03/03/10 11 :00
Nitrogen, Nitrate+Nitrite as N 2.49 mg/L 0.10 90 90 110
Sample 10: C10020B4B-010BMS Sample Matrix Spike Run: TECHNICON_100303A 03/03/10 11: 15
Nitrogen, Nitrate+Nitrite as N 2.15 mg/L 0.10 107 90 110
Sample 10: C1 0020B4B-01 OBMSO Sample Matrix Spike Duplicate Run: TECHNICON_100303A 03/03/10 11: 18
Nitrogen, Nitrate+Nitrite as N 2.19 mg/L 0.10 109 90 110 1.B 10
Sample 10: C10020B4B-020BMS Sample Matrix Spike Run: TECHNICON_1 00303A 03/03/10 11 :53
Nitrogen, Nitrate+Nitrite as N 3.46 mg/L 0.10 105 90 110
Sample 10: C10020B4B-020BMSO Sample Matrix Spike Duplicate Run: TECHNICON_100303A 03/03/10 11 :55
Nitrogen, Nitrate+Nitrite as N 3.47 mg/L 0.10 106 90 110 0.3 10
Sample 10: C1 0020B23-001 GMS Sample Matrix Spike Run: TECHNICON_100303A 03/03/10 12:35
Nitrogen, Nitrate+Nitrite as N 2.14 mg/L 0.10 107 90 110
Sample 10: C1 0020B23-001 GMSO Sample Matrix Spike Duplicate Run: TECHNICON_100303A 03/03/10 12:38
Nitrogen, Nitrate+Nitrite as N 2.16 mg/L 0.10 10B 90 110 0.9 10
Qualifiers:
RL -Analyte reporting limit. NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC. • 2393 Salt Creek Highway (82601) • po. Box 3258 • Casper, WY 82602 199;{({e!7 lOll Free 888.235.0515 • 307.235.0515· Fax [phone] • [e-mail] • www.energylab.com
LABORA TORIES
Client: Denison Mines USA Corp
Project: 1 st Quarter Chloroform
Analyte
Method: SW8260B
Sample 10: 022610_LCS_5
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: Dibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Surr: 1,2-Dichlorobenzene-d4
Sample 10: 022610_MBLK_8
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: Dibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: T oluene-d8
Surr: 1,2-Dichlorobenzene-d4
Sample 10: C10020808-002BMS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: Dibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Surr: 1,2-Dichlorobenzene-d4
Sample 10: C10020808-002BMSO
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: Dibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Surr: 1,2-Dichlorobenzene-d4
Qualifiers:
RL -Analyte reporting limit.
QA/Qc Summary Report
Report Date: 03/03/10
Work Order: C10020848
~
Result Units RL %REC Low Limit High Limit RPO RPOLimit Qual I
Batch: R130120
Laboratory Control. Sample Run: SATURNCA_100226C 02/26/10 15:07
10 ug/L 1.0 102 70 130
11 ug/L 1.0 108 70 130
9.2 ug/L 1.0 92 70 130
11 ug/L 1.0 109 70 130
1.0 98 70 130
1.0 98 80 130
1.0 103 80 120
1.0 96 80 120
Method Blank Run: SATURNCA_100226C 02/26/10 17:00
ND ug/L 1.0
ND ug/L 1.0
ND ug/L 1.0
ND ug/L 1.0
1.0 96 70 130
1.0 99 80 120
1.0 99 80 120
1.0 95 80 120
Sample Matrix Spike Run: SATURNCA_100226C 02/26/10 23:59
100 ug/L 10 104 70 130
110 ug/L 10 109 70 130
100 ug/L 10 103 70 130
120 ug/L 10 116 70 130
10 101 70 130
10 97 80 120
10 97 80 120
10 94 80 120
Sample Matrix Spike Duplicate Run: SATURNCA_100226C 02/27/1000:38
100 ug/L 10 101 70 130 3.5 20
110 ug/L 10 110 70 130 0.7 20
99 ug/L 10 99 70 130 4.4 20
120 ug/L 10 115 70 130 1 20
10 102 70 130 0 10
10 102 80 120 0 10
10 98 80 120 0 10
10 103 80 120 0 10
ND -Not detected at the reporting limit.
ENERGY LABORATORIE~ INC. ·2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602 Igg:{({r,7 Toll Free 888.235.0515 • 307.235.0515' Fax [phone] • [e-mail] • www.energylab.com
LABORA TORIES
QAlQC Summary Report
Client: Denison Mines USA Corp Report Date: 03/03/10
Project: 1 st Quarter Chloroform Work Order: C10020848
Analyte Result Units RL %REC Low Limit High Limit RPO RPOLimit Qual
Method: SW8260B Batch: R130167
Sample 10: 030110_LCS_3 Laboratory Control Sample Run: SATURNCA_1 00301 B 03/01/1011 :42
Carbon tetrachloride 9.5 ug/L 1.0 95 70 130
Chloroform 9.6 ug/L 1.0 96 70 130
Chloromethane 8.8 ug/L 1.0 88 70 130
Methylene chloride 9.9 ug/L 1.0 99 70 130
Surr: Dibromofluoromethane 1.0 98 70 130
Surr: p-Bromofluorobenzene 1.0 100 80 130
Surr: Toluene-d8 1.0 106 80 120
Surr: 1,2-Dichlorobenzene-d4 1.0 92 80 120
Sample 10: 030110_MBLK_6 Method Blank Run: SATURNCA_100301B 03/01/10 13:35
Carbon tetrachloride ND ug/L 1.0
Chloroform ND ug/L 1.0
Chloromethane ND ug/L 1.0
Methylene chloride ND ug/L 1.0
Surr: Dibromofluoromethane 1.0 82 70 130
Surr: p-Bromofluorobenzene 1.0 95 80 120
Surr: Toluene-d8 1.0 104 80 120
Surr: 1,2-Dichlorobenzene-d4 1.0 96 80 120
Sample 10: C10020848-026CMS Sample Matrix Spike Run: SATURNCA_1 00301 B 03/01/1019:24
Carbon tetrachloride 960 ug/L 100 96 70 130
Chloroform 1900 ug/L 100 84 70 130
Chloromethane 860 ug/L 100 86 70 130
Methylene chloride 1000 ug/L 100 104 70 130
Surr: Dibromofluoromethane 100 97 70 130
Surr: p-Bromofluorobenzene 100 95 80 120
Surr: Toluene-d8 100 98 80 120
Surr: 1,2-Dichlorobenzene-d4 100 92 80 120
Sample 10: C10020848-026CMSO Sample Matrix Spike Duplicate Run: SATURNCA_100301B 03/01/1020:02
Carbon tetrachloride 1000 ug/L 100 102 70 130 6.1 20
Chloroform 1900 ug/L 100 91 70 130 3.4 20
Chloromethane 920 ug/L 100 92 70 130 6.7 20
Methylene chloride 1100 ug/L 100 106 70 130 1.5 20
Surr: Dibromofluoromethane 100 94 70 130 0 10
Surr: p-Bromofluorobenzene 100 95 80 120 0 10
Surr: Toluene-d8 100 96 80 120 0 10
Surr: 1,2-Dichlorobenzene-d4 100 95 80 120 0 10
Qualifiers:
RL -Analyte reporting limit. ND -Not detected at the reporting limit.
ENERGYLABORATORIE~ INC. ·~393Sa/tCreekHighway(82601) -P.O Box3258 -Casper, WY82602 tUgf{""'" Toll Free 888.235.0515 -307.235.0515: -Fax [phone] -casper@energy/ab.com -www.energy/ab.com
LASORA TORIES
QAlQC Summary Report
Client: Denison Mines USA Corp Report Date: 03/03/10
Project: 1 st Quarter Chloroform Work Order: C10020848
Analyte Result Units RL %REC Low Limit High Limit RPO RPOLimit Qual
Method: SW8260B Batch: R130235
Sample 10: 030210_LCS_3 Laboratory Control Sample Run: SATURNCA_100302A 03/0211012:30
Carbon tetrachloride 9.9 ug/L 1.0 99 70 130
Chloroform 9.7 ug/L 1.0 97 70 130
Chloromethane 8.8 ug/L 1.0 88 70 130
Methylene chloride 10 ug/L 1.0 102 70 130
Surr: Dibromofluoromethane 1.0 90 70 130
Surr: p-Bromofluorobenzene 1.0 97 80 130
Surr: Toluene-d8 1.0 108 80 120
Surr: 1,2-Dichlorobenzene-d4 1.0 94 80 120
Sample 10: 030210_MBLK_8 Method Blank Run: SATURNCA_100302A 03/02/10 16:28
Carbon tetrachloride NO ug/L 1.0
Chloroform NO ug/L 1.0
Chloromethane NO ug/L 1.0
Methylene chloride NO ug/L 1.0
Surr: Dibromofluoromethane 1.0 99 70 130
Surr: p-Bromofluorobenzene 1.0 90 80 120
Surr: Toluene-d8 1.0 108 80 120
Surr: 1,2-Dichlorobenzene-d4 1.0 93 80 120
Sample 10: C10020848-023CMS Sample Matrix Spike Run: SATURNCA_100302A 03/0211019:00
Carbon tetrachloride 110 ug/L 10 106 70 130
Chloroform 190 ug/L 10 121 70 130
Chloromethane 92 ug/L 10 92 70 130
Methylene chloride 110 ug/L 10 106 70 130
Surr: Dibromofluoromethane 10 94 70 130
Surr: p-Bromofluorobenzene 10 95 80 120
Surr: Toluene-d8 10 99 80 120
Surr: 1,2-Dichlorobenzene-d4 10 95 80 120
Sample 10: C10020848-023CMSO Sample Matrix Spike Duplicate Run: SATURNCA_100302A 03/02/10 19:38
Carbon tetrachloride 95 ug/L 10 95 70 130 10 20
Chloroform 170 ug/L 10 101 70 130 11 20
Chloromethane 87 ug/L 10 87 70 130 6.3 20
Methylene chloride 99 ug/L 10 99 70 130 6.3 20
Surr: Dibromofluoromethane 10 84 70 130 0 10
Surr: p-Bromofluorobenzene 10 97 80 120 0 10
Surr: Toluene-d8 10 98 80 120 0 10
Surr: 1,2-Dichlorobenzene-d4 10 97 80 120 0 10
Qualifiers:
RL -Analyte reporting limit. NO -Not detected at the reporting limit.
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Contact Name: afw.u Phone/Fax:
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In certain circumstances, samples submitted to Energy Laboratories, Inc. may be subcontracted to other certified laboratories in order to complete the analysis r
This serves as notice of this possibility. All sub-contract data will be clearly notated on your analytical report.
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I,g;[({ety
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MUSTbe~--------------------~----------~~~~~ __ ~~~ ______ ~~~~~ __ ~
Signed Return to Client:
In certain circumstances, samples submitted to Energy Laboratories, Inc. may be subcontracted to other certified laboratories in order to complete the analy
This serves as notice of this possibility. All sub-contract data will be clearly notated on your analytical report.
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CO~Name: Project Na e, PWS, Permit, Etc. EPA/StaJ Compliance: ~t'Jlh~O'" 1n,'Ncs SI ~lAltlEd cltkoFd£11Il Yes [g' No 0
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MUSTbe~------------------~---------
Signed Sample Disposal: Return to Client: Lab Disposal: 7.:l~
In certain circumstances, samples submitted to Energy Laboratories, Inc. may be subcontracted to other certified laboratories in order to complete the anal~~ested.
This serves as notice of this possibility. All sub-contract data will be clearly notated on your analytical report.
Visit our web site at www.energylab.com for additional information, downloadable fee schedule, forms, and links.
Energy Laboratories Inc
Workorder Receipt Checklist
Denison Mines USA Corp
Login completed by: Halley Ackerman
Reviewed by:
Reviewed Date:
Shipping container/cooler in good condition?
Custody seals intact on shipping container/cooler?
Custody seals intact on sample bottles?
Chain of custody present?
Chain of custody signed when relinquished and received?
Chain of custody agrees with sample labels?
Samples in proper container/bottle?
Sample containers intact?
Sufficient sample volume for indicated test?
All samples received within holding time?
ContainerfTemp Blank temperature:
Water -VOA vials have zero headspace?
Water -pH acceptable upon receipt?
Contact and Corrective Action Comments:
Yes [{1
Yes [{1
Yes D
Yes [{1
Yes [{1
Yes [{1
Yes [{1
Yes [{1
Yes [{1
Yes [{1
Yes [{1
Yes [{1
IIIIIIII~ 1IIIIIi III ~IIIIIIIIIIIIIIIIIII
.C10020848
Date Received: 2/26/2010
Received by: al
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Carrier name: FedEx
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Not Applicable D
l '-ENERGY LABORATORIE~ INC .• 2393 Salt Creek Highway (82601) • Po. Box 3258 • Casper, WY 82602 .rggr{#!27 Toll Free 888235.0515 • 307235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LASORA TORIES
CLIENT: Denison Mines USA Corp
Project: 1 st Quarter Chloroform Report Date: 03/05/10
Sample Delivery Group: C10020848 CASE NARRATIVE
ORIGINAL SAMPLE SUBMITTAL(S)
All original sample submittals have been returned with the data package.
SAMPLE TEMPERATURE COMPLIANCE: 4°C (~OC)
Temperature of samples received may not be considered properly preserved by accepted standards. Samples that are hand
delivered immediately after collection shall be considered acceptable if there is evidence that the chilling process has begun.
GROSS ALPHA ANALYSIS
Method 900.0 for gross alpha and gross beta is in_ended as a drinking water method for low TDS waters. Data provided by
this method for non potable waters should be viewed as inconsistent.
RADON IN AIR ANALYSIS
The desired exposure time is 48 hours (2 days). The time delay in returning the canister to the laboratory for processing
should be as short as possible to avoid excessive decay. Maximum recommended delay between end of exposure to
beginning of counting should not exceed 8 days.
SOIUSOLlD SAMPLES
All samples reported on an as received basis unless otherwise indicated.
ATRAZINE, SIMAZINE AND PCB ANALYSIS
Data for PCBs, Atrazine and Simazine are reported from EPA 525.2. PCB data reported by ELI reflects the results for seven
individual Aroclors. When the results for all seven are ND (not detected), the sample meets EPA compliance criteria for
PCB monitoring.
SUBCONTRACTING ANALYSIS
Subcontracting of sample analyses to an outside laboratory may be required. If so, ENERGY LABORATORIES will utilize its
branch laboratories or qualified contract laboratories for this service. Any such laboratories will be indicated within the
Laboratory Analytical Report.
BRANCH LABORATORY LOCATIONS
eli-b -Energy Laboratories, Inc. -Billings, MT
eli-g -Energy Laboratories, Inc. -Gillette, WY
eli-h -Energy Laboratories, Inc. -Helena, MT
eli-r -Energy Laboratories, Inc. -Rapid City, SO
eli-t -Energy Laboratories, Inc. -College Station, TX
CERTIFICATIONS:
USEPA: WY00002, Radiochemical WY00937; FL·DOH NELAC: E87641, Radiochemical E871017; California: 02118CA;
Oregon: WY200001; Utah: 3072350515; Virginia: 00057; Washington: C1903
ISO 17025 DISCLAIMER:
The results of this Analytical Report relate only to the items submitted for analysis.
ENERGY LABORATORIES, INC. -CASPER,WY certifies that certain method selections contained in this report meet
requirements as set forth by the above accrediting authorities. Some results requested by the client may not be covered
under these certifications. All analysis data to be submitted for regulatory enforcement should be certified in the sample
state of origin. Please verify ELI's certification coverage by visiting www.energylab.com
ELI appreciates the opportunity to provide you with this analytical service. For additional information and services visit our
web page www.energylab.com.
THIS IS THE FINAL PAGE OF THE LABORATORY ANALYTICAL REPORT
ENERGY LABORATORIE~ INC. • 2393 Salt Creek Highway (82601) • PO Box 3258 • Casper, WY 82602 lugr{ft7 Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABORA10I?I£5
ANALYTICAL SUMMARY REPORT
March 15,2010
Denison Mines USA Corp
6425 S Hwy 191
Blanding, UT 84511
Workorder No.: C10030236
Project Name: 1 st Quarter Choloform
Quote 10: C2975 -Chloroform Sampling
Energy Laboratories, Inc. received the following 17 samples for Denison Mines USA Corp on 3/5/2010 for analysis.
Sample 10 Client Sample 10 Collect Date Receive Date Matrix Test
C10030236-001 TW4-10R 03/02/10 08:20 03/05/10 Aqueous Chloride
Nitrogen, Nitrate + Nitrite
SW8260B VQCs, Standard List
C 10030236-002 TW4-22R 03/02/10 09:32 03/05/10 Aqueous Same As Above
C 10030236-003 TW4-11 R 03/02110 10:35 03/05/10 Aqueous Same As Above
C 10030236-004 TW4-7R 03/02/10 11: 17 03/05/10 Aqueous Same As Above
C 10030236-005 TW4-1 R 03/02/10 13:28 03/05/10 Aqueous Same As Above
C 10030236-006 TW4-2R 03/02/10 14:15 03/05/10 Aqueous Same As Above
C10030236-007 TW4-60 03/02/10 08:25 03/05/10 Aqueous Same As Above
C 10030236-008 TW4-70 03/03/10 09:37 03/05/10 Aqueous Same As Above
C 10030236-009 TW4-14 03/03/10 10:42 03/05/10 Aqueous Same As Above
C10030236-010 TW4-10 03/03/1009:37 03/05/10 Aqueous Same As Above
C 10030236-011 TW4-22 03/03/10 09:24 03/05/10 Aqueous Same As Above
C 10030236-012 TW4-11 03/03/10 09:49 03/05/10 Aqueous Same As Above
C 10030236-013 TW4-7 03/03/10 10:06 03/05/10 Aqueous Same As Above
C10030236-014 TW4-1 03/03/10 10: 17 03/05/10 Aqueous Same As Above
C10030236-015 TW4-2 03/03/10 09:58 03/05/10 Aqueous Same As Above
C10030236-016 Trip Blank 03/03/10 00:00 03/05/10 Aqueous SW8260B VQCs, Standard List
C 10030236-017 Temp Blank 03/03/10 00:00 03/05/10 Aqueous Temperature
Any exceptions or problems with the analyses are noted in the Laboratory Analytical Report, the QA/QC Summary
Report, or the Case Narrative.
The results as reported relate only to the item(s) submitted for testing.
If you have any questions regarding these test results, please call.
Report Approved By: 8ttfhU,Q D. UJ~ Step anie D. Waldrop
Reporting Supervisor
ENERGY LABORATORIES, INC •• 2393 Salt Creek Highway (82601)' PO. Box 3258 • Casper, WY 82602 'gg!ll{f)Y Toll Free 888.235.0515 • 307.235.0515 • Fax [phone] • casper@energy/ab.com· www.energy/ab.com
f ABORA TomES
QA/QC Summary Report
Client: Denison Mines USA Corp
Project: 1 st Quarter Choloform
Analyte Count Result Units
Method: A4500-CI B
Sample 10: MBLK9-100312A
Chloride
Sample 10: C10030165-001AMS
Chloride
Sample 10: C10030165-001AMSO
Chloride
Sample 10: C10030236-008AMS
Chloride
Sample 10: C10030236-008AMSO
Chloride
Sample 10: LCS35-100312A
Chloride
Qualifiers:
RL -Analyte reporting limit.
Method Blank
NO mg/L
Sample Matrix Spike
73.0 mg/L
Sample Matrix Spike Duplicate
73.0 mg/L
Sample Matrix Spike
126 mg/L
Sample Matrix Spike Duplicate
125 mg/L
Laboratory Control Sample
3650 mg/L
Report Date: 03/15/10
Work Order: C10030236
RL %REC Low Limit High Limit RPO RPOLimit Qual
Batch: 100312A-CL-TTR-W
Run: TITRA TION_100312B 03/12/10 11 :00
0.4
Run: TITRATION_100312B
1.0 103 90 110
Run: TITRATION_100312B
1.0 103 90 110
Run: TITRATION_100312B
1.0 99 90 110
Run: TITRATION_100312B
1.0 98 90 110
Run: TITRATION_100312B
1.0 103 90 110
ND -Not detected at the reporting limit.
o
0.6
03/12/10 11 :45
03/12/10 11 :46
10
03/12/1015:07
0311211015:09
10
03/12/10 15:13
ENERGY LABORATORIE~ INC •• 2393 Salt Creek Highway (82601) • P.o. Box 3258 • Casper, WY 82602 1999f{!2Y 70// Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail]· www.energylab.com
LABOI?A TomES
QA/QC Summary Report
Client: Denison Mines USA Corp Report Date: 03/15/10
Project: 1 st Quarter Choloform Work Order: C10030236
Analyte Count Result Units RL %REC Low Limit High Limit RPO RPOLimit Qual
Method: E3S3.2 Batch: R130499
Sample 10: MBLK-1 Method Blank Run: TECHNICON_1 0031 OA 03110/1013:04
Nitrogen, Nitrate+Nitrite as N NO mg/L 0.03
Sample 10: LCS-2 Laboratory Control Sample Run: TECHNICON_1 0031 OA 03/10/10 13:07
Nitrogen, Nitrate+Nitrite as N 2.50 mg/L 0.10 100 90 110
Sample 10: C10030236-00SBMS Sample Matrix Spike Run: TECHNICON_100310A 03/10/1015:17
Nitrogen, Nitrate+Nitrite as N 2.19 mg/L 0.10 109 90 110
Sample 10: C10030236-00SBMSO Sample Matrix Spike Duplicate Run: TECHNICON_1 0031 OA 03/10/10 15:19
Nitrogen, Nitrate+Nitrite as N 2.18 mg/L 0.10 109 90 110 0.5 10
Qualifiers:
RL -Analyte reporting limit. NO -Not detected at the reporting limit.
ENERGY LABORATORIES, INC. • /393 Salt Creek Highway (82601) • p.D. Box 3258 • Casper, WY 82602 lum{r,y 70/1 Free 888.235.0515 • 307.235.0515 • Fax [phone] • [e-mail] • www.energylab.com
[AflORA TORIES
QA/QC Summary Report
Client: Denison Mines USA Corp Report Date: 03/08/10
Project: 1 st Quarter Choloform Work Order: C10030236
r"
I Analyte Result Units RL %REC Low Limit High Limit RPO RPOLimit Qual
Method: SW8260B Batch: R130373
Sample 10: 030510_LCS_3 Laboratory Control Sample Run: SATURNCA_100305A 03/05/10 11 :48
Carbon tetrachloride 8.1 ug/L 1.0 81 70 130
Chloroform 7.9 ug/L 1.0 79 70 130
Chloromethane 7.3 ug/L 1.0 73 70 130
Methylene chloride 9.0 ug/L 1.0 90 70 130
Surr: 1.2-Dichlorobenzene-d4 1.0 94 80 120
Surr: Dibromofluoromethane 1.0 83 70 130
Surr: p-Bromofluorobenzene 1.0 98 80 130
Surr: Toluene-d8 1.0 103 80 120
Sample 10: 030510_MBLK_6 Method Blank Run: SATURNCA_100305A 03/05/1014:44
Carbon tetrachloride NO ug/L 1.0
Chloroform NO ug/L 1.0
Chloromethane NO ug/L 1.0
Methylene chloride NO ug/L 1.0
Surr: 1.2-Dichlorobenzene-d4 1.0 95 80 120
Surr: Dibromofluoromethane 1.0 82 70 130
Surr: p-Bromofluorobenzene 1.0 89 80 120
Surr: Toluene-d8 1.0 102 80 120
Sample 10: C10030236-015CMS Sample Matrix Spike Run: SATURNCA_100305A 03/05/10 21 :47
Carbon tetrachloride 990 ug/L 100 99 70 130
Chloroform 3500 ug/L 100 83 70 130
Chloromethane 980 ug/L 100 98 70 130
Methylene chloride 1100 ug/L 100 105 70 130
Surr: 1.2-Dichlorobenzene-d4 100 97 80 120
Surr: Dibromofluoromethane 100 86 70 130
Surr: p-Bromofluorobenzene 100 95 80 120
Surr: Toluene-d8 100 100 80 120
Sample 10: C10030236-015CMSO Sample Matrix Spike Duplicate Run: SATURNCA_100305A 03/05/10 22:26
Carbon tetrachloride 1000 ug/L 100 103 70 130 4 20
Chloroform 3700 ug/L 100 111 70 130 7.8 20
Chloromethane 1000 ug/L 100 101 70 130 3.2 20
Methylene chloride 1100 ug/L 100 109 70 130 3.4 20
Surr: 1.2-Dichlorobenzene-d4 100 93 80 120 0 10
Surr: Dibromofluoromethane 100 95 70 130 0 10
Surr: p-Bromofluorobenzene 100 86 80 120 0 10
Surr: Toluene-d8 100 99 80 120 0 10
Qualifiers:
RL -Analyte reporting limit. NO -Not detected at the reporting limit.
'.glf({etY Chain of Custody and Analytical Request Record page_I_Of2 ... ';l.»z,z.»naw PLEASE PRINT (Provide as much information as possible.)
Company Name: Project N?):WS, Permit, Etc. Sample Origin EPA/State Compliance: ~DeAlj~t1JJ /Il,'AlGS / 5J AL~f'dtjr£)Ft:tl.~ State: LAI Yes~ No D
Report Mailtd6ess: 3 oJ>(. &;"0'1 Contact Name: Phone/Fax: Email: Sampler: (Please Print)
l2t~ ~/~a 61g' ZZ,Z/ r:--I-k . ~/awl,~ 1A1' K'-fS)1 /().I1i1~( //,;.I~
Invoice Address: I Invoice Contact & Phone: Purchase Order: Quote/Bottle Orderl
( )'/l lIv\.-c. S~~.;
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~oen.r:: for charges and Cooler 10(s):
~co~51 CD 0 ~ R scheduling -See (0trl./-._> 0 >.05 W C. Instruction Page Dow D EOO/EOT(Electronic Data) ~enenms: C en en I 0s:= ~ C) "0 Receipt Temp D POTWIWWTP ~ U e: Comments: Format: ~«~I.Q~ :::::J U « 0 d °c D State: D LEVEL IV o r.... COl c: L-.. 0) c: .-I-m
L-~05.Q 0 . '"' ~, l-e: ~N D Other: D NELAC ~0=I05 I
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SAMPLE IDENTIFICATION Collection Collection MATRIX ~) Signature
(Name, Location, Interval, etc.) Date Time Match
1 X '1vJ4-IO ~ 3--2.-fo ()f)20 S-I/J I~ J
2 TIJ'lY-22~ i3<l'ID I(jQ3J. 5-vJ X 1s::;!J ~~\OO'~Yl?>~
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Date/Time: ,Z),1 Received by (print): DatelTime: Signature:
_'5. 't.//) J ~l)tJ Record Relinquislled by (print): -DatelTime: FalrlrF Received by (print): DatelTime: Signature:
MUST be "-
Signed
, K1\Frtoto]\tr('v1~7S£/ J 9}/':f ::iignature:
Sample Disposal: Return to Client: Lab Disposal:
In certain circumstances, samples submitted to Energy Laboratories, Inc. may be subcontracted to other certified laboratories in order to complete the analysis requested.
This serves as notice of this possibility. All sub-contract data will be clearly notated on your analytical report.
Visit our web site at www.energylab.com for additional information, downloadable fee schedule, forms, and links.
Igg.r{"Y
R'#l·ua'I.Ud4.
Chain of Custody and Analytical Request Record
PLEASE PRINT (Provide as much information as possible.)
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EPA/State Compliance:
Yes J'1 No D
Email: Report Mab~rtJ~e~~ 801 r t2ktllll'.Au tAr /(4S'11
cT2:inepJ rncl2-Phon~F;T;r 222, Sampler: (Please Print)
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Purchase Order: Quote/BottreOrder!
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RUSH sample submittal
for charges and
scheduling -See
Instruction Page
5.7t;f£v
Cooler'1'O(5):-I
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Format: ____ _ o~==ca C> u«~I_Q~ D POTWMlWTP D State: D LEVEL IV c .. Qj~I.§ ~
.... Q)-ro 00 "( ~~I16 I D Other: ----D NELAC E ......... :>-~
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SAMPLE IDENTIFICATION
(Name, Location, Interval, etc.)
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. ~----------------------------------------~~------------------~~~~~~~~~~~--~~~~-------~~-/------~~Ig~na~u~r~e:--------------..
Igned Sample Disposal: Return to Client: Lab Disposal: I ; . r
" In certain circumstances, samples submitted to Energy Laboratories, Inc. may be subcontracted to other certified laboratories in order to complete the analysis requested.
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Denison Mines USA Corp
Login completed by: Halley Ackerman
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1 I111111111111111111111I
C10030236
Date Received: 3/5/2010
Received by: ha .
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No D
No D
No D
No D
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No D
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Method 900.0 for gross alpha and gross beta is intended as a drinking water method for low TDS waters. Data provided by
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Tab I
Quality Assurance and Data Validation Tables

Table I-1: Field Data QA/QC Evaluation
Location
2x Casing
Volume
Volume
Pumped
Volume
Check RPD RPD RPD RPD RPD
MW-4 -- -- -- -- -- -- -- --
TW4-1 63 63 OK 2235 2245 -0.45 6.13 6.15 -0.33 14.61 14.6 0.07 471 470 0.21 21.6 28.2 -26.51
TW4-2 69 63 Insufficient 2772 3124 -11.94 6.56 6.55 0.15 14.6 14.61 -0.07 485 485 0.00 59.7 54.9 8.38
TW4-3 67 70 OK 1805 1.8 199.60 6.54 6.6 -0.91 13.97 13.8 1.22 514 511 0.59 1277 1316 -3.01
TW4-4 -- -- -- -- -- -- -- --
TW4-5 87 90 OK 1737 1734 0.17 6.49 6.48 0.15 14.85 14.86 -0.07 493 493 0.00 50 73.4 -37.93
TW4-6 35 35 OK 3578 3572 0.17 6.77 6.79 -0.29 14.28 14.33 -0.35 495 496 -0.20 40.1 50.7 -23.35
TW4-7 70 70 OK 1668 1580 5.42 6.69 6.78 -1.34 14.57 14.87 -2.04 509 508 0.20 86.1 48.5 55.87
TW4-8 78 78 OK 3319 3324 -0.15 6.69 6.7 -0.15 14.55 14.56 -0.07 432 424 1.87 51 57.7 -12.33
TW4-9 88 88 OK 2537 2508 1.15 6.39 6.37 0.31 500 498 0.40 500 498 0.40 197.2 875 -126.43
TW4-10 74 60 Insufficient 2676 2756 -2.95 6.37 6.44 -1.09 14.35 14.3 0.35 579 574 0.87 25.3 11.3 76.50
TW4-11 54 54 OK 1715 1700 0.88 6.64 6.64 0.00 14.06 14.08 -0.14 514 515 -0.19 3.3 5.3 -46.51
TW4-12 83 83 OK 727.7 795 -8.84 6.81 6.89 -1.17 14.41 14.42 -0.07 492 490 0.41 23.3 21.6 7.57
TW4-13 75 75 OK 1550 1580 -1.92 6.75 6.74 0.15 14.68 14.6 0.55 405 406 -0.25 28.6 21.4 28.80
TW4-14 5 5 OK 4582 4515 1.47 6.99 6.9 1.30 14.16 15.02 -5.89 475 473 0.42 258.6 2839 -166.61
TW4-15 -- -- -- -- -- -- -- --
TW4-16 101 90 Insufficient 3608 3666 -1.59 6.45 6.48 -0.46 14.42 14.64 -1.51 361 375 -3.80 75.3 29.6 87.13
TW4-17 73 72 OK 4025 4026 -0.02 6.14 6.13 0.16 14.05 14.06 -0.07 115 115 0.00 2.1 1.7 21.05
TW4-18 -- -- -- -- -- -- -- --
TW4-19 -- -- -- -- -- -- -- --
TW4-20 -- -- -- -- -- -- -- --
TW4-21 81 81 OK 3194 3218 -0.75 6.62 6.63 -0.15 15.68 15.7 -0.13 511 511 0.00 4.6 3.8 19.05
TW4-22 76 76 OK 5040 5036 0.08 6.52 6.53 -0.15 15.17 15.25 -0.53 540 540 0.00 111.3 70.4 45.02
TW4-23 74 74 OK 3738 3724 0.38 6.16 6.04 1.97 14.05 14.07 -0.14 378 376 0.53 95.7 68.9 32.56
TW4-24 86 86 OK 9092 9121 -0.32 6.31 6.31 0.00 14.77 14.78 -0.07 521 521 0.00 3.2 3.6 -11.76
TW4-25 128 128 OK 2978 2963 0.50 6.8 6.8 0.00 14.78 14.81 -0.20 501 500 0.20 58.1 16 113.63
MW-4, TW4-4, TW4-15, TW4-18, TW4-19, and TW4-20 are continually pumped wells, only one set of parameters was collected.
TW4-1 has only operated since January 31, 2010.
TWN4-18 only purged for 9 days in the first quarter from March 22 through March 31.
TW4-2, TW4-3, TW4-10, and TW4-16 were pumped dry and sampled after recovery.
TW4-3 ran dry from while parameters were being measured. It was sampled after it recovered.
TW4-16 was pumped to the static pump elevation and sampled.
Conductivity
(μMHOs) pH Temp (°C)
Redox Potential
(meV) Turbidity (NTU)
1935 6.73 14.31 399
0
2531 6.63 14.14 423
0
5.4
1462 6.43 11.02 476
0
3527 6.39 15.53 394
7.53357 6.22 15.54 399
21.9
2491 6.56 15.07 356
Table I-2: Holding Time Evaluation
Well VOCs Nitrate/Nitrite as Nitrogen Chloride
MW-4 XX X
TW4-1 XX X
TW4-1R XX X
TW4-2 XX X
TW4-2R XX X
TW4-3 XX X
TW4-3R XX X
TW4-4 XX X
TW4-5 XX X
TW4-5R XX X
TW4-6 XX X
TW4-6R XX X
TW4-7 XX X
TW4-7R XX X
TW4-8 XX X
TW4-8R XX X
TW4-9 XX X
TW4-9R XX X
TW4-10 XX X
TW4-10R XX X
TW4-11 XX X
TW4-11R XX X
TW4-12 XX X
TW4-12R XX X
TW4-13 XX X
TW4-13R XX X
TW4-14 XX X
TW4-14R XX X
TW4-15 XX X
TW4-16 XX X
TW4-16R XX X
TW4-17 XX X
TW4-18 XX X
TW4-19 XX X
TW4-20 XX X
TW4-21 XX X
TW4-21R XX X
TW4-22 XX X
TW4-22R XX X
TW4-23 XX X
TW4-23R XX X
TW4-24 XX X
TW4-24R XX X
TW4-25 XX X
TW4-25R XX X
TW4-60 (DI Blank)XX X
TW4-65 (Duplicate
of TW4-17) X X X
TW4-70 (Duplicate
of TW4-10) X X X
X = Holding times were verified against the method and QAP requirements and were found to be in compliance.
Table I-3 Laboratory Receipt Temperature Check
Sample Batch Wells in Batch Temperature
C10020658 MW-4, TW4-4, TW4-15, TW4-17, TW4-19, TW4-20,
and TW4-65
2 ˚C
C10020848
TW4-3, TW4-3R, TW4-5, TW4-5R, TW4-6, TW4-6R,
TW4-8, TW4-8R, TW4-9, TW4-9R, TW4-12, TW4-
12R, TW4-13, TW4-13R, TW4-16, TW4-16R, TW4-
18, TW4-21, TW4-21R, TW4-23, TW4-23R, TW4-24,
TW4-24R, TW4-25, and TW4-25R
2 ˚C
C10030236
TW4-1, TW4-1R, TW4-2, TW4-2R, TW4-7, TW4-7R,
TW4-10, TW4-10R, TW4-11, TW4-11R, TW4-14,
TW4-14R, TW4-22, TW4-22R, TW4-65, and TW4-70
2 ˚C
Table I-4: Analytical Method Check
Parameter Method Method Used by Lab
Carbon Tetrachloride SW8260B SW8260B
Chloride A4500-Cl B A4500-Cl B
Chloroform SW8260B SW8260B
Chloromethane SW8260B SW8260B
Methylene chloride SW8260B SW8260B
Nitrate and Nitrite as Nitrogen E353.2 E353.2
All parameters were analyzed using the reporting methods specified in the QAP
Table: I-5 Reporting Limit Exceedance Evaluation
Well Analyte
MW-4 Chloroform 100 ug/L 1.0 ug/L
MW-4 Nitrate and Nitrite as Nitrogen 0.2 mg/L 0.1 mg/L
TW4-1 Chloroform 100 ug/L 1.0 ug/L
TW4-1 Nitrate and Nitrite as Nitrogen 0.2 mg/L 0.1 mg/L
TW4-2 Chloroform 100 ug/L 1.0 ug/L
TW4-2 Nitrate and Nitrite as Nitrogen 0.2 mg/L 0.1 mg/L
TW4-4 Chloroform 100 ug/L 1.0 ug/L
TW4-4 Nitrate and Nitrite as Nitrogen 0.2 mg/L 0.1 mg/L
TW4-5 Nitrate and Nitrite as Nitrogen 0.2 mg/L 0.1 mg/L
TW4-6 Chloroform 100 ug/L 1.0 ug/L
TW4-7 Chloroform 100 ug/L 1.0 ug/L
TW4-7 Nitrate and Nitrite as Nitrogen 0.2 mg/L 0.1 mg/L
TW4-10 Chloroform 100 ug/L 1.0 ug/L
TW4-10 Nitrate and Nitrite as Nitrogen 0.2 mg/L 0.1 mg/L
TW4-11 Chloroform 100 ug/L 1.0 ug/L
TW4-11 Nitrate and Nitrite as Nitrogen 0.2 mg/L 0.1 mg/L
TW4-12 Nitrate and Nitrite as Nitrogen 0.2 mg/L 0.1 mg/L
TW4-13 Nitrate and Nitrite as Nitrogen 0.2 mg/L 0.1 mg/L
TW4-15 Chloroform 100 ug/L 1.0 ug/L
TW4-18 Chloroform 10 ug/L 1.0 ug/L
TW4-19 Chloroform 100 ug/L 1.0 ug/L
TW4-20 Chloroform 200 ug/L 1.0 ug/L
TW4-21 Chloroform 10 ug/L 1.0 ug/L
TW4-21 Nitrate and Nitrite as Nitrogen 0.2 mg/L 0.1 mg/L
TW4-22 Chloroform 100 ug/L 1.0 ug/L
TW4-25 Nitrate and Nitrite as Nitrogen 0.2 mg/L 0.1 mg/L
TW4-70
(Duplicate of
TW4-10)Chloroform 100 ug/L 1.0 ug/L
TW4-70
(Duplicate of
TW4-10)Nitrate and Nitrite as Nitrogen 0.2 mg/L 0.1 mg/L
These RLs are acceptable because they resulted from sample dilution due to high
concentration and/or matrix interference and in all cases where a reporting limit
was increased the analytical result was greater then the elevated reporting limit.
Reporting Limit
Used
Approved Reporting
Limit With Qualifier
Table I-6: Trip Blank Evaluation
Lab Report Constituent
Carbon tetrachloride ND
Chloroform ND
Chloromethane ND
Methylene chloride ND
Carbon tetrachloride ND
Chloroform ND
Chloromethane ND
Methylene chloride ND
Carbon tetrachloride ND
Chloroform ND
Chloromethane ND
Methylene chloride ND
#N/A
C10030236
C10020848
C10020658
Result
Table I-7: QA/QC Evaluation for Routine Sample Duplicates
Constituent TW4-10 TW4-70 %RPD
Carbon Tetrachloride 1 1 0.00
Chloride 49 55 11.54
Chloroform 460 480 4.26
Chloromethane 1 1 0.00
Methylene chloride 1 1 0.00
Constituent TW4-17 TW4-65 %RPD
Carbon Tetrachloride 1 1 0.00
Chloride 38 38 0.00
Chloroform 1 1 0.00
Chloromethane 1 1 0.00
Methylene chloride 1 1 0.00
#N/A
Table I-8: QC Control Limits for Analyses and Blanks
The percent recovery was within the limits for all method blanks, lab control samples, matrix spikes, and matrix spike
duplicates from Energy Labs reports C10020658, C10020848 and C10030236.
The RPD was below acceptable limits for each sample matrix spike duplicate from Energy Labs reports
C10020658, C10020848 and C10030236.
Table I-9: Rinsate Check
Rinsate Sample Parameter Qualifier
Previous Well
Sampled Qualifier
Reporting
Limit
TW4-1R Chloroform 7.8 ug/L TW4-1 1300 ug/L 1.0 ug/L
TW4-2R Chloroform 16 ug/L TW4-2 2600 ug/L 1.0 ug/L
TW4-3R Chloroform 1.2 ug/L TW4-3 1 ug/L U 1.0 ug/L
TW4-5R Chloride 2 mg/L TW4-5 43 mg/L 1 mg/L
TW4-5R Chloroform 3.4 ug/L TW4-5 13 ug/L 1.0 ug/L
TW4-6R Chloroform 12 ug/L TW4-6 1000 ug/L 1.0 ug/L
TW4-7R Chloroform 10 ug/L TW4-7 1200 ug/L 1.0 ug/L
TW4-8R Chloroform 1.7 ug/L TW4-8 1 ug/L U 1.0 ug/L
TW4-10R Chloroform 12 ug/L TW4-10 460 ug/L 1.0 ug/L
TW4-11R Chloroform 17 ug/L TW4-11 820 ug/L 1.0 ug/L
TW4-12R Chloroform 1.4 ug/L TW4-12 1 ug/L U 1.0 ug/L
TW4-13R Chloroform 3 ug/L TW4-13 1 ug/L U 1.0 ug/L
TW4-14R Chloroform 3.3 ug/L TW4-14 1 ug/L U 1.0 ug/L
TW4-16R Chloroform 3.2 ug/L TW4-16 780 ug/L 1.0 ug/L
TW4-21R Chloroform 2.5 ug/L TW4-21 170 ug/L 1.0 ug/L
TW4-22R Chloroform 13 ug/L TW4-22 2200 ug/L 1.0 ug/L
TW4-23R Chloroform 2.9 ug/L TW4-23 1 ug/L U 1.0 ug/L
TW4-24R Chloroform 2.9 ug/L TW4-24 1.3 ug/L 1.0 ug/L
TW4-25R Chloroform 1.2 ug/L TW4-25 1 ug/L U 1.0 ug/L
Rinsate Result Result

Tab J
Kriged Current Quarter Chloroform Isoconcentration Map

HYDRO
GEO
CHEM, INC.APPROVED DATE REFERENCE FIGURE
3332
3000
SCALE IN FEET
0
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS 1300
2600
ND
1700
13
1000
ND
460
820
ND
ND
ND
780
ND
ND
69940
3500
170
2200
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS NS
NS
NS
NS
NS
NS
NS
NS
MW-01
MW-02
MW-03
MW-05
MW-11
MW-12
MW-14
MW-15
MW-17
MW-18
MW-19
MW-20
MW-22
MW-23
MW-24
MW-25
MW-27
MW-28
MW-29
MW-30
MW-31

MW-32
TW4-19

PIEZ-1
PIEZ-2
PIEZ-3
PIEZ-4
PIEZ-5
TWN-1
TWN-2
TWN-3
TWN-4
TWN-5
TWN-6
TWN-7
TWN-8
TWN-9
TWN-10
TWN-11 TWN-12
TWN-13
TWN-14
TWN-15
TWN-16
TWN-17
TWN-18
TWN-19
1200
1600 NDMW-04
ND
1
ND
MW-26
TW4-20
MW-4
PIEZ-1
1600
NS
perched monitoring well showing
concentration in uG/l
temporary perched monitoring well installed
April, 2005 showing concentration in uG/l
perched piezometer (not sampled)
1300
MW-32
ND
temporary perched monitoring well
showing concentration in uG/l
170
perched monitoring well installed April, 2005
showing concentration in uG/l KRIGED 1st QUARTER, 2010 CHLOROFORM (uG/L)
WHITE MESA SITE
H:/718000/may10/chl0310.srf
EXPLANATION
NOTES: ND = not detected, NS = not sampled
temporary perched monitoring well installed
May, 2007 showing concentration in uG/lND SJS

Tab K
Analyte Concentrations Over Time

MW-4

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
28-Sep-99 6200
28-Sep-99 5820
28-Sep-99 6020
15-Mar-00 5520
15-Mar-00 5430
2-Sep-00 5420 9.63
30-Nov-00 6470 9.37
29-Mar-01 4360 8.77
22-Jun-01 6300 9.02
20-Sep-01 5300 9.45
8-Nov-01 5200 8
26-Mar-02 4700 8.19
22-May-02 4300 8.21
12-Sep-02 6000 8.45
24-Nov-02 2500 8.1
28-Mar-03 2000 8.3
30-Apr-03 3300 NA
30-May-03 3400 8.2
23-Jun-03 4300 8.2
30-Jul-03 3600 8.1
29-Aug-03 4100 8.4
12-Sep-03 3500 8.5
15-Oct-03 3800 8.1
8-Nov-03 3800 8.0
29-Mar-04 NA NA
22-Jun-04 NA NA
17-Sep-04 3300 6.71
17-Nov-04 4300 7.5
16-Mar-05 2900 6.3
25-May-05 3170 7.1
31-Aug-05 3500 7.0
1-Dec-05 3000 7.0
9-Mar-06 3100 6.0
14-Jun-06 3000 6.0
20-Jul-06 2820 1.2
9-Nov-06 2830 6.4
15-Aug-07 2600 6.2
10-Oct-07 2300 6.2
26-Mar-08 2400 5.8
25-Jun-08 2500 6.09
10-Sep-08 1800 6.36
15-Oct-08 2100 5.86
12-Sep-02 5700 8.3
24-Nov-02 5000 8.5
28-Mar-03 4500 8.2
23-Jun-03 4700 8.4
12-Sep-03 3400 8.6
10-Nov-03 4500 8.4
29-Mar-04 NA NA
22-Jun-04 NA NA
17-Sep-04 3300 6.83
MW-4

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
17-Nov-04 4100 8
16-Mar-05 3700 7.1
25-May-05 3740 7.8
31-Aug-05 3800 <10 <10 <10 6.9
1-Dec-05 3000 <50 <50 <50 7 NA
20-Jul-06 2820 <50 <50 <50 1.2 48
9-Nov-06 2830 2.1 1.4 <1 6.4 50
9-Mar-06 3100 <50 <50 50 6 49
14-Jun-06 3000 <50 <50 50 6 49
28-Feb-07 2300 1.6 <1 <1 6.3 47
27-Jun-07 2000 1.8 <1 <1 7 45
15-Aug-07 2600 1.9 <1 <1 6.2 47
10-Oct-07 2300 1.7 <1 <1 6.2 45
26-Mar-08 2400 1.7 <1 <1 5.8 42
25-Jun-08 2500 1.6 <1 <1 6.09 42
10-Sep-08 1800 1.8 <1 <1 6.36 35
15-Oct-08 2100 1.7 <1 <1 5.86 45
4-Mar-09 2200 1.5 <1 <1 5.7 37
23-Jun-09 1800 1.3 <1 <1 5.2 34
14-Sep-09 2000 1.4 <1 <1 5.3 43
14-Dec-09 1800 1.6 ND ND 5.8 44
17-Feb-10 1600 1.2 ND ND 4.0 45

TW4-1

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
28-Jun-99 1700 7.2
10-Nov-99 5.79
15-Mar-00 1100
10-Apr-00 1490
6-Jun-00 1530
2-Sep-00 2320 5.58
30-Nov-00 3440 7.79
29-Mar-01 2340 7.15
22-Jun-01 6000 8.81
20-Sep-01 NA 12.8
8-Nov-01 3200 12.4
26-Mar-02 3200 13.1
22-May-02 2800 12.7
12-Sep-02 3300 12.8
24-Nov-02 3500 13.6
28-Mar-03 3000 12.4
23-Jun-03 3600 12.5
12-Sep-03 2700 12.5
8-Nov-03 3400 11.8
29-Mar-04 3200 11
22-Jun-04 3100 8.78
17-Sep-04 2800 10.8
17-Nov-04 3000 11.1
16-Mar-05 2700 9.1
25-May-05 3080 10.6
31-Aug-05 2900 <10 <10 <10 9.8
1-Dec-05 2400 <50 <50 <50 9.6
20-Jul-06 2840 <50 <50 <50 9.7 51
8-Nov-06 2260 1.4 <1 <1 9.4 47
9-Mar-06 2700 <50 <50 <50 9.2 49
14-Jun-06 2200 <50 <50 <50 9.2 48
28-Feb-07 1900 1.2 <1 <1 8.9 47
27-Jun-07 1900 1.4 <1 <1 9 45
15-Aug-07 2300 1.3 <1 <1 8.4 43
10-Oct-07 2000 1.3 <1 <1 7.8 43
26-Mar-08 2000 1.3 <1 <1 7.6 39
25-Jun-08 1900 1.1 <1 <1 8.68 39
10-Sep-08 1700 1.3 <1 <1 8.15 35
15-Oct-08 1700 1.3 <1 <1 9.3 41
11-Mar-09 1700 1.1 <1 <1 7.5 37
24-Jun-09 1500 1 <1 <1 6.9 37
15-Sep-09 1700 <1 <1 <1 7.3 36
29-Dec-09 1400 ND ND ND 6.8 41
03-Mar-10 1300 ND ND ND 7.1 35

TW4-2

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
10-Nov-99 2510
2-Sep-00 5220
28-Nov-00 4220 10.7
29-Mar-01 3890 10.2
22-Jun-01 5500 9.67
20-Sep-01 4900 11.4
8-Nov-01 5300 10.1
26-Mar-02 5100 9.98
23-May-02 4700 9.78
12-Sep-02 6000 9.44
24-Nov-02 5400 10.4
28-Mar-03 4700 9.5
23-Jun-03 5100 9.6
12-Sep-03 3200 8.6
8-Nov-03 4700 9.7
29-Mar-04 4200 9.14
22-Jun-04 4300 8.22
17-Sep-04 4100 8.4
17-Nov-04 4500 8.6
16-Mar-05 3700 7.7
25-May-05 3750 8.6
31-Aug-05 3900 <10 <10 <10 8.0
1-Dec-/05 3500 <50 <50 <50 7.8
9-Mar-06 3800 <50 <50 <50 7.5 56
14-Jun-06 3200 <50 <50 <50 7.1 56
20-Jul-06 4120 <50 <50 <50 7.4 54
8-Nov-06 3420 2.3 <1 <1 7.6 55
28-Feb-07 2900 1.8 <1 <1 7.3 54
27-Jun-07 3000 2.5 <1 <1 7.8 50
15-Aug-07 340 2.2 <1 <1 7.3 49
10-Oct-07 3200 2.1 <1 <1 6.9 51
26-Mar-08 3300 2.3 <1 <1 6.9 48
25-Jun-08 3100 2.2 <1 <1 7.44 46
10-Sep-08 2800 2.4 <1 <1 7.1 42
15-Oct-08 3200 2.4 <2 <2 7.99 47
11-Mar-09 3100 2.2 <1 <1 6.5 46
24-Jun-09 2800 2 <1 <1 6.4 44
15-Sep-09 3000 2 <1 <1 6.6 43
29-Dec-09 1600 2.0 ND ND 6.4 46
03-Mar-10 2600 2.0 ND ND 6.8 42

TW4-3

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
28-Jun-99 3500 7.6
29-Nov-99 702
15-Mar-00 834
2-Sep-00 836 1.56
29-Nov-00 836 1.97
27-Mar-01 347 1.85
21-Jun-01 390 2.61
20-Sep-01 300 3.06
7-Nov-01 170 3.6
26-Mar-02 11 3.87
21-May-02 204 4.34
12-Sep-02 203 4.32
24-Nov-02 102 4.9
28-Mar-03 ND 4.6
23-Jun-03 ND 4.8
12-Sep-03 ND 4.3
8-Nov-03 ND 4.8
29-Mar-04 ND 4.48
22-Jun-04 ND 3.68
17-Sep-04 ND 3.88
17-Nov-04 ND 4.1
16-Mar-05 ND 3.5
25-May-05 ND 3.7
31-Aug-05 ND <1 <1 <1 3.5
1-Dec-05 ND <1 2.3 <1 3.3
9-Mar-06 ND <1 2.2 <1 3.3 26
14-Jun-06 ND <1 <1 <1 3.2 26
20-Jul-06 ND <1 1.6 <1 2.9 26
8-Nov-06 ND <1 <1 <1 1.5 23
28-Feb-07 ND <1 <1 <1 3.1 22
27-Jun-07 ND <1 <1 <1 3.3 23
15-Aug-07 ND <1 <1 <1 3.1 24
10/10/2007 ND <1 <1 <1 2.8 27
26-Mar-08 ND <1 <1 <1 2.8 21
25-Jun-08 ND <1 <1 <1 2.85 19
10-Sep-08 ND <1 <1 <1 2.66 19
15-Oct-08 ND <1 <1 <1 2.63 22
4-Mar-09 ND <1 <1 <1 2.5 21
24-Jun-09 ND <1 <1 <1 2.9 20
15-Sep-09 ND <1 <1 <1 2.8 21
16-Dec-09 ND ND ND ND 2.5 22
23-Feb-10 ND ND ND ND 2.8 23

TW4-4

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
6-Jun-00 ND
2-Sep-00 ND
28-Nov-00 3.85
28-Mar-01 2260 1.02
20-Jun-01 3100 14.5
20-Sep-01 3200 14
8-Nov-01 2900 14.8
26-Mar-02 3400 15
22-May-02 3200 13.2
12-Sep-02 4000 13.4
24-Nov-02 3800 12.6
28-Mar-03 3300 13.4
23-Jun-03 3600 12.8
12-Sep-03 2900 12.3
8-Nov-03 3500 12.3
29-Mar-04 3200 12.2
22-Jun-04 3500 12.1
17-Sep-04 3100 11.1
17-Nov-04 3600 10.8
16-Mar-05 3100 11.6
25-May-05 2400 10
31-Aug-05 3200 <10 <10 <10 11.3
1-Dec-05 2800 50 50 50 10.2
9-Mar-06 2900 50 50 50 9.5 51
14-Jun-06 2600 50 50 50 8.6 48
20-Jul-06 2850 50 50 50 9.7 50
8-Nov-06 2670 1.7 <1 <1 10.1 49
28-Feb-07 2200 1.5 <1 <1 9 49
27-Jun-07 2400 1.7 <1 <1 9.4 47
15-Aug-07 2700 1.5 <1 <1 9.5 45
10-Oct-07 2500 1.5 <1 <1 9.5 47
26-Mar-08 2800 1.6 <1 <1 9.2 43
25-Jun-08 2500 1.5 <1 <1 10.8 42
10-Sep-08 2200 1.4 <1 <1 8.83 39
15-Oct-08 2500 2 <2 <2 10.1 44
4-Mar-09 2200 1.2 <1 <1 10.2 37
24-Jun-09 1800 1.2 <1 <1 8.2 34
15-Sep-09 2000 1.1 <1 <1 8.4 39
29-Dec-09 950 1.1 ND ND 7.6 41
17-Feb-10 1700 1.0 ND ND 6.6 48

TW4-5

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
20-Dec-99 29.5
15-Mar-00 49
2-Sep-00 124
29-Nov-00 255
28-Mar-01 236
20-Jun-01 240
20-Sep-01 240
7-Nov-01 260
26-Mar-02 260
22-May-02 300
12-Sep-02 330
24-Nov-02 260
28-Mar-03 240
23-Jun-03 290
12-Sep-03 200
8-Nov-03 240
29-Mar-04 210
22-Jun-04 200
17-Sep-04 150
17-Nov-04 180
16-Mar-05 120
25-May-05 113
31-Aug-05 82 <2.5 5.8 <2.5 6
1-Dec-05 63 <2.5 <2.5 <2.5 6
9-Mar-06 66 <2.5 3.1 <2.5 6 52
14-Jun-06 51 <1 <2.5 <2.5 5.9 51
20-Jul-06 53.7 <1 <1 <1 6.7 54
8-Nov-06 47.1 <1 <1 <1 2.9 55
28-Feb-07 33 <1 <1 <1 7.8 57
27-Jun-07 26 <1 <1 <1 7 45
15-Aug-07 9.2 <1 <1 <1 7.7 38
10-Oct-07 9.4 <1 <1 <1 8.2 39
26-Mar-08 11 <1 <1 <1 7.4 36
25-Jun-08 9.3 <1 <1 <1 8.7 37
10-Sep-08 11 <1 <1 <1 7.91 34
15-Oct-08 10 <1 <1 <1 9.3 37
4-Mar-09 12 <1 <1 <1 7.9 34
24-Jun-09 13 <1 <1 <1 7.5 37
15-Sep-09 12 <1 >1 <1 8.3 48
22-Dec-09 8.5 ND ND ND 7.5 41
25-Feb-10 13 ND ND ND 6.8 43

TW4-6

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
6-Jun-00 ND
2-Sep-00 ND
28-Nov-00 ND ND
26-Mar-01 ND .13
20-Jun-01 ND ND
20-Sep-01 3.6 ND
7-Nov-01 1.00 ND
26-Mar-02 ND ND
21-May-02 ND ND
12-Sep-02 ND ND
24-Nov-02 ND ND
28-Mar-03 ND 0.1
23-Jun-03 ND ND
12-Sep-03 ND ND
8-Nov-03 ND ND
29-Mar-04 ND ND
22-Jun-04 ND ND
17-Sep-04 ND ND
17-Nov-04 ND ND
16-Mar-05 ND 0.2
25-May-05 ND 0.4
31-Aug-05 10.0 <10 2.8 <10 0.8
1-Dec-05 17 <1 1.3 <1 0.9
9-Mar-06 31 <1 <1 <1 1.2 31
14-Jun-06 19 <1 <1 <1 1.0 30
20-Jul-06 11 <1 <1 <1 0.6 37
8-Nov-06 42.8 <1 <1 <1 1.4 65
28-Feb-07 46 <1 <1 <1 1.5 32
27-Jun-07 11 <1 <1 <1 0.6 38
15-Aug-07 18 <1 <1 <1 0.7 36
10-Oct-07 18 <1 <1 <1 0.8 38
26-3-08 52 <1 <1 <1 1.1 33
25-Jun-08 24 <1 <1 <1 0.9 35
10-Sep-08 39 <1 <1 <1 1.14 35
15-Oct-08 37 <1 <1 <1 1.01 33
11-Mar-09 81 <1 <1 <1 2.2 35
24-Jun-09 120 <1 <1 <1 2.7 37
15-Sep-09 280 <1 <1 <1 37
22-Dec-09 250 ND ND ND 6.1 41
25-Feb-10 1000 ND ND ND 1.6 45

TW4-7

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
29-Nov-99 256
15-Mar-00 616
2-Sep-00 698
29-Nov-00 684 1.99
28-Mar-01 747 2.46
20-Jun-01 1100 2.65
20-Sep-01 1200 3.38
8-Nov-01 1100 2.5
26-Mar-02 1500 3.76
23-May-02 1600 3.89
12-Sep-02 1500 3.18
24-Nov-02 2300 4.6
28-Mar-03 1800 4.8
23-Jun-03 5200 7.6
12-Sep-03 3600 7.6
8-Nov-03 4500 7.1
29-Mar-04 2500 4.63
22-Jun-04 2900 4.83
17-Sep-04 3100 5.59
17-Nov-04 3800 6
16-Mar-05 3100 5.2
25-May-05 2700 5.4
31-Aug-05 3100 <10 <10 <10 5.2
1-Dec-05 2500 <50 <50 <50 5.3
9-Mar-06 1900 <50 <50 <50 1.0 48
14-Jun-06 2200 <50 <50 <50 4.5 47
20-Jul-06 2140 <50 <50 <50 4.7 51
8-Nov-06 2160 1.5 <1 1 4.6 49
28-Feb-07 1800 1.1 <1 1 5 47
27-Jun-07 2600 1.5 <1 1 5.1 45
14-Aug-07 2300 1.4 <1 1 4.7 44
10-Oct-07 1900 1.2 <1 1 4.7 45
26-Mar-08 2200 1.3 <1 1 4.2 43
25-Jun-08 1800 1.3 <1 1 4.8 43
10-Sep-08 1600 1.4 <1 1 4.16 35
15-Oct-08 1900 <2 <2 2 4.01 40
11-Mar-09 1800 1.2 <1 1 3.7 35
24-Jun-09 1400 <1 <1 1 3.8 37
15-Sep-09 1500 <1 <1 1 4.1 37
29-Dec-09 1300 ND ND ND 4.2 37
03-Mar-10 1200 ND ND ND 3.8 36

TW4-8

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
29-Nov-99 ND
15-Mar-00 21.8
2-Sep-00 102
29-Nov-00 107 ND
26-Mar-01 116 ND
20-Jun-01 180 ND
20-Sep-01 180 0.35
7-Nov-01 180 ND
26-Mar-02 190 0.62
22-May-02 210 0.77
12-Sep-02 300 ND
24-Nov-02 450 ND
28-Mar-03 320 0.8
23-Jun-03 420 ND
12-Sep-03 66 ND
8-Nov-03 21.0 0.1
29-Mar-04 24 0.65
22-Jun-04 110 0.52
17-Sep-04 120 ND
17-Nov-04 120 ND
16-Mar-05 10.0 ND
25-May-05 ND 0.2
31-Aug-05 1.1 ND
1-Dec-05 ND <1 1.7 <1 ND
9-Mar-06 1.3 <1 <1 <1 0.3 39
14-Jun-06 ND <1 2.1 <1 ND 37
20-Jul-06 ND <1 1.8 <1 0.1 39
8-Nov-06 ND <1 1 <1 ND 40
28-Feb-07 2.50 <1 1 <1 0.7 39
27-Jun-07 2.5 <1 1 <1 0.2 42
15-Aug-07 1.5 <1 1 <1 ND 42
10-Oct-07 3.5 <1 1 <1 0.5 43
26-Mar-08 ND <1 1 <1 0.1 46
25-Jun-08 ND <1 1 <1 ND 45
10-Sep-08 ND <1 1 <1 ND 39
15-Oct-08 ND <1 1 <1 ND 44
4-Mar-09 ND <1 1 <1 ND 42
24-Jun-09 ND <1 1 <1 ND 44
15-Sep-09 ND <1 1 <1 ND 44
17-Dec-09 ND ND ND ND ND 51
24-Feb-10 ND ND ND ND ND 57

TW4-9

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
20-Dec-99 4.24
15-Mar-00 1.88
2-Sep-00 14.2
29-Nov-00 39.4 ND
27-Mar-01 43.6 ND
20-Jun-01 59 .15
20-Sep-01 19 0.40
7-Nov-01 49 0.1
26-Mar-02 41 0.5
22-May-02 38 0.65
12-Sep-02 49 0.2
24-Nov-02 51 0.6
28-Mar-03 34 0.6
23-Jun-03 33 0.8
12-Sep-03 32 1.1
8-Nov-03 46 1.1
29-Mar-04 48 0.82
22-Jun-04 48 0.75
17-Sep-04 39 0.81
17-Nov-04 26 1.2
16-Mar-05 3.8 1.3
25-May-05 1.2 1.3
31-Aug-05 ND <1 2.9 <1 1.3
1-Dec-05 ND <1 <1 <1 1.3
9-Mar-06 ND <1 2.6 <1 1.5 38
14-Jun-06 ND <1 2.7 <1 1.5 39
20-Jul-06 ND <1 <1 <1 0.9 41
8-Nov-06 ND <1 <1 <1 0.7 44
28-Feb-07 ND <1 <1 <1 0.6 44
27-Jun-07 21 <1 <1 <1 1.3 42
15-Aug-07 9.5 <1 <1 <1 1.8 38
10-Oct-07 8.7 <1 <1 <1 2 40
26-Mar-08 1.3 <1 <1 <1 2.1 35
25-Jun-08 1.0 <1 <1 <1 2.3 35
10-Sep-08 ND <1 <1 <1 2.79 28
15-Oct-08 ND <1 <1 <1 1.99 58
4-Mar-09 ND <1 <1 <1 2.5 30
24-Jun-09 ND <1 <1 <1 2.3 30
15-Sep-09 ND <1 <1 <1 2.5 30
17-Dec-09 ND ND ND ND 1.7 37
23-Feb-10 ND ND ND ND 1.7 47

TW4-10

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
21-Jan-02 14
26-Mar-02 16 0.14
21-May-02 17 0.11
12-Sep-02 6.0 ND
24-Nov-02 14 ND
28-Mar-03 29 0.2
23-Jun-03 110 0.4
12-Sep-03 74 0.4
8-Nov-03 75 0.3
29-Mar-04 22 0.1
22-Jun-04 32 ND
17-Sep-04 63 0.46
17-Nov-04 120 0.4
16-Mar-05 140 1.6
25-May-05 62.4 0.8
31-Aug-05 110 1.1
1-Dec-05 300 <2.5 <2.5 6.2 3.3
9-Mar-06 190 <5 <50 <50 2.4 50
14-Jun-06 300 <5 <50 <50 3.5 54
20-Jul-06 504.00 <5 <50 <50 6.8 61
8-Nov-06 452.00 <1 1.6 1 5.7 58
28-Feb-07 500 <1 <1 1 7.6 62
27-Jun-07 350 <1 <1 1 5.1 54
15-Aug-07 660 <1 <1 1 7.3 59
10-Oct-07 470 <1 <1 1 6.7 59
26-Mar-08 620 <1 <1 1 7.3 55
25-Jun-08 720 <1 <1 1 9.91 58
10-Sep-08 680 <1 <1 1 9.23 51
15-Oct-08 1200 <2 <2 2 10.5 61
11-Mar-09 1100 <1 <1 1 11.6 64
24-Jun-09 1200 <1 <1 1 9.8 62
15-Sep-09 910 <1 <1 1 8.1 51
22-Dec-09 300 ND ND ND 3.5 51
03-Mar-10 460 ND ND ND 5.0 49

TW4-11

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
21-Jan-02 4700
26-Mar-02 4900 9.60
22-May-02 5200 9.07
12-Sep-02 6200 8.84
24-Nov-02 5800 9.7
28-Mar-03 5100 9.7
23-Jun-03 5700 9.4
12-Sep-03 4600 9.9
8-Nov-03 5200 9.3
29-Mar-04 5300 9.07
22-Jun-04 5700 8.74
17-Sep-04 4800 8.75
17-Nov-04 5800 9.7
16-Mar-05 4400 8.7
25-May-05 3590 10.3
31-Aug-05 4400 <10 <10 <10 9.4
1-Dec-05 4400 <100 <100 <100 9.4
9-Mar-06 4400 <50 <50 <50 9.2 56
14-Jun-06 4300 <50 <50 <50 10 56
20-Jul-06 4080 <50 <50 <50 10 55
8-Nov-06 3660 1.7 2.7 1.3 10 55
28-Feb-07 3500 1.3 <1 1.6 10.1 54
27-Jun-07 3800 1.6 <1 1.1 10.6 53
15-Aug-07 4500 1.7 <1 1.1 10.2 53
10-Oct-07 4400 1.6 <1 1.2 9.8 53
26-Mar-08 340 <1 <1 <1 7.7 63
25-Jun-08 640 <1 <1 <1 7.28 46
10-Sep-08 900 <1 <1 <1 7.93 42
15-Oct-08 1000 <2 <2 <2 9.46 47
11-Mar-09 1100 <1 <1 <1 7.3 49
24-Jun--09 980 <1 <1 <1 6.8 44
15-Sep-09 1000 <1 <1 <1 7.0 49
29-Dec-09 860 ND ND ND 6.6 46
03-Mar-10 820 ND ND ND 6.8 42

TW4-12

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
12-Sep-02 1.5 2.54
24-Nov-02 ND 2.2
28-Mar-03 ND 1.9
23-Jun-03 ND 1.8
12-Sep-03 ND 1.8
9-Nov-03 ND 1.6
29-Mar-04 ND 1.58
22-Jun-04 ND 1.4
17-Sep-04 ND 1.24
17-Nov-04 ND 1.5
16-Mar-05 ND 1.4
25-May-05 ND 1.6
31-Aug-05 ND <1 5.8 <1 1.5
1-Dec-05 ND <1 <1 1.4
9-Mar-06 ND <1 <1 <1 1.3 19
14-Jun-06 ND <1 <1 <1 1.4 16
20-Jul-06 ND <1 <1 <1 1.4 16
8-Nov-06 ND <1 <1 <1 1.4 16
28-Feb-07 ND <1 <1 <1 1.5 16
27-Jun-07 ND <1 <1 <1 1,5 18
Aug-15-07 ND <1 <1 <1 1.4 29
10-Oct-07 ND <1 <1 <1 1.4 16
26-Mar-08 ND <1 <1 <1 1.6 16
25-Jun-08 ND <1 <1 <1 2.69 19
10-Sep-08 ND <1 <1 <1 2.65 18
15-Oct-08 ND <1 <1 <1 2.47 22
4-Mar-09 ND <1 <1 <1 2.4 23
24-Jun-09 ND <1 <1 <1 3.8 22
15-Sep-09 ND <1 <1 <1 5.1 22
16-Dec-09 ND ND ND ND 3.6 23
23-Feb-10 ND ND ND ND 4.0 22

TW4-13

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
12-Sep-02 ND ND
24-Nov-02 ND ND
28-Mar-03 ND 0.2
23-Jun-03 ND 0.2
12-Sep-03 ND ND
9-Nov-03 ND 0.9
29-Mar-04 ND 0.12
22-Jun-04 ND 0.17
17-Sep-04 ND 4.43
17-Nov-04 ND 4.7
16-Mar-05 ND 4.2
25-May-05 ND 4.3
31-Aug-05 ND <1 3.1 <1 4.6
1-Dec-05 ND <1 <1 <1 4.3
9-Mar-06 ND <1 1.7 <1 4.2 67
14-Jun-06 ND <1 1.4 <1 4.9 66
20-Jul-06 ND <1 <1 <1 4.3 65
8-Nov-06 ND <1 <1 <1 0.8 33
28-Feb-07 ND <1 <1 <1 4 59
27-Jun-07 ND <1 <1 <1 4.6 59
15-Aug-07 ND <1 <1 <1 4.4 58
10-Oct-07 ND <1 <1 <1 4.1 58
26-Mar-08 ND <1 <1 <1 3.8 54
25-Jun-08 ND <1 <1 <1 4.24 58
10-Sep-08 ND <1 <1 <1 4.26 50
15-Oct-08 ND <1 <1 <1 4.63 58
4-Mar-09 ND <1 <1 <1 3.7 58
24-Jun-09 ND <1 <1 <1 1.2 57
15-Sep-09 ND <1 <1 <1 4.7 63
16-Dec-09 ND ND ND ND 4.1 60
24-Feb-10 ND ND ND ND 4.3 53

TW4-14

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
8-Nov-06 ND ND ND ND 2.4 37
28-Feb-07 ND ND ND ND 2.3 38
27-Jun-07 ND ND ND ND 1.4 38
15-Aug-07 ND ND ND ND 1.1 36
10-Oct-07 ND ND ND ND 0.8 36
26-Mar-08 ND ND ND ND .04 57
25-Jun-08 ND ND ND ND 1.56 35
10-Sep-08 ND ND ND ND 1.34 34
15-Oct-08 ND ND ND ND 0.76 40
4-Mar-09 ND ND ND ND 1.6 35
24-Jun-09 ND ND ND ND 1.4 36
15-Sep-09 ND ND ND ND 1.5 38
16-Dec-09 ND ND ND ND 1.4 34
03-Mar-10 ND ND ND ND 2.5 33

TW4-15
(MW-26)

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
12-Sep-02 2.6 ND
24-Nov-02 ND ND
28-Mar-03 ND 0.1
23-Jun-03 7800 14.5
15-Aug-03 7400 16.8
12-Sep-03 2500 2.7
25-Sep-03 2600 2.5
29-Oct-03 3100 3.1
8-Nov-03 3000 2.8
29-Mar-04 NA NA
22-Jun-04 NA NA
17-Sep-04 1400 0.53
17-Nov-04 300 0.2
16-Mar-05 310 0.3
30-Mar-05 230 0.2
25-May-05 442 0.2
31-Aug-05 960 <5 5.4 <5 0.2
1-Dec-05 1000 <50 <50 0.3
9-Mar-06 1100 <50 <50 <50 0.2 52
14-Jun-06 830 <50 <50 <50 0.2 52
20-Jul-06 2170 <50 <50 <50 1.4 65
8-Nov-06 282 <1 <1 2.8 0.3 54
28-Feb-07 570 <1 <1 5.5 0.5 56
27-Jun-07 300 <1 <1 13 0.4 49
15-Aug-07 1400 <1 <1 36 1 57
10-Oct-07 2000 <1 <1 14 0.6 57
26-Mar-08 930 <1 <1 40 0.1 49
25-Jun-08 1300 <1 <1 53 0.56 57
10-Sep-08 630 <1 <1 24 0.24 44
15-Oct-08 1700 <1 <1 100 0.65 64
4-Mar-09 950 <1 <1 51 0.4 49
24-Jun-09 410 <1 <1 12 0.2 48
15-Sep-09 850 <1 <1 30 0.1 46
14-Dec-09 1100 ND ND 40 2.3 60
17-Feb-10 780 ND ND 19 0.2 57

TW4-16

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
12-Sep-02 140 ND
24-Nov-02 200 ND
28-Mar-03 260 ND
23-Jun-03 370 ND
12-Sep-03 350 ND
8-Nov-03 400 ND
29-Mar-04 430 ND
22-Jun-04 530 ND
17-Sep-04 400 ND
17-Nov-04 350 ND
16-Mar-05 240 ND
25-May-05 212 ND
31-Aug-05 85 <1 3.2 43 ND
1-Dec-05 14 <1 2.6 5.9 1.4
9-Mar-06 39 <1 1.1 21 3.0 60
14-Jun-06 13 <1 2.4 8.9 1.9 55
20-Jul-06 5 <1 <1 2.7 2.7 60
8-Nov-06 13.6 <1 <1 9.2 5.6 62
28-Feb-07 8.70 <1 <1 6.5 12.3 79
27-Jun-07 2.60 <1 <1 1.8 9.9 75
15-Aug-07 7.10 <1 <1 5.1 5.4 66
10-Oct-07 1.40 <1 <1 <1 4.4 69
26-Mar-08 11.00 <1 <1 26 ND 52
25-Jun-08 ND <1 <1 <1 1.46 58
10-Sep-08 10.00 <1 <1 14 10.5 71
15-Oct-08 3.9 <1 <1 6.6 9.82 89
4-Mar-09 ND <1 <1 <1 9.6 78
24-Jun-09 ND <1 <1 <1 8.9 76
15-Sep-09 ND <1 <1 <1 8.8 79
17-Dec-09 ND ND ND ND 5.2 76
24-Feb-10 ND ND ND ND 4.2 77

TW4-17
(MW-32)
Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
12-Sep-02 1.6 ND
24-Nov-02 ND ND
28-Mar-03 ND ND
23-Jun-03 ND ND
12-Sep-03 ND ND
8-Nov-03 ND ND
29-Mar-04 ND ND
22-Jun-04 ND ND
17-Sep-04 ND ND
17-Nov-04 ND ND
16-Mar-05 ND ND
30-Mar-05 ND ND
25-May-05 ND ND
31-Aug-05 ND <1 3.2 <1 ND
1-Dec-05 ND <1 1 ND 32
9-Mar-06 ND <1 1 ND 30
14-Jun-06 ND <1 3.5 ND 32
20-Jul-06 ND <1 1.8 ND 31
8-Nov-06 ND <1 1.5 ND 32
28-Feb-07 ND <1 <1 ND 32
27-Jun-07 ND <1 <1 ND 31
15-Aug-07 ND <1 <1 ND 32
10-Oct-07 ND <1 <1 ND 31
26-Mar-08 ND <1 <1 ND 29
25-Jun-08 ND <1 <1 ND 30
10-Sep-08 ND <1 <1 ND 26
15-Oct-08 ND <1 <1 ND 30
4-Mar-09 ND <1 <1 ND 31
24-Jun-09 ND ND ND ND ND 31
15-Sep-09 ND <1 <1 ND 33
16-Dec-09 ND ND ND ND ND 34
17-Feb-10 ND ND ND ND ND 38

TW4-18

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
12-Sep-02 440 1.49
24-Nov-02 240 13.3
28-Mar-03 160 13.1
23-Jun-03 110 19
12-Sep-03 68 19.9
9-Nov-03 84 20.7
29-Mar-04 90 14
22-Jun-04 82 12.2
17-Sep-04 38 14.5
17-Nov-04 51 17.3
16-Mar-05 38 14.1
25-May-05 29.8 12.9
31-Aug-05 39 13.3
1-Dec-05 14 <1 2.8 <1 7.3
9-Mar-06 12 <1 1.1 <1 5.9 5.9
14-Jun-06 12 <1 1.6 <1 4.7 35
20-Jul-06 10.80 <1 2.7 <1 6.1 35
8-Nov-06 139.00 <1 <1 <1 8.7 34
28-Feb-07 9.2 <1 <1 <1 5.1 30
27-Jun-07 8.0 <1 <1 <1 4.9 28
15-Aug-07 8.9 <1 <1 <1 5 32
10-Oct-07 7.4 <1 <1 <1 4.4 27
26-Mar-08 6.4 <1 <1 <1 0.7 23
25-Jun-08 5.7 <1 <1 <1 4.55 23
10-Sep-08 8.0 <1 <1 <1 4.68 26
15-Oct-08 9.4 <1 <1 <1 5,15 30
4-Mar-09 11.0 <1 <1 <1 5.2 29
24-Jun-09 16.0 <1 <1 <1 6.2 30
15-Sep-09 13.0 <1 <1 <1 5.9 26
22-Dec-09 8.2 ND ND ND 5.4 30
24-Feb-10 69 ND ND ND 5.1 41

TW4-19

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
12-Sep-02 7700 47.6
24-Nov-02 5400 42
28-Mar-03 4200 61.4
15-May-03 4700 NA
23-Jun-03 4500 11.4
15-Jul-03 2400 6.8
15-Aug-03 2600 4
12-Sep-03 2500 5.7
25-Sep-03 4600 9.2
29-Oct-03 4600 7.7
9-Nov-03 2600 4.8
29-Mar-04 NA NA
22-Jun-04 NA NA
16-Aug-04 7100 9.91
17-Sep-04 2600 4.5
17-Nov-04 1800 3.6
16-Mar-05 2200 5.3
25-May-05 1200 5.7
31-Aug-05 1400 <5 <5 <5 4.6
1-Dec-05 2800 50 <50 <50 ND
9-Mar-06 1200 50 <50 <50 4.0 86
14-Jun-06 1100 50 <50 <50 5.2 116
20-Jul-06 1120 50 <50 <50 4.3 123
8-Nov-06 1050 1.6 2.6 <1 4.6 134
28-Feb-07 1200 1.3 <1 <1 4 133
27-Jun-07 1800 2.3
15-Aug-07 1100 1.9 <1 <1 4.1 129
10-Oct-07 1100 1.9 <1 <1 4 132
26-Mar-08 1800 2.9 <1 <1 2.2 131
25-Jun-08 1000 1 <1 <1 2.81 128
10-Sep-08 3600 8.6 <1 <1 36.2 113
15-Oct-08 4200 12 <1 <1 47.8 124
4-Mar-09 1100 1.2 <1 <1 3.2 127
24-Jun-09 990 1.2 <1 <1 2.4 132
15-Sep-09 6600 15 <1 <1 0.1 43
14-Dec-09 4700 16 ND ND 26.7 124
17-Feb-10 940 1.3 ND ND 2.0 144

TW4-20

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
25-May-05 39000 NS ND ND 10.1 NS
31-Aug-05 3800 ND ND ND 2.9 NS
1-Dec-05 19000 ND ND ND 1.8 131
9-Mar-06 9200 ND ND ND 3.8 120
14-Jun-06 61000 ND ND ND 9.4 235
20-Jul-06 5300 ND ND ND 2.9 134
8-Nov-06 11000 7.1 1.9 2.2 3.5 124
28-Feb-07 4400 3.1 ND 1.1 4.2 124
27-Jun-07 1800 2.2 ND ND 2.3 112
15-Aug-07 5200 3.5 ND 1.8 2.1 117
10-Oct-07 9000 6.8 ND 1.9 5.6 170
26-Mar-08 13000 9.0 ND 1.5 0.9 132
25-Jun-08 30000 13 ND 1.2 7.96 191
10-Sep-08 21000 15 ND 3.7 4.44 156
15-Oct-08 NS NS NS NS 5.51 166
4-Mar-09 8200 5.7 ND 5.2 5.1 164
24-Jun-09 6800 4.9 ND 4.2 2.9 164
15-Sep-09 13000 8.4 ND 4.4 3.3 153
14-Dec-09 15000 14 ND 3.0 5.3 187
17-Feb-10 3500 2.7 ND 3.2 2.0 179

TW4-21

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
25-May-05 192 NS NS NS 14.6 NS
31-Aug-05 78 ND ND ND 10.1 NS
1-Dec-05 86 ND 1.0 ND 9.6 353
9-Mar-06 120 ND ND ND 8.5 347
14-Jun-06 130 ND ND ND 10.2 318
20-Jul-06 106 ND ND ND 8.9 357
8-Nov-06 12.5 2.0 ND ND 5.7 296
28-Feb-07 160 1.8 ND ND 8.7 306
27-Jun-07 300.0 5.8 ND ND 8.6 327
15-Aug-07 140 ND ND ND 8.6 300
10-Oct-07 120 ND ND ND 8.3 288
26-Mar-08 380 7.0 ND ND 14.3 331
25-Jun-08 160 1.7 ND ND 8.81 271
10-Sep-08 120 1.6 ND ND 7.57 244
15-Oct-08 170 2.0 ND ND 8.0 284
11-Mar-09 180 ND ND ND 8.3 279
24-Jun-09 200 ND ND ND 8.1 291
15-Sep-09 200 ND ND ND 9.2 281
29-Dec-09 380 ND ND ND 17.8 175
25-Feb-10 170 ND ND ND 8.4 228

TW4-22

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
25-May-05 340 NS NS NS 18.2 NS
31-Aug-05 290 ND ND ND 15.7 NS
1-Dec-05 320 ND ND ND 15.1 263
9-Mar-06 390 ND ND ND 15.3 236
14-Jun-06 280 ND ND ND 14.3 221
20-Jul-06 864 ND ND ND 14.5 221
08-Nov-06 350 ND 1.6 ND 15.9 236
28-Feb-07 440 ND ND ND 20.9 347
27-Jun-07 740 ND ND ND 19.3 273
15-Aug-07 530 ND ND ND 19.3 259
10-Oct-07 440 ND ND ND 18.8 238
26- Mar-08 1400 ND ND ND 39.1 519
25-Jun-08 1200 ND ND ND 41.9 271
10-Sep-08 6300 1.3 ND ND 38.7 524
15-Oct-08 630 ND ND ND 36.3 539
11-Mar-09 390 ND ND ND 20.7 177
24-Jun-09 730 ND ND ND 20.6 177
15-Sep-09 2300 ND ND ND 40.3 391
29-Dec-09 380 ND ND ND 17.8 175
03-Mar-10 380 ND ND ND 17.8 175

TW4-23

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
06/27/07 ND ND ND ND ND 47
15-Aug-07 ND ND ND ND ND 46
10-Oct-07 ND ND ND ND ND 43
26-Mar08 ND ND ND ND ND 41
25-Jun-08 ND ND ND ND ND 41
10-Sep-08 ND ND ND ND ND 35
15-Oct-08 ND ND ND ND ND 51
11-Mar-09 ND ND ND ND ND 41
24-Jun-09 ND ND ND ND ND 43
15-Sep-09 ND ND ND ND ND 43
16-Dec-09 ND ND ND ND ND 37
24-Feb-10 ND ND ND ND ND 45

TW4-24

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
27-Jun-07 0 ND ND ND 26.1 770
15-Aug -07 0 ND ND ND 29.0 791
10-Oct-07 1.5 ND ND ND 24.7 692
26-Mar-08 2.9 ND ND ND 24.4 740
25-Jun-08 1.4 ND ND ND 45.3 834
10-Sep-08 1.5 ND ND ND 38.4 1180
15-Oct-08 0 ND ND ND 44.6 1130
11-Mar-09 1.4 ND ND ND 30.5 1010
24-Jun-09 1.5 ND ND ND 30.4 759
15-Sep-09 2.2 ND ND ND 30.7 618
17-Dec-09 1.2 ND ND ND 28.3 1080
25-Feb-10 1.3 ND ND ND 33.1 896

TW4-25

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
27-Jun-07 ND ND ND ND 17.1 395
15-Aug-07 ND ND ND ND 16.7 382
10-Oct -07 ND ND ND ND 17.0 356
26-Mar-08 ND ND ND ND 18.7 374
25-Jun-08 ND ND ND ND 22.1 344
10-Sep-08 ND ND ND ND 18.8 333
15-Oct-08 ND ND ND ND 21.3 366
11-Mar-09 ND ND ND ND 15.3 332
24-Jun-09 ND ND ND ND 15.3 328
15-Sep-09 ND ND ND ND 3.3 328
16-Dec-09 ND ND ND ND 14.2 371
23-Feb-10 ND ND ND ND 14.4 296

Tab L
Chloroform Concentration Trend Graphs

3000
4000
5000
6000
7000
(u
g
/
L
)
MW4-Chloroform Values
0
1000
2000
Se
p
-
9
9
De
c
-
9
9
Ma
r
-
0
0
Ju
n
-
0
0
Se
p
-
0
0
De
c
-
0
0
Ma
r
-
0
1
Ju
n
-
0
1
Se
p
-
0
1
De
c
-
0
1
Ma
r
-
0
2
Ju
n
-
0
2
Se
p
-
0
2
De
c
-
0
2
Ma
r
-
0
3
Ju
n
-
0
3
Se
p
-
0
3
De
c
-
0
3
Ma
r
-
0
4
Ju
n
-
0
4
Se
p
-
0
4
De
c
-
0
4
Ma
r
-
0
5
Ju
n
-
0
5
Se
p
-
0
5
De
c
-
0
5
Ma
r
-
0
6
Ju
n
-
0
6
Se
p
-
0
6
De
c
-
0
6
Ma
r
-
0
7
Ju
n
-
0
7
Se
p
-
0
7
De
c
-
0
7
Ma
r
-
0
8
Ju
n
-
0
8
Se
p
-
0
8
De
c
-
0
8
Ma
r
-
0
9
Ju
n
-
0
9
Se
p
-
0
9
De
c
-
0
9
2000
3000
4000
5000
6000
7000
(u
g
/
L
)
TW4-1 Chloroform Values
0
1000
2000
Ju
n
-
9
9
Se
p
-
9
9
De
c
-
9
9
Ma
r
-
0
0
Ju
n
-
0
0
Se
p
-
0
0
De
c
-
0
0
Ma
r
-
0
1
Ju
n
-
0
1
Se
p
-
0
1
De
c
-
0
1
Ma
r
-
0
2
Ju
n
-
0
2
Se
p
-
0
2
De
c
-
0
2
Ma
r
-
0
3
Ju
n
-
0
3
Se
p
-
0
3
De
c
-
0
3
Ma
r
-
0
4
Ju
n
-
0
4
Se
p
-
0
4
De
c
-
0
4
Ma
r
-
0
5
Ju
n
-
0
5
Se
p
-
0
5
De
c
-
0
5
Ma
r
-
0
6
Ju
n
-
0
6
Se
p
-
0
6
De
c
-
0
6
Ma
r
-
0
7
Ju
n
-
0
7
Se
p
-
0
7
De
c
-
0
7
Ma
r
-
0
8
Ju
n
-
0
8
Se
p
-
0
8
De
c
-
0
8
Ma
r
-
0
9
Ju
n
-
0
9
Se
p
-
0
9
De
c
-
0
9
3000
4000
5000
6000
7000
(u
g
/
L
)
TW4-2 Chloroform Values
0
1000
2000
Se
p
-
9
9
De
c
-
9
9
Ma
r
-
0
0
Ju
n
-
0
0
Se
p
-
0
0
De
c
-
0
0
Ma
r
-
0
1
Ju
n
-
0
1
Se
p
-
0
1
De
c
-
0
1
Ma
r
-
0
2
Ju
n
-
0
2
Se
p
-
0
2
De
c
-
0
2
Ma
r
-
0
3
Ju
n
-
0
3
Se
p
-
0
3
De
c
-
0
3
Ma
r
-
0
4
Ju
n
-
0
4
Se
p
-
0
4
De
c
-
0
4
Ma
r
-
0
5
Ju
n
-
0
5
Se
p
-
0
5
De
c
-
0
5
Ma
r
-
0
6
Ju
n
-
0
6
Se
p
-
0
6
De
c
-
0
6
Ma
r
-
0
7
Ju
n
-
0
7
Se
p
-
0
7
De
c
-
0
7
Ma
r
-
0
8
Ju
n
-
0
8
Se
p
-
0
8
De
c
-
0
8
Ma
r
-
0
9
Ju
n
-
0
9
Se
p
-
0
9
De
c
-
0
9
Ma
r
-
1
0
0
1
1
1
1
1
1
(u
g
/
L
)
TW-4-3 Chloroform Values
TW4-3 Has been less than the detection limit since March 28, 2003
0
0
0
0
Se
p
-
0
6
Oc
t
-
0
6
No
v
-
0
6
De
c
-
0
6
Ja
n
-
0
7
Fe
b
-
0
7
Ma
r
-
0
7
Ap
r
-
0
7
Ma
y
-
0
7
Ju
n
-
0
7
Ju
l
-
0
7
Au
g
-
0
7
Se
p
-
0
7
Oc
t
-
0
7
No
v
-
0
7
De
c
-
0
7
Ja
n
-
0
8
Fe
b
-
0
8
Ma
r
-
0
8
Ap
r
-
0
8
Ma
y
-
0
8
Ju
n
-
0
8
Ju
l
-
0
8
Au
g
-
0
8
Se
p
-
0
8
Oc
t
-
0
8
No
v
-
0
8
De
c
-
0
8
Ja
n
-
0
9
Fe
b
-
0
9
Ma
r
-
0
9
Ap
r
-
0
9
Ma
y
-
0
9
Ju
n
-
0
9
Ju
l
-
0
9
Au
g
-
0
9
Se
p
-
0
9
Oc
t
-
0
9
No
v
-
0
9
De
c
-
0
9
Ja
n
-
1
0
Fe
b
-
1
0
Ma
r
-
1
0
1500
2000
2500
3000
3500
4000
4500
TW4-4 Chloroform Values
0
500
1000
Ju
n
-
0
0
Se
p
-
0
0
De
c
-
0
0
Ma
r
-
0
1
Ju
n
-
0
1
Se
p
-
0
1
De
c
-
0
1
Ma
r
-
0
2
Ju
n
-
0
2
Se
p
-
0
2
De
c
-
0
2
Ma
r
-
0
3
Ju
n
-
0
3
Se
p
-
0
3
De
c
-
0
3
Ma
r
-
0
4
Ju
n
-
0
4
Se
p
-
0
4
De
c
-
0
4
Ma
r
-
0
5
Ju
n
-
0
5
Se
p
-
0
5
De
c
-
0
5
Ma
r
-
0
6
Ju
n
-
0
6
Se
p
-
0
6
De
c
-
0
6
Ma
r
-
0
7
Ju
n
-
0
7
Se
p
-
0
7
De
c
-
0
7
Ma
r
-
0
8
Ju
n
-
0
8
Se
p
-
0
8
De
c
-
0
8
Ma
r
-
0
9
Ju
n
-
0
9
Se
p
-
0
9
De
c
-
0
9
(ug/L)
100 0
150.0
200.0
250.0
300.0
350.0
(u
g
/
L
)
TW4-5 Chloroform Values
0.0
50.0
100.0
De
c
-
9
9
Ma
r
-
0
0
Ju
n
-
0
0
Se
p
-
0
0
De
c
-
0
0
Ma
r
-
0
1
Ju
n
-
0
1
Se
p
-
0
1
De
c
-
0
1
Ma
r
-
0
2
Ju
n
-
0
2
Se
p
-
0
2
De
c
-
0
2
Ma
r
-
0
3
Ju
n
-
0
3
Se
p
-
0
3
De
c
-
0
3
Ma
r
-
0
4
Ju
n
-
0
4
Se
p
-
0
4
De
c
-
0
4
Ma
r
-
0
5
Ju
n
-
0
5
Se
p
-
0
5
De
c
-
0
5
Ma
r
-
0
6
Ju
n
-
0
6
Se
p
-
0
6
De
c
-
0
6
Ma
r
-
0
7
Ju
n
-
0
7
Se
p
-
0
7
De
c
-
0
7
Ma
r
-
0
8
Ju
n
-
0
8
Se
p
-
0
8
De
c
-
0
8
Ma
r
-
0
9
Ju
n
-
0
9
Se
p
-
0
9
De
c
-
0
9
550.0
750.0
950.0
1150.0
(u
g
/
L
)
TW4-6 Chloroform Values
(50.0)
150.0
350.0
6…2…7…1…2…2…1…3…1…2…1…1…2…2…
2000
3000
4000
5000
6000
(u
g
/
L
)
TW4-7 Chloroform Values
0
1000
2000
Se
p
-
9
9
De
c
-
9
9
Ma
r
-
0
0
Ju
n
-
0
0
Se
p
-
0
0
De
c
-
0
0
Ma
r
-
0
1
Ju
n
-
0
1
Se
p
-
0
1
De
c
-
0
1
Ma
r
-
0
2
Ju
n
-
0
2
Se
p
-
0
2
De
c
-
0
2
Ma
r
-
0
3
Ju
n
-
0
3
Se
p
-
0
3
De
c
-
0
3
Ma
r
-
0
4
Ju
n
-
0
4
Se
p
-
0
4
De
c
-
0
4
Ma
r
-
0
5
Ju
n
-
0
5
Se
p
-
0
5
De
c
-
0
5
Ma
r
-
0
6
Ju
n
-
0
6
Se
p
-
0
6
De
c
-
0
6
Ma
r
-
0
7
Ju
n
-
0
7
Se
p
-
0
7
De
c
-
0
7
Ma
r
-
0
8
Ju
n
-
0
8
Se
p
-
0
8
De
c
-
0
8
Ma
r
-
0
9
Ju
n
-
0
9
Se
p
-
0
9
De
c
-
0
9
Ma
r
-
1
0
200.00
300.00
400.00
500.00
(u
g
/
L
)
TW4-8 Chloroform Values
-100.00
0.00
100.00
Se
p
-
9
9
De
c
-
9
9
Ma
r
-
0
0
Ju
n
-
0
0
Se
p
-
0
0
De
c
-
0
0
Ma
r
-
0
1
Ju
n
-
0
1
Se
p
-
0
1
De
c
-
0
1
Ma
r
-
0
2
Ju
n
-
0
2
Se
p
-
0
2
De
c
-
0
2
Ma
r
-
0
3
Ju
n
-
0
3
Se
p
-
0
3
De
c
-
0
3
Ma
r
-
0
4
Ju
n
-
0
4
Se
p
-
0
4
De
c
-
0
4
Ma
r
-
0
5
Ju
n
-
0
5
Se
p
-
0
5
De
c
-
0
5
Ma
r
-
0
6
Ju
n
-
0
6
Se
p
-
0
6
De
c
-
0
6
Ma
r
-
0
7
Ju
n
-
0
7
Se
p
-
0
7
De
c
-
0
7
Ma
r
-
0
8
Ju
n
-
0
8
Se
p
-
0
8
De
c
-
0
8
Ma
r
-
0
9
Ju
n
-
0
9
Se
p
-
0
9
De
c
-
0
9
20.00
30.00
40.00
50.00
60.00
70.00
(u
g
/
L
)
TW4-9 Chloroform Values
-10.00
0.00
10.00
De
c
-
9
9
Ma
r
-
0
0
Ju
n
-
0
0
Se
p
-
0
0
De
c
-
0
0
Ma
r
-
0
1
Ju
n
-
0
1
Se
p
-
0
1
De
c
-
0
1
Ma
r
-
0
2
Ju
n
-
0
2
Se
p
-
0
2
De
c
-
0
2
Ma
r
-
0
3
Ju
n
-
0
3
Se
p
-
0
3
De
c
-
0
3
Ma
r
-
0
4
Ju
n
-
0
4
Se
p
-
0
4
De
c
-
0
4
Ma
r
-
0
5
Ju
n
-
0
5
Se
p
-
0
5
De
c
-
0
5
Ma
r
-
0
6
Ju
n
-
0
6
Se
p
-
0
6
De
c
-
0
6
Ma
r
-
0
7
Ju
n
-
0
7
Se
p
-
0
7
De
c
-
0
7
Ma
r
-
0
8
Ju
n
-
0
8
Se
p
-
0
8
De
c
-
0
8
Ma
r
-
0
9
Ju
n
-
0
9
Se
p
-
0
9
De
c
-
0
9
600
800
1000
1200
1400
(u
g
/
L
)
TW4-10 Chloroform Values
-200
0
200
400
De
c
-
0
1
Ma
r
-
0
2
Ju
n
-
0
2
Se
p
-
0
2
De
c
-
0
2
Ma
r
-
0
3
Ju
n
-
0
3
Se
p
-
0
3
De
c
-
0
3
Ma
r
-
0
4
Ju
n
-
0
4
Se
p
-
0
4
De
c
-
0
4
Ma
r
-
0
5
Ju
n
-
0
5
Se
p
-
0
5
De
c
-
0
5
Ma
r
-
0
6
Ju
n
-
0
6
Se
p
-
0
6
De
c
-
0
6
Ma
r
-
0
7
Ju
n
-
0
7
Se
p
-
0
7
De
c
-
0
7
Ma
r
-
0
8
Ju
n
-
0
8
Se
p
-
0
8
De
c
-
0
8
Ma
r
-
0
9
Ju
n
-
0
9
Se
p
-
0
9
De
c
-
0
9
Ma
r
-
1
0
2000
3000
4000
5000
6000
7000
(u
g
/
L
)
TW4-11 Chloroform Values
0
1000
2000
De
c
-
0
1
Ma
r
-
0
2
Ju
n
-
0
2
Se
p
-
0
2
De
c
-
0
2
Ma
r
-
0
3
Ju
n
-
0
3
Se
p
-
0
3
De
c
-
0
3
Ma
r
-
0
4
Ju
n
-
0
4
Se
p
-
0
4
De
c
-
0
4
Ma
r
-
0
5
Ju
n
-
0
5
Se
p
-
0
5
De
c
-
0
5
Ma
r
-
0
6
Ju
n
-
0
6
Se
p
-
0
6
De
c
-
0
6
Ma
r
-
0
7
Ju
n
-
0
7
Se
p
-
0
7
De
c
-
0
7
Ma
r
-
0
8
Ju
n
-
0
8
Se
p
-
0
8
De
c
-
0
8
Ma
r
-
0
9
Ju
n
-
0
9
Se
p
-
0
9
De
c
-
0
9
Ma
r
-
1
0
1
1
1
1
1
2
(u
g
/
L
)
TW4-12 Chloroform Values
0
0
0
1-
S
e
p
-
0
2
1-
D
e
c
-
0
2
1-
M
a
r
-
0
3
1-
J
u
n
-
0
3
1-
S
e
p
-
0
3
1-
D
e
c
-
0
3
1-
M
a
r
-
0
4
1-
J
u
n
-
0
4
1-
S
e
p
-
0
4
1-
D
e
c
-
0
4
1-
M
a
r
-
0
5
1-
J
u
n
-
0
5
1-
S
e
p
-
0
5
1-
D
e
c
-
0
5
1-
M
a
r
-
0
6
1-
J
u
n
-
0
6
1-
S
e
p
-
0
6
1-
D
e
c
-
0
6
1-
M
a
r
-
0
7
1-
J
u
n
-
0
7
1-
S
e
p
-
0
7
1-
D
e
c
-
0
7
1-
M
a
r
-
0
8
1-
J
u
n
-
0
8
1-
S
e
p
-
0
8
1-
D
e
c
-
0
8
1-
M
a
r
-
0
9
1-
J
u
n
-
0
9
1-
S
e
p
-
0
9
1-
D
e
c
-
0
9
0
1
1
1
1
(u
g
/
L
)
TW4-13
Chloroform has not been detected in TW4-13
0
0
0
Se
p
-
0
2
De
c
-
0
2
Ma
r
-
0
3
Ju
n
-
0
3
Se
p
-
0
3
De
c
-
0
3
Ma
r
-
0
4
Ju
n
-
0
4
Se
p
-
0
4
De
c
-
0
4
Ma
r
-
0
5
Ju
n
-
0
5
Se
p
-
0
5
De
c
-
0
5
Ma
r
-
0
6
Ju
n
-
0
6
Se
p
-
0
6
De
c
-
0
6
Ma
r
-
0
7
Ju
n
-
0
7
Se
p
-
0
7
De
c
-
0
7
Ma
r
-
0
8
Ju
n
-
0
8
Se
p
-
0
8
De
c
-
0
8
Ma
r
-
0
9
Ju
n
-
0
9
Se
p
-
0
9
De
c
-
0
9
0
1
1
1
1
(u
g
/
L
)
TW4-14
Chloroform has not been detected in TW4-14
0
0
0
Se
p
-
0
2
De
c
-
0
2
Ma
r
-
0
3
Ju
n
-
0
3
Se
p
-
0
3
De
c
-
0
3
Ma
r
-
0
4
Ju
n
-
0
4
Se
p
-
0
4
De
c
-
0
4
Ma
r
-
0
5
Ju
n
-
0
5
Se
p
-
0
5
De
c
-
0
5
Ma
r
-
0
6
Ju
n
-
0
6
Se
p
-
0
6
De
c
-
0
6
Ma
r
-
0
7
Ju
n
-
0
7
Se
p
-
0
7
De
c
-
0
7
Ma
r
-
0
8
Ju
n
-
0
8
Se
p
-
0
8
De
c
-
0
8
Ma
r
-
0
9
Ju
n
-
0
9
Se
p
-
0
9
De
c
-
0
9
Ma
r
-
1
0
3000
4000
5000
6000
7000
8000
9000
(u
g
/
L
)
TW4-15 Chloroform Values
0
1000
2000
Se
p
-
0
2
De
c
-
0
2
Ma
r
-
0
3
Ju
n
-
0
3
Se
p
-
0
3
De
c
-
0
3
Ma
r
-
0
4
Ju
n
-
0
4
Se
p
-
0
4
De
c
-
0
4
Ma
r
-
0
5
Ju
n
-
0
5
Se
p
-
0
5
De
c
-
0
5
Ma
r
-
0
6
Ju
n
-
0
6
Se
p
-
0
6
De
c
-
0
6
Ma
r
-
0
7
Ju
n
-
0
7
Se
p
-
0
7
De
c
-
0
7
Ma
r
-
0
8
Ju
n
-
0
8
Se
p
-
0
8
De
c
-
0
8
Ma
r
-
0
9
Ju
n
-
0
9
Se
p
-
0
9
De
c
-
0
9
200
300
400
500
600
(u
g
/
L
)
TW4-16 Chloroform Values
-200
-100
0
100
Se
p
-
0
2
De
c
-
0
2
Ma
r
-
0
3
Ju
n
-
0
3
Se
p
-
0
3
De
c
-
0
3
Ma
r
-
0
4
Ju
n
-
0
4
Se
p
-
0
4
De
c
-
0
4
Ma
r
-
0
5
Ju
n
-
0
5
Se
p
-
0
5
De
c
-
0
5
Ma
r
-
0
6
Ju
n
-
0
6
Se
p
-
0
6
De
c
-
0
6
Ma
r
-
0
7
Ju
n
-
0
7
Se
p
-
0
7
De
c
-
0
7
Ma
r
-
0
8
Ju
n
-
0
8
Se
p
-
0
8
De
c
-
0
8
Ma
r
-
0
9
Ju
n
-
0
9
Se
p
-
0
9
De
c
-
0
9
0.6
0.8
1.0
1.2
1.4
1.6
1.8
(u
g
/
L
)
TW4-17 Chloroform Values
0.0
0.2
0.4
Se
p
-
0
2
De
c
-
0
2
Ma
r
-
0
3
Ju
n
-
0
3
Se
p
-
0
3
De
c
-
0
3
Ma
r
-
0
4
Ju
n
-
0
4
Se
p
-
0
4
De
c
-
0
4
Ma
r
-
0
5
Ju
n
-
0
5
Se
p
-
0
5
De
c
-
0
5
Ma
r
-
0
6
Ju
n
-
0
6
Se
p
-
0
6
De
c
-
0
6
Ma
r
-
0
7
Ju
n
-
0
7
Se
p
-
0
7
De
c
-
0
7
Ma
r
-
0
8
Ju
n
-
0
8
Se
p
-
0
8
De
c
-
0
8
Ma
r
-
0
9
Ju
n
-
0
9
Se
p
-
0
9
De
c
-
0
9
200
300
400
500
(u
g
/
L
)
TW4-18 Chloroform Values
-100
0
100
Se
p
-
0
2
De
c
-
0
2
Ma
r
-
0
3
Ju
n
-
0
3
Se
p
-
0
3
De
c
-
0
3
Ma
r
-
0
4
Ju
n
-
0
4
Se
p
-
0
4
De
c
-
0
4
Ma
r
-
0
5
Ju
n
-
0
5
Se
p
-
0
5
De
c
-
0
5
Ma
r
-
0
6
Ju
n
-
0
6
Se
p
-
0
6
De
c
-
0
6
Ma
r
-
0
7
Ju
n
-
0
7
Se
p
-
0
7
De
c
-
0
7
Ma
r
-
0
8
Ju
n
-
0
8
Se
p
-
0
8
De
c
-
0
8
Ma
r
-
0
9
Ju
n
-
0
9
Se
p
-
0
9
De
c
-
0
9
3000
4000
5000
6000
7000
8000
(u
g
/
L
)
TW4-19 Chloroform Values
0
1000
2000
Ju
n
-
0
4
Se
p
-
0
4
De
c
-
0
4
Ma
r
-
0
5
Ju
n
-
0
5
Se
p
-
0
5
De
c
-
0
5
Ma
r
-
0
6
Ju
n
-
0
6
Se
p
-
0
6
De
c
-
0
6
Ma
r
-
0
7
Ju
n
-
0
7
Se
p
-
0
7
De
c
-
0
7
Ma
r
-
0
8
Ju
n
-
0
8
Se
p
-
0
8
De
c
-
0
8
Ma
r
-
0
9
Ju
n
-
0
9
Se
p
-
0
9
De
c
-
0
9
30000
40000
50000
60000
70000
(u
g
/
L
)
TW4-20 Chloroform Values
0
10000
20000
Ma
y
-
0
5
Au
g
-
0
5
No
v
-
0
5
Fe
b
-
0
6
Ma
y
-
0
6
Au
g
-
0
6
No
v
-
0
6
Fe
b
-
0
7
Ma
y
-
0
7
Au
g
-
0
7
No
v
-
0
7
Fe
b
-
0
8
Ma
y
-
0
8
Au
g
-
0
8
No
v
-
0
8
Fe
b
-
0
9
Ma
y
-
0
9
Au
g
-
0
9
No
v
-
0
9
Fe
b
-
1
0
150
200
250
300
350
400
(u
g
/
L
)
TW4-21 Chloroform Values
0
50
100
Ma
r
-
0
5
Ju
n
-
0
5
Se
p
-
0
5
De
c
-
0
5
Ma
r
-
0
6
Ju
n
-
0
6
Se
p
-
0
6
De
c
-
0
6
Ma
r
-
0
7
Ju
n
-
0
7
Se
p
-
0
7
De
c
-
0
7
Ma
r
-
0
8
Ju
n
-
0
8
Se
p
-
0
8
De
c
-
0
8
Ma
r
-
0
9
Ju
n
-
0
9
Se
p
-
0
9
De
c
-
0
9
2000
3000
4000
5000
6000
7000
(u
g
/
L
)
TW4-22 Chloroform Values
0
1000
2000
Ma
r
-
0
5
Ju
n
-
0
5
Se
p
-
0
5
De
c
-
0
5
Ma
r
-
0
6
Ju
n
-
0
6
Se
p
-
0
6
De
c
-
0
6
Ma
r
-
0
7
Ju
n
-
0
7
Se
p
-
0
7
De
c
-
0
7
Ma
r
-
0
8
Ju
n
-
0
8
Se
p
-
0
8
De
c
-
0
8
Ma
r
-
0
9
Ju
n
-
0
9
Se
p
-
0
9
De
c
-
0
9
0
1
1
1
1
(u
g
/
L
)
TW4-23
Chloroform has not been detected in TW4-23
0
0
0
Se
p
-
0
2
De
c
-
0
2
Ma
r
-
0
3
Ju
n
-
0
3
Se
p
-
0
3
De
c
-
0
3
Ma
r
-
0
4
Ju
n
-
0
4
Se
p
-
0
4
De
c
-
0
4
Ma
r
-
0
5
Ju
n
-
0
5
Se
p
-
0
5
De
c
-
0
5
Ma
r
-
0
6
Ju
n
-
0
6
Se
p
-
0
6
De
c
-
0
6
Ma
r
-
0
7
Ju
n
-
0
7
Se
p
-
0
7
De
c
-
0
7
Ma
r
-
0
8
Ju
n
-
0
8
Se
p
-
0
8
De
c
-
0
8
Ma
r
-
0
9
Ju
n
-
0
9
Se
p
-
0
9
De
c
-
0
9
1.5
2
2.5
3
3.5
(u
g
/
l
)
TW4‐24 Chloroform Values
0
0.5
1
Ju
n
‐07
Ju
l
‐07
Au
g
‐07
Se
p
‐07
Oc
t
‐07
No
v
‐07
De
c
‐07
Ja
n
‐08
Fe
b
‐08
Ma
r
‐08
Ap
r
‐08
Ma
y
‐08
Ju
n
‐08
Ju
l
‐08
Au
g
‐08
Se
p
‐08
Oc
t
‐08
No
v
‐08
De
c
‐08
Ja
n
‐09
Fe
b
‐09
Ma
r
‐09
Ap
r
‐09
Ma
y
‐09
Ju
n
‐09
Ju
l
‐09
Au
g
‐09
Se
p
‐09
Oc
t
‐09
No
v
‐09
De
c
‐09
Ja
n
‐10
Fe
b
‐10
0
1
1
1
1
(u
g
/
L
)
TW4-25
Chloroform has not been detected in TW4-25
0
0
0
Se
p
-
0
2
De
c
-
0
2
Ma
r
-
0
3
Ju
n
-
0
3
Se
p
-
0
3
De
c
-
0
3
Ma
r
-
0
4
Ju
n
-
0
4
Se
p
-
0
4
De
c
-
0
4
Ma
r
-
0
5
Ju
n
-
0
5
Se
p
-
0
5
De
c
-
0
5
Ma
r
-
0
6
Ju
n
-
0
6
Se
p
-
0
6
De
c
-
0
6
Ma
r
-
0
7
Ju
n
-
0
7
Se
p
-
0
7
De
c
-
0
7
Ma
r
-
0
8
Ju
n
-
0
8
Se
p
-
0
8
De
c
-
0
8
Ma
r
-
0
9
Ju
n
-
0
9
Se
p
-
0
9
De
c
-
0
9
Ma
r
-
1
0

Tab M
Chloroform Well Daily Inspection Form

Chloroform Investigation Wells ‐ Daily Inspection Report
Date:
Inspection Ti It Weather and Wellhead Protective 
B (kOK
Electric System 
(kOK t
Heat Lamp 
Operational Status 
Flow Meter 
Operational (mark Pump Operational 
(kOK t Ab lOti Pt tilPbl
Chloroform Investigation Wells  Daily Inspection Report
Inspection 
No.Time Inspector
Weather and 
Temp.Boxes (mark OK or 
note otherwise)
(mark OK or note 
otherwise)
Operational Status 
(mark OK or note 
otherwise)
Operational (mark 
OK or note 
otherwise)
(mark OK or note 
otherwise)
Abnormal Operation or Potential Problems
1
2
3
4
5
6
7
8

Tab N
CSV Transmittal Letter

Jo Ann Tischler
From:
Sent:
To:
Cc:
Subject:
Attachments:
Dear Mr. Finerfrock,
Jo Ann Tischler
Wednesday, May 19,20105:31 PM
'Dane Finerfrock'
David Frydenlund; Harold Roberts
Transmittal of CSV Files White Mesa Mill 2 010 01 Chloroform Monitoirng
C10020658.csv; C10020848.csv; C10030236.csv
Attached to this email are electronic copies of laboratory results for chloroform monitoring conducted at the White
Mesa Mill during the first quarter of 2010, in Comma Separated Value (CSV) format.
Please contact me at 303-389-4132 if you have any questions on this transmittal.
Your Truly,
Jo Ann Tischler
Denison Mines (USA) Corp.
Director, Compliance and Permitting
1