DRC-2010-002341 - 0901a06880361a31

Denison Mines (USA) Corp.
1050 17th Street, Suite 950
Denver, CO 80265
USA
Tel : [phone]
Fax : [phone]
www.denisonmines.com
Sent VIA Federal Express

February 27, 2010

Mr. Dane L. Finerfrock
Co-Executive Secretary
Utah Water Quality Board
State of Utah Department of Environmental Quality
168 North 1950 West
Salt Lake City, UT 84114-4850

Re: Transmittal of 4th Quarter 2009 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
4th Quarter of 2009 as required by the Notice of Violation and Groundwater Corrective Action
Order, UDEQ Docket No. UGQ-20-01.

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
White Mesa Uranium Mill

Chloroform Monitoring Report

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

4th Quarter
(October through December)
2009

Prepared by:

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

February 2010
1
1.0 INTRODUCTION

This is the Quarterly Chloroform Monitoring Report, as required under State of Utah
Notice of Violation and Groundwater Corrective Action Order State of Utah Department
of Environmental Quality (“UDEQ”) Docket No. UGQ-20-01 for the 2nd Quarter of 2009
(the “Quarter”) for Denison Mines’ (USA) Corp.’s (“DUSA’s”) White Mesa Uranium
Mill (the “Mill”). This Report also includes the Operations Report for the Long Term
Pump Test at MW-4, TW4-19, TW4-15 (MW-26) and TW4-20 for the Quarter.

2.0 SAMPLING AND MONITORING PLAN

2.1 Description of Monitor Wells Sampled During the Quarter

During the Quarter, the following chloroform contaminant investigation groundwater
samples and measurements were taken:

2.1.1 Groundwater Monitoring

Groundwater Monitoring was performed in all of the chloroform monitoring wells, as
follows:

• MW-4
• TW4-1
• TW4-2
• TW4-3
• TW4-4
• TW4-5
• TW4-6
• TW4-7
• TW4-8
• TW4-9
• TW4-10
• TW4-11
• TW4-12

• TW4-13
• TW4-14
• MW-26
• TW4-16
• MW-32
• TW4-18
• TW4-19
• TW4-20
• TW4-21
• TW4-22
• TW4-23
• TW4-24
• TW4-25

The locations of these wells are indicated on the map attached under Tab A.

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

• Chloroform
• Chloromethane
• Carbon tetrachloride
• Methylene chloride
• Chloride
• Nitrogen, Nitrate + Nitrite as N
2

2.1.2 Groundwater Head/Level Monitoring

Depth to groundwater was taken in the following wells and/or piezometers during the
Quarter:

a) All of the chloroform contaminant investigation wells listed in paragraph 2.1.1
above in two measurement events on December 11, 2009;
b) The point of compliance monitoring wells under the Mill’s Groundwater
Discharge Permit (“GWDP”) on December 11, 2009.
c) Piezometers – P-1, P-2, P-3, P-4, and P-5 on December 11, 2009.
d) Nitrate monitoring wells on December 14, 2009.

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

2.2 Sampling Methodology, Equipment and Decontamination Procedures

The sampling methodology, equipment and decontamination procedures that were
performed for the chloroform contaminant investigation during the Quarter can be
summarized as follows:

2.2.1 Well Purging and Depth to Groundwater

a) A list is gathered of the wells in order of increasing chloroform contamination.
The order for purging is thus established. Mill personnel start purging with all of
the non-detect wells and then move to the more contaminated wells in order of
chloroform contamination, starting with the wells having the lowest chloroform
contamination; and

b) Before leaving the Mill office, the pump and hose are rinsed with de-ionized
(“DI”) water. Mill personnel then proceed to the first well which is the well
indicating 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 (measurements are made using the same instrument used
for the monitoring wells under the Mill’s GWDP). The Grundfos pump (a 6 gpm
pump) is then lowered to the bottom of the well and purging is begun. At the
first well, the purge rate is established for the purging event by using a calibrated
5 gallon bucket. After the evacuation of the first well has been completed, the
pump is removed from the well and the process is repeated at each well location
moving from least contaminated to most contaminated well. All wells are
capped and secured prior to leaving the sampling location.

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2.2.2 Sampling

a) Following the purging of all chloroform investigation wells, the sampling takes
place (usually the next morning). Prior to leaving the Mill office to sample, a
cooler along with blue 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 dedicated bailers and the wells are purged by means of a
dedicated portable pump. Each quarterly pumping and sample collection event
begins at the location least affected by chloroform (based on the previous
quarter’s sampling event) and proceeds by affected concentration to the most
affected location. The dedicated portable pump is appropriately decontaminated
prior to each purging sampling event and the QA rinsate sample is collected after
said decontamination but prior to the commencement of the sampling event. In
response to discussions held with UDEQ on October 29, 2009 relative to purging
and decontamination of sampling equipment, mill sampling personnel have been
re-instructed as to decontamination procedures in accordance with Section 6.2.5
of the QAP and purging practices.

b) Mill personnel use a disposable bailer to sample each well. 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;

(i) First, a set of VOC vials is filled. This set consists of three 40 ml vials
provided by the Analytical Laboratory. The set is not filtered and is
preserved with HCl;
(ii) Second, a 500 ml sample is collected for Nitrates/Nitrites. This sample is
also not filtered and is preserved with H2SO4 (the bottle for this set is also
provided by the Analytical Laboratory);
(iii) Third, a 500 ml sample is collected for Chloride. This sample is not
filtered and is not preserved; and

c) 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 blue ice. The well is
then recapped and Mill personnel proceed to the next well.

DUSA completed, and transmitted to UDEQ on May 25, 2006, a revised Quality
Assurance Plan (“QAP”) for sampling under the Mill’s GWDP. The GWDP QAP was
reviewed by UDEQ and has been approved for implementation. The QAP provides a
detailed presentation of procedures utilized for groundwater sampling activities under the
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
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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 a separate document. The chloroform QA
document describes the differing needs of the chloroform investigation program, and is
and attachment to the GWDP QAP where QA needs other than those described in the
chloroform QA document are addressed.

2.3 Field Data Worksheets

Attached under Tab B are copies of all Field Data Worksheets that were completed
during the Quarter for the chloroform contaminant investigation monitoring wells listed
in paragraph 2.1.1 above and sampled during the sampling event of December 14 to 17,
December 21 to 22, and December 28 to 29, 2009.

2.4 Depth to Groundwater Sheets

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 and TW4-20 as well as the monthly depth to
groundwater monitoring data for chloroform contaminant investigation wells measured
during the quarter. Depth-to-groundwater measurements which were utilized for
groundwater contours are included on the Field Data Worksheets at Tab B of this report.

3.0 DATA INTERPRETATION

3.1 Interpretation of Groundwater Levels, Gradients and Flow Directions.

3.1.1 Current Site Groundwater Contour Map

The contour map (Tab D) uses the December 11, 2009 data for all the wells listed in
paragraph 2.1.2 a0, b), and c),above, and the December 14, 2009 data for the wells listed
in 2.1.2 d) above..

Also included under Tab D is a groundwater contour map of the portion of the Mill site
where the four chloroform pumping wells are located, with hand-drawn stream tubes, in
order to demonstrate hydraulic capture from the pumping

3.1.2 Comparison of Current Groundwater Contour Maps to Groundwater Contour
Maps for Previous Quarter

The groundwater contour maps for the Mill site for the third quarter of 2009, as submitted
with the Chloroform Monitoring Report for the third quarter of 2009, are attached under
Tab E.
5

A comparison of the water table contour maps for the Quarter 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. 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 in the northeastern portion of the site are
primarily due to the inclusion of the TWN-series wells in the preparation of the maps and
to the surveying of well TW4-25.

Reported increases in water levels of approximately 11 feet in well MW-20 and of
approximately 12 feet in well TW4-25 occurred. The reported water level at MW-20 is
more typical for the well than the anomalously low value reported for the third quarter.
The change in water level elevation at TW4-25 is due to recent surveying of the well and
not to a significant change in depth to water.

A reported decrease in water level of approximately 13 feet occurred in pumping well
TW4-19 and a reported increase in water level of approximately 5 feet occurred in
pumping well MW-26 (TW4-15). Water level changes at pumping wells MW-4 and
TW4-20 were less than 5 feet.

Water level fluctuations at pumping wells MW-4, MW-26 (TW4-15), 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 13 feet occurred in well TW4-19 and the largest increase (decrease in
drawdown), of approximately 5 feet, occurred at MW-26 (TW4-15).

3.1.3 Hydrographs

Attached under Tab F are hydrographs showing groundwater elevation in each
chloroform contaminant investigation monitor well over time.

3.1.4 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.

3.1.5 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, and TW4-20. 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. The relatively high transmissivity of the
perched zone in the vicinity of the pumping wells results in the wells having a relatively
6
high productivity. The combination of relatively high productivity and high chloroform
concentrations allows a high rate of chloroform mass removal.

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 the pumping
wells 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 the pumping wells is occurring. As
noted in Section 3.1.2, a decrease in water level (increase in drawdown) occurred at
TW4-19, and an increase in water level (decrease in drawdown) occurred at MW-26
(TW4-15) since the last quarter. 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 TW4-19 and the decrease in drawdown at MW-26 (TW4-15)
have increased, and decreased, respectively, the apparent capture zones of these wells
relative to other nearby pumping wells. The apparent expansion of capture in the
northeastern portion of the site is primarily due to the inclusion of the TWN-series wells
in the preparation of the maps.

Although high chloroform concentrations exist at some locations downgradient of the
pumping wells (for example, near TW4-4), the low permeability of the perched zone at
these locations would prevent significant rates of chloroform mass removal should these
wells be pumped. By pumping at the more productive, upgradient locations, however,
the rate of downgradient chloroform migration will be diminished because of the
reduction in hydraulic gradients, and natural attenuation will be more effective.

3.2 Interpretation of Analytical Results

3.2.1 Copy of Laboratory Results

Included under Tab H of this Report are copies of all laboratory analytical results for the
groundwater quality samples collected under the chloroform contaminant investigation
on December 14 to 17, December 21 to 22, and December 28 to 29, 2009 along with the
laboratory analytical results for required QC samples.

All required wells were sampled and analyzed. Due to a labeling error, the laboratory
mistakenly labeled the analytical results for TW4-5, TW4-6, TW4-10, TW4-18 and
TW4-21, as TWN-5, TWN-6, TWN-10, TWN-18 and TWN-21, respectively. (The TWN
series refers to nitrate-nitrite wells). Despite the mis-labeling of result sheets as nitrate
wells sheets, the QA manager has confirmed that these samples and results are, in fact,
for the appropriate TW4 series chloroform monitoring wells.

3.2.2 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
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investigation during the Quarter, in Comma Separated Values (CSV). A copy of the
transmittal e-mail is included under Tab I.

3.2.3 Current Chloroform Iso-concentration Map

Included under Tab J of this Report is a current chloroform iso-concentration map for the
Mill site.

3.2.4 Data and Graphs Showing Chloroform Concentration Trends

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.

3.2.5 Analysis of Analytical Results
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 TW4-15
compared to last quarter;

b) Chloroform concentrations have decreased by more than 20% in the following
wells compared to last quarter: TW4-2, TW4-4, TW4-5, TW4-10, TW4-18,
TW4-19, TW4-21, and TW4-22;

c) Chloroform concentrations have remained within 20% in the following wells
compared to last quarter: MW-4, TW4-1, TW4-6, TW4-7, TW4-11, TW4-20,
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
increased from 13,000 µg/L to 15,000 µg/L, the concentration in pumping well TW4-19
decreased from 6,600 µg/L to 4,700 µg/L, and the concentration in well TW4-22
decreased from 2,300 µg/L to 380 µg/L. Wells TW4-23 and TW4-25 remained non-
detect for chloroform, and the concentration in well TW4-24 decreased slightly from 1.4
µg/L to 1.2 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.

Chloroform concentrations 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, decreased from 280 µg/L to 250
8
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.

The slow rate of chloroform migration in the vicinity of TW4-6 is demonstrated by the
contrast between the rate of increase in chloroform at this well compared 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.

3.3 Quality Assurance Evaluation And Data Validation

Quality assurance evaluation and data validation procedures in effect at the time of
sampling were followed. These involve three basic types of evaluations: field QC
checks; Analytical Laboratory checks; and checks performed by DUSA personnel, as
described below.

3.3.1 Field QC Checks

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, and a DI
field blank. These check samples are to be generated for each quarterly sampling
episode. During the 4th Quarter 2009 duplicates (TW4-65, duplicate of TW4-17) and
(TW4-70, duplicate of TW4-2), a DI field blank (TW4-60), and three trip blanks were
collected and analyzed. Rinsates were also collected between well samples, and 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.

3.3.2 Analytical Laboratory QA/QC Procedures

The Analytical Laboratory has provided summary reports of the analytical quality
assurance/quality control (QA/QC) measurements necessary to maintain conformance
with NELAC certification and reporting protocol. The Analytical Laboratory QA/QC
Summary Report, including copies of the Mill’s Chain of Custody and Analytical
Request Record forms, for the fourth quarter sampling event, are included under Tab H.

3.3.3 Mill QA Manager Review

The Mill QA Manager, which, for these sampling events was DUSA’s Director of
Permitting and Compliance, performed four types of reviews: a determination of whether
Mill sampling personnel followed Mill sampling procedures; a review of the results from
the Field QC Checks; a review of analytical reports for holding times and qualifying
9
indicators for the data; and a review of the Analytical Laboratory QA/QC analysis. The
results of the QA Manager’s review are discussed below.

a) Adherence to Mill Sampling SOPs

On a review of adherence by Mill personnel to the sampling procedures summarized in
Section 2.2 above, the QA Manager concluded that such procedures had been followed.

b) Results From Field QC Checks

The duplicate samples of TW4-2, and TW4-17 indicated a relative percent
difference within the prescribed standard of 20% for all parameters duplicated.
The rinsate sample preceding TW4-2 also contained trace presence of
chloroform.

During previous report periods it was noted that field blank de-ionized water
continued to yield trace volatile organic presence (i.e. chloroform). This matter
was further investigated by the QA manager. Samples were collected upstream,
downstream and between columns of the deionizer system. to further isolate the
cause of this low level contaminant source. The Mill plans to repeat this
additional testing one or more additional periods,

The field DI blank for the 4th quarter sampling period did not indicate the
presence of chloroform.

In response to program improvement needs the QA Manager has initiated a documented
review of field recorded parameters and their adherence with Quality Assurance Plan
requirements with regard to well purging volumes, and stability of parameters.

Necessary corrective actions from last monitoring period, completed in accordance with
Section 10 of the QAP, are described below:

1. Identification and definition of the problem

The three problems previously identified were
• the failure to evacuate two casing volumes during purging operations,
• the failure to measure at least two field parameter data sets within +/-
10%, and
• the failure to measure turbidity in collected samples.

2. Assignment of responsibility for investigation the problem

The problem has been investigated by the QA Manager.

3. Investigation and determination of cause of the problem

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Sampling personnel previously believed that the process of decontaminating
prior to each sampling day and proceeding from the least contaminated to
most contaminated well was within the QAP guidelines. However, based on
discussions with UDEQ on October 29, 2009, it became apparent that the
sampling pump must be decontaminated between each sample location in
accordance with Section 6.2.5 of the QAP.

Further investigation as to why turbidity was not measured in all wells has
identified that the field data worksheet did not have a specific space to record
turbidity, and the sampling personnel had not received clear enough
instruction that this measurement is required, even though the field sheets do
not so indicate. T

4. Determination of a corrective action to eliminate the problem

• Sampling personnel have been informed that the procedures outlined in
the QAP for well purging with regard to evacuation of two casing volumes
and at least two sets of field parameters within 10% RDP must be adhered
to.
• Sampling personnel have been informed that non-dedicated sampling
equipment must be decontaminated before each sampling event and
between each individual sample in accordance with Section 6.2.5 of the
QAP.
• Sampling personnel have been informed that turbidity measurements are
required for all samples collected..

5. Assigning and accepting responsibility for implementing the corrective action

It will be the responsibility of the RSO and sampling technicians to implement
the corrective action.

6. Implementing the corrective action and evaluating effectiveness

Implementation of the corrective action has occurred by means of the
notification and improved instruction cited under item 4, above.

7. Verifying that the corrective action has eliminated the problem

• Two Casing Volumes
The corrective action (instruction) appears to have eliminated the
problem. Field personnel have attempted to evacuate two casing
volumes on all wells sampled in this period. Further refinement of the
method used to improve the accuracy of estimating the correct volume
in the field, may be required, as discussed below.

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• Rinsate
The corrective action (instruction) appears to have eliminated the
problem. During the fourth quarter sampling event, the pump was
decontaminated, and rinsate samples collected, before each well
sample was collected.

• Turbidity
The corrective action (instruction) appears to have eliminated the
turbidity measurement problem. During the fourth quarter sampling
event, turbidity was measured and recorded for all wells.

Results of the review of field data sheets for the current (fourth quarter) monitoring
period are summarized in the table below:

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Summary of Field Data QC Review
2x
Casings Vol OK RPD RPD RPD RPD RPD
Is NTU
<5
(gal) (Y/N) (%) (%) (%) (%) (%)
T1 T2 T1 T2 T1 T2 T1 T2 T1 T2
MW-4 No
Param
2013 6.63 14.09 410 0
Y
TW4-1 64.2 150 Y 2259 2274 -0.17 6.64 6.67 -0.11 13.05 13.19 -0.27 430 430 0.00 25.3 25.7 -0.39 N
TW4-2 68.64 66 Y 2741 2775 -0.31 6.98 7 -0.07 13.74 13.76 -0.04 488 484 0.21 33.1 32.3 0.61 N
TW4-3 66.48 66 Y 1800 1803 -0.04 6.82 6.83 -0.04 13.4 13.45 -0.09 475 474 0.05 4.2 3.8 2.50 Y
TW4-4 66.5 66 Y 2503 2498 0.05 6.76 6.78 -0.07 14.04 14.06 -0.04 469 467 0.11 10.8 9.3 3.73 N
TW4-5 86.02 84 Y 1761 1763 -0.03 6.93 6.97 -0.14 14.41 14.41 0.00 587 585 0.09 1.7 2.6 -10.47 Y
TW4-6 36.84 48 Y 3544 3522 0.16 7.22 7.45 -0.78 13.55 13.56 -0.02 508 501 0.35 531 136.6 29.54 N
TW4-7 1 68.8 66 Y 1758 1860 -1.41 7.11 7.15 -0.14 13.43 13.5 -0.13 486 481 0.26 18.8 48.5 -22.07 N
TW4-8 75.46 72 Y 3293 3329 -0.27 7.08 7.13 -0.18 13.39 13.24 0.28 266 241 2.47 7.4 7.3 0.34 N
TW4-9 87.42 84 Y 2552 2564 -0.12 6.72 6.93 -0.77 13.54 13.44 0.19 362 358 0.28 1.5 1 10.00 Y
TW4-10 73.88 72 Y 2702 2848 -1.32 6.82 6.92 -0.36 14.1 14.11 -0.02 514 502 0.59 68 51 7.14 N
TW4-11 53.46 54 Y 1769 1770 -0.01 7.01 6.99 0.07 12.94 13.1 -0.31 510 509 0.05 3.4 3.2 1.52 Y
TW4-12 82.2 78 N 792.4 788.1 0.14 7.01 7.05 -0.14 13.81 13.82 -0.02 475 471 0.21 3.6 3.9 -2.00 Y
TW4-13 73.46 72 Y 1582 1583 -0.02 7.02 6.86 0.58 14.3 14.34 -0.07 466 468 -0.11 15.7 16.5 -1.24 N
TW4-14 2 41.96 12 N 2761 4101 -9.76 7.13 6.96 0.60 9.89 12.23 -5.29 460 474 -0.75 20.5 13.1 11.01 N
TW4-15 NA 3506 6.84 14.01 449 70.3 N
TW4-16 99.48 102 Y 3750 3738 0.08 6.87 6.91 -0.15 14.25 14.03 0.39 375 371 0.27 3.6 1.3 23.47 Y
TW4-17/
MW32
66.2 71.82 Y 4037 4063 -0.16 6.5 6.39 0.43 13.68 13.21 0.87 370 246 10.06 1.1 0.5 18.75 Y
TW4-18 105.26 102 Y 1410 1413 -0.05 6.82 6.8 0.07 14.3 14.43 -0.23 543 540 0.14 0.4 0.1 30.00 Y
TW4-19 NA 3067 7.02 14.5 366 0.8 Y
TW4-20 NA 3462 6.5 15.2 529 4.7 Y
TW4-21 86.16 84
Y 3200 3210 -0.08 7.05 7.1 -0.18 15.03 15.04 -0.02 564 559 0.22 1.1 1.2 -2.17 Y
TW4-22 77.64 78
Y 4981 5207 -1.11 7.14 6.97 0.60 13.89 14.07 -0.32 484 481 0.16 20.8 21.1 -0.36 N
TW4-23 73.34 72
Y 3687 3690 -0.02 6.57 6.57 0.00 13.33 13.35 -0.04 344 328 1.19 92.5 92.4 0.03 N
TW4-24 85.7 84 Y 9039 9084 -0.12 6.86 6.87 -0.04 13.99 13.9 0.16 463 462 0.05 30.535.71 Y
TW4-25 126.6 126 Y 2965 2966 -0.01 7.16 7.25 -0.31 13.81 13.79 0.04 398 393 0.32 3.6 3.8 -1.35 Y
Note 1 The well ran dry after last parameters collected
2 The well was evalcuated to dryness
Well
Vol
pumped
(gal)Conductance pH
Temp. Turbidity
(0C) Potential (NTU)
Redox.

As indicated in the table:
• Sampling personnel have implemented a procedure to estimate the
evacuation/purging of two sample volumes from each required well.
• Sampling personnel have implemented a real time calculation in the field to
confirm that required measured parameters have stabilized within a 10% RPD for
each required well.
• Sampling personnel have implemented the measurement of turbidity for each
required well.
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In addition, it was identified that Chain of Custody sheets for two of the three shipped
sample batches recorded that trip blanks were present in the batch. One of the Chain of
Custody sheets did not record that a trip blank was included. In fact, trip blanks were
correctly shipped from the lab, included in the shipments from the Mill, and analyzed
with all three batches. Field sampling personnel indicated that the missed entry on the
Chain of Custody was an oversight due to the large amount of information logged on the
sheets at one time. Every other entry on all Chain of Custody sheets was correct.
Based on the results in this quarter’s field QA/QC review,
1. Identification and definition of the problem

Since implementation of the new measurement procedures:

• Evacuated/purged well volumes now approximate the required two casing
volumes, but several of the well volumes appear to vary from 5 to 8% below the
targeted volume.
• Field calculations of RPD as a basis for well stability have resulted in acceptable
RPD’s (within 10%) for all but one parameter (redox potential) in one well.
• Turbidity measurements, now collected for all required wells, exceeded either the
maximum turbidity (5NTU), the stability indicator (within 10% RPD), or both, for
18 out of 25 wells.

2. Assignment of responsibility for investigation the problem

The problem has already been investigated by the QA Manager.

3. Investigation and determination of cause of the problem

Purged Volumes
Sampling personnel use purging time, calculated from the required volume and
purging rate, as the indicator that they have purged sufficient volume. The
calculation is not sufficiently conservative (slightly underestimates the number of
minutes) to purge. Steps are underway to modify the estimation for each well to
make the estimation more conservative, and add in a margin of safety in the
measurement.

RPD
Sampling personnel calculate the RPD between measurements and round the
resulting RPD value down to the nearest whole percent. Steps are underway to
instruct the sampling personnel to round up, and re-equilibrate and re-measure the
parameter a rounded up value is greater than 10%.

Turbidity
Data indicate that it may not be feasible to achieve a turbidity level less than 5 and
a stabilized turbidity between any two measurements within 10% RPD.
14
Discussions are underway with UDEQ to address the issue that it may not be
appropriate or feasible to achieve consistent turbidity levels of 5 NTU in the
White Mesa chloroform program wells under the current evacuation scheme, and
that other well purging approaches, such as micro-purging, may be more
appropriate.

4. Determination of a corrective action to eliminate the problem

Purged Volumes
Steps are underway to modify the estimation for each well to make the estimation
more conservative, and add in a margin of safety in the measurement.

RPD
Steps are underway to instruct the sampling personnel to round up, and re-
equilibrate and re-measure the parameter a rounded up value is greater than 10%.

Turbidity
Discussions are underway with UDEQ to address the issue that it may not be
appropriate or feasible to achieve consistent turbidity levels of 5 NTU in the
White Mesa chloroform program wells under the current evacuation scheme, and
that other well purging approaches, such as micro-purging, may be more
appropriate. A proposed request for a variance from the turbidity requirement
will be submitted during the next monitoring period. Development of an alternate
approach, and proposed changes to the QAO, are underway.

5. Assigning and accepting responsibility for implementing the corrective action

It will be the responsibility of the RSO and sampling technicians to implement
the corrective action.

6. Implementing the corrective action and evaluating effectiveness

Implementation of the corrective action for the casing volumes and RPD
consistency are already underway. Implementation of the corrective action
for turbidity will follow development and UDEQ approval of an agreed upon
action, as discussed in item 4.

7. Verifying that the corrective action has eliminated the problem

15
Purged Volumes
Verification will occur after field data is received from the next sampling period

RPD
Verification will occur after field data is received from the next sampling period
•
Turbidity
Verification will occur following submittal of a proposal to UDEQ to modify the
well purging approach.

c) Review of Analytical Laboratory QA/QC Analysis and Analytical Reports
sample
(i) Check samples were reviewed for each method used in analyzing the
chloroform investigation samples. These methods were:

Parameter Method

Nitrogen, (Nitrate + Nitrite as N)E353.2
Chloroform,
Carbon tetrachloride
Chloromethane
Methylene chloride
E624
E624
E624
E624
Chloride A4500-CL B

(ii) The check samples included at least the following: a method blank, a
laboratory control spike (sample), a matrix spike and a matrix spike
duplicate;

(iii) All qualifiers, if any, and the corresponding explanations in the summary
reports, were reviewed by the QA Manager. Only two qualifiers were
reported. One was reported for matrix interference in the nitrate/nitrate
result in one of the analyzed monitoring location samples, however, the
reporting limit was maintained below the parameter standard and the
reported result. One additional qualifier was reported for spike recovery
outside acceptable limits for two parameters: The methylene chloride
spike for sample TW4-20. One of the surrogate species in the spike,
dibromofluoromethane, had a % recovery outside the acceptable limits,
however the other three of the four surrogate species in the spike had %
recoveries within the required ranges. The sample matrix spike for one
nitrate/nitrite sample also had a % recovery outside acceptable limits.

(iii) The laboratory holding time for all analyses was within chloroform
specification and sample temperature was acceptable upon receipt.

16
4.0 LONG TERM PUMP TEST AT MW-4, TW4-15 (MW-26), TW4-19 AND
TW4-20, OPERATIONS REPORT

4.1 Introduction

As a part of the investigation of chloroform contamination at the Mill site, IUSA has been
conducting a Long Term Pump Test on MW-4, TW4-19, TW4-15 (MW-26) and TW4-
20. 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.

4.2 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
and from TW4-20 on August 4, 2005. 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. IUSA 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:

a) Measurement of water levels at MW-4, TW4-19, TW4-15 (MW-26), and TW4-
20 on a weekly basis, and at selected temporary wells and permanent monitoring
wells on a monthly basis (See Section 3.1 and Tabs B and C for a discussion of
the water levels);

b) Measurement of pumping history:

(i) pumping rates
(ii) total pumped volume
(iii) operational and non-operational periods;

c) Periodic sampling of pumped water for chloroform and nitrate/nitrite analysis
and other constituents, as discussed in detail in Section 3.2 above.

4.3 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, water levels in that well have been measured weekly. Depth to
17
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 and TW4-20 and the October and December monthly Depth to Water
monitoring sheets for all of the chloroform contaminant investigation wells are typically
included under Tab C but will be transmitted separately on December 1, 2008. Monthly
depth to water measurements for September are recorded in the Field Data Worksheets
included under Tab B.

4.4 Pumping Rates and Volumes

4.4.1 MW-4
Approximately 91,320 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 purging 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.

4.4.2 TW4-19

Approximately 454,205 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.

4.4.3 TW4-15 (MW-26)

Approximately 61,960 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 purging 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.
4.4.4 TW4-20
Approximately 208,790 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.

18
4.4.5 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 the table below, indicating
that a total of 480.0.pounds of chloroform have been removed.
Chloroform Mass
removal (lbs)
MW4 TW4-15TW4-19TW4-20Total
Mass
Removed
(lbs)
Total lbs as of 1st
Qtr 2007
36.8 12.9 150.2 87 286.9
2nd Qtr 2007 lbs
removed
1.40.1 02.5 4
3rd Qtr 2007 lbs
removed
2.2 0.8 2.9 3.1 9
4th Qtr 2007 lbs
removed
1.7 1 3.1 4.8 10.6
1st Qtr 2008 lbs
removed
1.7 0.4 4.6 7.2 13.9
2nd Qtr 2008 lbs
removed
1.3 0.5 3.2 9.9 14.9
3rd Qtr 2008 lbs
removed
1.2 0.3 15.9 9.3 26.7
4th Qtr 2008 lbs
removed
1.3 0.3 20.7 0.4 22.7
1st Qtr 2009 lbs
removed
1.7 0.4 4.3 3.6 10
2nd Qtr 2009 lbs
removed
6.8 0.2 3.7 2.8 13.5
3rd Qtr 2009 lbs
removed
1.5 0.4 11.1 5.5 18.5
4th Qtr 2009 lbs
removed
4.8 0.6 17.8 26.1 49.3
Total lbs
chloroform
removed
62.4 17.9 237.5 162.2 480
Mass of Chloroform Removed Per Well Per Quarter

19
4.5 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, Operational Problems.

No operational problems in the pumping wells were reported during the 4th Quarter,
2009 period.

4.7 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.
4.8 Chloroform Analysis

Monthly chloroform sampling ceased on November 8, 2003. From that time all
chloroform contaminant investigation wells were sampled on a quarterly basis. The
sample results are discussed above in Section 3.2.

5.0 CONCLUSIONS AND RECOMMENDATIONS

The water level contour map for the Quarter indicates that effective capture of water
containing high chloroform concentrations in the vicinity of the pumping wells is
occurring.

Between the third and fourth quarters of 2009, the chloroform concentration in pumping
well TW4-20 increased from 13,000 µg/L to 15,000 µg/L, the concentration in pumping
well TW4-19 decreased from 6,600 µg/L to 4,700 µg/L, and the concentration in well
TW4-22 decreased from 2,300 µg/L to 380 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), indicated 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
1.2 µg/L at TW4-24.

The chloroform concentration at downgradient well TW4-6, which remained outside the
plume until the first quarter of 2009, decreased from 280 to 250 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-
20
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
chloroform migration by removing chloroform mass and reducing average hydraulic
gradients, thereby allowing natural attenuation to be more effective.

6.0 SIGNATURE AND CERTIFICATION

This document was prepared by Denison Mines (USA) Corp. on February 27, 2010.

DENISON MINES (USA) CORP.

By:

David C. Frydenlund
Vice President, Regulatory Affairs and Counsel

21
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 of my knowledge and belief, true, accurate, and complete. I am aware that there are
significant penalties for submitting false information, including the possibility of fine and
imprisonment for knowing violations.

______________________________________
David C. Frydenlund
Vice President, Regulatory Affairs and Counsel
Denison Mines (USA) Corp.

INDEX OF TABS

Tab A Site Plan and Perched Well Locations White Mesa Site
Tab B Field Data Worksheets
Tab C Depth to Water Sheets
Tab D Kriged Current Quarter Groundwater Contour Map, Details Map, and Depth 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 CSV Transmittal Letter
Tab J Kriged Current Quarter Chloroform Isoconcentration Map
Tab K Analyte Concentrations Over Time
Tab L Chloroform Concentration Trend Graphs
Tab M Chloroform Well Daily Inspection Form

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/feb10/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
TabB
Field Data Worksheets
Order of Contamination for 3rd Quarter 2009 Chloroform Purging Event
Chloroform Water Well
Well Sample time Levels level Depth 1;),-15 -D'l
W4-3 10D1 ND '1q .d!1 100 Ono -:J£.
TW4-12 of.Q.7 ND "\K'l7 101.5 oCIYO -\::I.R 2-/0"'
TW4-13 (,'>3-;'C,ND '-\'1.ljj 105.5 IllS -i3 R I
i2·t&TW4-14 0'"15 ND Q:;\.73 121.33
TW4-17 Ico'\("11\\4\NO 77.43 130 ~_-.'1",-
TW4-23 Q'l§i NO P·OI 123.3 IVIZ -t3£..
rrW4-25 07'-l1 NO '-157~143.15 ISS::'-:;>.5 R
{~:::0'1:>,0 ND (,lS.l~126 '""-·JOq;J.~NO 121.33 1:;t45 -1 R.2./&
2·11 TW4-16 0'1<.\0 ND !?5.<{142 14?>;}.-If.R /
TW4-24 ()"to(',1.5 122 1'-1':>-g.4R
TW4-5 0'110 13 12Ll'»:-3K;}Y-TW4-18 DIi';\6 16 137.5 OqS'\_i'-Po.)).-dJ-Cf\TW4-Z1 6542 200 125 II 17 -.9,1 fl.
TW4.6 ()~>;9,120 100 \'l>"q-"R
/]./L/TW4-15 /'f20 410 7S.3/;DNP,continuous pumping well
W4-1O (}11~1200 113 II.\'Y\_\0 R
..Q!iI2.TW4-11 980 100
(j'1,3k TW4-7 1400 121-TW4-1 1500 III 111:>3 -11<.ot%
IZ"~I MW4 11f()()1800 JI.33 DNP,continuous pumping well.1:1-;26"01.
.016';''1 TW4-4 1800 114.5 1157 -Y R,
~TW4-22 730 115 13()).-Xl.1(
o~~5 TW4-2 2800 121.13 I~";)"~R.
1'2'J~TW4-19 !5Ji"U 990 IS.57;)DNP,continuous pumping well.
(2.It.(TW4-20 r J32,5"6800 hKS![DNP,continuous pumping well.
/2'rl-'C!/TW4-60 D.1.Blank ,1000
TW4-63 Rinsate
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WJJ1HII!'lI'lE lM!11m.&WAl\lJ1iIJM lliiHU.
Jli1lIElL1ID 1IDh-'JI'h-W<1JJl!Iillffil!lllfJ:]}j)'JI']ji'(Q)~«i1JlR<1JJ1URlJI)J WA'1I'lEllRJ)esc~ilpin!llli illfSIlJ.1iWplu®g JE!v@nl!:"in,Q"e-ckc··Chl.rP'\4<M
iI,,~.~p'l~f '..'"...,
lLur-aIRGll.(we!!Hn_)'1yJel -£0 .N~ii'Mriildin!iii!iaiB---r:nt,«}),II,A..1 ,'T-!J
lJ
Dale anlo1 'J!'im.~e for lI'!Ilrgiilg 12r \7-oq IIil1ld SIll)J1l'llrdg (ift.IIiffeKeiit)_
•(.'<,''.,,-:,,;.)1-'",,:,,'.."';,,~.··;'_\:',::>~.L;).i;\;?(
WeiR J:"Mi1!i~g lEllll@iW 1Ufiem:_\1~iin'~Uf _IMi~er W~!pP;Mmjtl (ifolller@mUllBerulet)_
'.'j
.'
(:::--,
.:.''.........'.;',:'i.,.-,
','j,!:.
;.,~~~~Jlrl,\(~:.1 ,T':'.m::§l7.";3D-b':Ci*:""S:~-,,!';;";-;7.i(;\.!i;:/';";i::··
lI'f~Y,f,~~"~;~~jJ,l!ii,¢~ii\'..?l)1AApli!j~,JiJ:V~!ll,·.....'.......,..(-,....
?ll!?~~,~(~~·1;~;-':;;::;..H:Q,,::c c',:;··"···
Tulbidi~y.D=-,..-'-__
remjietlllUre )0 .iQ
3 r3Rs;dolt Potential (E11)--",,,-,,t>~-_
rj~t&.:i;i1$,;~*j~n~«~!'~i\1i?iJf:'j;,"',·:'.',.'','..
Coilid'ulli!JliiJe·,·,:j'K ...,c,,','•.
,.,""'>i .'"':',',.,.,':')".,"';"'."
pHe...',-,--_~....:'"1_.8__4 _
'fenlfmtilillwe ,i 0 '0&.•(,-.,-...:;',:':'"";',,""'<"..,".,..'~'
aooOltPilt¢Il,1liitfuiY·;'·'·Ss,";;(":.-~.,-'."',":".:.:--"'.)',',,."':;:',~..:.,":''"
Turbldil,V_..,...-_--"'O'--_
Ti1lW;..,...-.,.-__Gat Purg'¥!'-:-_time:_---GaI.PUrged,----
COllducmllce COmlluctal1Ctl'--__...,-_
IllH'..",-''--_pI'II,------------
TelJljfJeml1Rre,;..·_·-_•..,-------
Reuu)[Potenlial (llli)_llMllOlr Ji'6leiltial (Eu),._
Mill-i1:lil!fwlJiwnwrJl)k!cl!C;·gtl lI'6.rnllilQ:JjV~lldvroira Mmlit<r,xiflg
QooIi'JI AJJGMrIJRCCPloo((!ilJP')
KMte:H.17.0Ii l:lellis;'Jm:I
JFillDW P""J:e (Q]I,iJIi fli[plil.
Stili!}""=,---~_~_.._-'---'-'-'-
I1Jl'woll e"",,!>.a~I"alIylll~nG,llilf!lJ!ber Iifg~i~i!~'eiYJ\E~~~,":.iIS!:+:-"--""~_-'-__-'-_
l\lUIDlt8 "fCeKllIiiedAlIa1yl;vmJ lLalJPK!JfIOk'fDt:9~~·,\jf~~!~~~¥gYJti~iis.'""...;.!!'",':P",''''''S'."".ss.:.......
';':i.,.\..'
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....
tClIiiliill1BJ!!'S /\rr',,,,,\..i.~---..k,);,,,)r 0,<]!;,.O.c..::::k,,!jf£..JJolLLL......f2'...c~Ct,.I·trn_.,.?.0.!!'.\.)±.'l0_~_"'72.s'!~:L,,~--d"',,2c:L~~.--9~~!?';;FC~~>1~h:{~~H,~td:.:~Jl_,J:'!'!,.t-m,.._."~:;.l:'l.J~.f2l.:0!:-,,_~.
.,_...B(.L..'>\l:w,£'"i..--Ci.L...l9.2k)..,._.J"."h_.J"'i,.,0~..l.oh..0....___
c)··r
Mm -G1am1dvvv.u6&'JDJJisd~fW;;1?effLWl:
Gm'!Jmdtf'J~~!f l\&Gillf~{J,gQb~g
QuaRuw A'St!iiBUCe fl."(QJl!")
iI\.'jl']['.Il.g;~111L~
'I:IIIiRDI1I'JE IMl!E§!i>.!ill<1Al1iIf[J]Mj OOHJL.JL
)J1TIIFJL]j])JlJJiI\.'lI'A 'I:IIIilJJJ!"JIffiJBIJEiE'JI'Jli'QJ)JJ;(~ilJJ1iJl\lIDl WITil\.1f1EJreJ!}BEc,jjl~gmJi @f Sa"1mpii~g JEve1l1~:lfTh Q"<JA~.'Ch IQrlwrM
.,.~lliilp.i"r ,...JLuca~imD (wdD il~i!W)1WL.l -bS Nmi~e Iill&Jm/tia!s "1:.~Mr 1~.11 ;Ja~/K<'J'/\Poc1mor
Date mull Tome for 1l'w"g~lg 1;),-)(,-D'l 8lil(l S8'!'1pliilg {if <lIiffen-e!lt)-----
Weinll'i!i)gi~g13'l1i1BPIrJseill:'.:h.i!¥~i1m1'or_baiiertWJil'~~inJP (ifo!!ier ~ilUffil Jl]elllle!)()S12
SllII'Ijliiilg lEvelit Lj11,Q""A.--cblo$O"'ll'!":'V,i"'o/Q)t~~!!,Ipl,elR,i~!S>ll!lJllint;JEven.t ,.'""h~)
OQ7"Specific Conduclance 1 l IlMHOSlcm,.Y~el,!;~#gtll'":,,::".....J3.:JJi:,,,'".,
Del'll!!o Water IDefoteJllil,gillg_7_7:.......'1.'-'3:......._C~si.og Voltime (V)4"Well.:-..\(.653h)
CW(jlliltiilli~i(&~ti'i',;'/.",.,.,.(.%7~!)
Temp~~tu.~-,,//'-
"";/;
Red()J[?o;i!¢l!ij~'~iii,.,.,c._:......._
~/./
Turbidily...,/_/_
Time;'--,-,--__G~1.Purgoo _
Conductallce~7"~_
,""
pH~__--;o-''-/_'------
Temp~~\\to!~_
RedOJ(POI:eIl!iaD {Eh)_
"0 'At>I;cccte
/',<TellipetattJJ:e,--,-"::-/_
,/
Rei\0l(~ot€~tial(Eli)--
//Ttlibidily _
Time:Ga!.Purged~_
Comlv,ctance _
I'H ---",...,;;.._
/."-~/
Tempel'llttli"C::../_
/'
RedoxPo!eutial (E1l)_
Milll-GmilJ:ciIW.1eflIli,ofu.'B"J1'e"ii!!i{
[llIlUi1.~wcter lVlmutmllJg
Q~pJity A""~rattce]!l"ij (QAl")
r~!'<!IirJ!ji)f_-======-_----'lI'!ir~itlli8y_'_
.."-.'.,'-;",
'Jl'i~!f'll6:'iOOUJmle tw@ ~~Gfumg 1IO!11lljle&(2V)
'Jr =-2V1Q =-.".3:">I t\i0 ..
NOJ)[,;'beK@f cMinlg vo!@!i<i5sevi1cl1J1ljioo1(ii'o'lliettlnlillfuto).'•.-'-~-'-,-_
JfJfweEl eVllowte<l to drynenG,llIumber "fglli!t~ev"i;;l~~JI",''';",'_--'--:...=-------
Name ofCeffiifloo A.l1alyticfllllLnbofllWtyi(Q~n';r',\jji@'ili~~~wibr Jr,mliii-C,',..;".•.c..:....':....---
,,
..,',:....,'.':."
ll"Jr€Gerewma.ijw®AalWIcq!
.@ii:1l~"'.'."",""'.'.
1[N
11'"N····'·
I!fnpmm,roalive ici'~s".d;
SJ.ll;t:l!Y 'li)i'.~R';~~,.
Quantity ofll"~eg,,\i"!live:
N
N
1t'N'
I]{!ner (Sj1~ify)
Ghlor,lc
--_.--_.
___-l -L L-.....L""-----
Co"weilta ._
-""-~~'~:~.c~:·-'~'--"-~----O--~~-T-\..-~·--~---··,---'~-'''---'''~'-·------~-7;'----,b ...._·-J-::;·.._-r.::-c--'·-fl::Ty-::::::-1-9-·--·,,·---------r-'·--cA17\cJJdAl,c---C;l-\f--·-.,-'-<7"="--,----:,'-:/-..".-----.",,·-"""------""--..---·"i""------",,·-----,,·--·..·,,-,,·------·....·c~-,..---..-..--.."..-
n._.~'.~"~..._."_~•._.••.__•._.,,••__'__~_..r~'~n~.._'"'._~_.•_.__u ~~~_··>~.~_~~·~,.~~"._._·....~.·."~,,..•-...
l'v1fm -([]If'JU~'lfJlw[je6:t JD1kchflrge JPiBKFif~H
GfHtilW'lWl1tl3!T MOIDri~llrnng
Q"o!ifY P"s~ram;e J!'!~n (Q.41P)
Dell,\;:2,25.07 JI;:evnsim1.:2:
A'lIjI'AiC'lBUVJ!JEN'JI']
ilmJl'J1'JE _§A lUlIRAl\11IIIJ1MT JWITILU.
1U1IIn:JLJ1»IDJA'Jl'A \%'ilJJJl@[§JHIl1);!E']['JFilJJl&is ilJ)1IJ1.1lIfj)\%'A'lrJEJE
Desc1ip~fiol!wfSmmpfi@g13ver~1:~n,L--ala,'"
"Salllpler
lLucatioil (well!l!!r..e)'-rwy -7().N~~~~ildi il,itia!s I:"rr \1.Jd~,R(\o/I.~1J'w-
Dnte nno1 Time for lPurgi!lg E -2-[-0'1 nml SllJIapliJrg (ifdiiffeL!eilt)\d.~;;;Lq -0~
Wen Ji"MrgJi~g lEllJirtll~1[Jseil1:);..!imiip or_bailer Wei!J!'v.lI1Ji'(if otller !lIUIDl Ele11l1e!)(,q.v"\.£is
C''':",-;
',,'
pH:~~fer4,O,_'__~'----'--L--'-1~.0,-:--,-+--,-,__
WelH}~!,lll 1,?-l-13,...•.•.••..,./.;;-.•,.""..~.,-'0~..7"',.i".~"---'~~-
.,',,,:,"\..;",
Well Warer'feml'.(avg),~
pHBllffsr 7.1)7.D
Specific COilducllll1ce qq 7 uMHOS/cill
JDeplb 10 Wnw,BeforelP\lming (,'/).'3'1 Casing Volume (V)4"Well:'~'1."13 {.653h}
QJlt'dOlccl,,~~:(iivg)~'".~_'___-'---'--_'__~.i~,~~!~~~~r,~~~~~,iH W~II:...•.(.367h)
·R@Ili'iiili?rittlt:,.'Il)··'·tilibid·11.'}"-:"':'i·"'i:·i~'f",--.·-......y---
W~lIlfll'Co!ld.MI\7.~Clt",,\.Lcvu Err!'!Alllb.T~llIi';~~i~l'(g~llIl1I:i!iilgeVe!it)'-::2 ~,
':...'"',,-c,.\""..-.<:,,0..',',,"
Condlich,llce'_-,-__..,......_
pH'--_'""".pIl'---"--'--'----_
'femperature,"'7,.-,-_-,-_,..-_
RedoxPo~l)!ial (13u),,,,,._
Turbidity _
'femperaturec......_
Redorr Porenlial {Eh),_
Turbidity _
Time:Gal.PUI-geil1L..._Time:GaI.PUI-gcd~_
CondlIcl!unce _Condiucmllce,_
pH _pHL _
Temperalw.r.:,_'femperawrc'--_
..
""
',:....,_."
.Mf1il!-«1-"GUfr~ViflltelIDj£du;tge lP'e1([lijt
Qrooudw8w!MoJJitlllTng
QlwRi€)'ABs"'n11Ce il'k~(QAI!')
]!)ate:H.17.1l6 lwvinioii>:I
'JI'€lwirlli1Ji:__-------_lI'Wibiruily '_
flow W!)J:e (IQ),iiII gffllil·I'
S/6lJi==·..ICIo"--_
'Il'Jim~1D evnc"ale fiw!J c~D~,volumes (2V)
T=2V1Q-"II M,I)
N€liDlllOF Df cllllir"g volume.evacruited (iIi'lither illutiitWo),.;.'_'''--_-'--,.--_
Ifwell eva"",,~to li!:yneDs,number ofg~Uol.ise1iacuii'ti;Il"',,'--_-'-__~_
Name of Certified Anlllyticall LalJoralory itOil~ei;'fllli~·En&~yLab&._'_''----
VOCs "
AiR d&ie{'Nin!-
P.adiolo·CD
Other (specn,,)
Lbl()f~1-
Y'N
N
"'Z5Gmi
lli\Inlll~OO
(.Biirele)
lI',\2lle.,,,,,auv,,A<Iildellil
("i~i:Il,,)",'.
Y'N
Y N
:Drapmsenrat8.ve Jis'uned~
spoony'J.'yis"a,nd
Quantity ofP¢Ire!Villive:
'-L __---.1 L-J~=====_'
TabC
Depth to Water Sheets
Depth to VVater
.-
140~MW-4 7i,71 Flow L \G-PMI
Meter 0379.'II',
I~Lfj TW4-15 7'6 74 Flow r::.'7 G-.PM
Meter 017"',170
.'
ISr:,1 TW4-19 ~L!,qg Flow 7<C\6[>1--\
Meter 0),Li 36.3()
j40:d.,TW4-20 (0'\5 'is I Flow ~Cj G-ptJ\
Meter o7\tJc'i.{)
Water:,;),59066
Depth to VVa~er
-=
12 2S~MW-4 'fl,"I"r Flow fIlo+r ~~,~",j JL.-h~"
Meter 3"1-1q:)o
17-10 TW4-15 71'-/,;;-}Flow run+-~~.J-kr.-Ln.~_.
Meter 1++"'(0 ,:>
-
I 7(5'TW4-19 (sA,S'?Flow NoJ-~~l-lL,_L -.
Meter A;;"/{)
17 7-TW4-20 YO.7-Y Flow N"./..r.~~"'-A-.J-+"-r 1,-.
Meter 7-77 fib G)
Water:.:7-bS,/'U'
Depth '~o Water
D<dt@JJ,,:..2P:..fLZ._.rmmH~j?(1,l'L .__._.__
--~=-~."......=='
)¥I 'i MW-4 7/..6Lj Flow tf,t [,IrA
Meter .Jn '(t()
I'!/()TW4-15 75('6S-Flow ~.J L1PN\
Meter I x <'iJ7 !J
/1;;z,1 TW4-19 I.'J,'6.2-Flow %.2 ~f1/11
Meter 2 7(,,U{J
11/0>TW4-20 b1.(}lj Flow S,/1.1;11
.Meter 11?Y{}()
Water:1 "l{}3c;7
(
(
Depth to VV81l(er
mmH~L.fa~3A,_
Depth CQlmmelfi]b~;
1DJ<1l~®.J.0..2j...1i._""""
lime We~~-=
!'lor MW-4 -:f I.'is r:;'\Flow tj 3 G-rth1,
Meter 31541.2/)
!!/dS~TW4-15 "1~:?L/1\Flow l,/&tllvl
Meter I&'l//}/)
JlUs<TW4-19 1,/k7 Flow 'if.rJ ({,/(/1
Meter 79,,;",/Lf;)
;till.TW4-20 £7.02IT Flow 3.0-&ftvl
Meter 797<:-:7/)
Water:11 Y/14f{?
(
Chllorofonn VVe~~§
~81fr®-10i~Ql2.btOq mm!'~(?J __",b~~Q.f?_.____.
'Jum@ W®J~~/Dl!hQ)tt~C(Q)uTI1l mglJ Il"ll t~~
~MW-4 7!.Q,
O~:J.I.J TW4-1 IOt.3':>
0\51'1 TW4-2 (;,$).41
O'i>t5 TW4-3 I·Hs.q
()1\A1$TW4-4 b3.f,5
Of}/:?,TW4-5 .55.'-1'-1
()lSA'I TW4-6 1/."/1
oif;)./TW4-7 G,g./7
C>~:?."TW4-8 b7.Q$
()~!'i TW4-9 53·']
oiSq TW4-10 fiG>0 is
U'ij"IOj TW4-11 55 J -l5
oS'?>,"!TW4-12 '?>K .'is
0\\3.!'>TW4-13 Y.3·~q
<:ll$37 TW4-14 ~q.1 15
Q8'i~TW4-15 lSl.~3
08%TW4-16 b~.'l'1
()gYl-/TW4-17 1'1.0'1
Cl1l5'!TW4-18 bC.S3
0'100 TW4-19 fSS.'5;2-
o\S'OIS TW4-20 &>7.7'-/
Clli'S5 TW4-21 5lS.o~
Q~Or,TW4-22 Sb .'-16
01{"1 {TW4-23 /0(2 .If'-l
()~()?>TW4-24 llb.;Q
()~50 TW4-25 liS .t;,"!
Depth to Water
Daft@JL..:u()()i mmH!L~)7&L~_
-".
fJ;,7..MW-4 f(l~1 Flow If.//..:,/fl1 NaJA I~,.
Meter I.JJI:?-1'7)J-dN v'
IY/sJ(TW4-15 >;:X,erf(Flow ~,2 L--rfJytI{
.~'[·"llk:;;.Meter /<:.?t..(rJ ()
7 T
iils TW4-19 /;S.3,2 Flow '1'.7-G"7tf/1 laMeter33Jf1lf()1'AA ..r:.,~
!IJil.TW4-20 ;;r.Iff Flow 3.(&rtfll
Meter f(-/J2 c,2..()
H2.rt Water:121~'"[5/)'
Depth to Wa~er
lJJalft®JLJ.JtJrJ t mmli~L ~211.._<6~-'-----_
IDm®w®~~!!)®lPltfrll C(Q)mm®ll'1Itts'"""--'".,...,
jI('fO MW-4 7S.J?3 How
Meter W&3(,6
,H /.,TW4-15 '3/./)1 Flow
.".uv 4..11 Meter (C1h(J.l..()
v {
/1f1'J TW4-19 b3.fb Flow
Meter SbJEf[l'cJ
1Y'f5 TW4-20 73 ..5'1 Flow
Meter 'X'1JJ1o()t,()
Water::111 t"<1
Depth to V\tater
'D'aKe.:.ll:....!..I:L.Jild.L mmlHl((L_..(,--2L3t-f__.
Time We~~1Di~())~~tCli)mmefi'1l~$","'"<=n<J..==-
U,z::9 MW-4 7/:J 1/Flow ~.'7 /;JM
Meter L(/33!)()~
fii02.TW4-15 ::;.<::•/i I Flow b·"<{-rPtl1
Meter :7/)/):;L,J /]
/1(I t/TW4-19 /'3.~'7 Flow ;7.9 (-r;?rv1
Meter 313%t.f1f
/L;i1 TW4-20 '11 S I Flow 2.(.&rIM
Meter 'XloS"/,/)'
Water:30~101
Depth to 'Nater
/j(,A P
-,-
III i 0 MW·4 &'6\~tN Flow ;lIkkr ""Grok'o ",,:1\Rcolucc
Meter ali;.).o 1'''-.,(,
/yos TW4-15 7'1 T~Flow S.)(G·ptJ\
Meter O;)OS4IU
IS?;>(,TW4-19 (;'-153 Flow 7 G-P;'-'l
Meter NI36t.;SO
/35;;l..TW4-20 g:q.(}!Flow 1S G-PIV\
Meter o 'is IS\(,()
Water:~OJ,(,7X
Chloroform 'NeIls
'/>,1->
bS,J.'2>
77i'?>
6771
.Sbd-L(
SZ<C(lS
:>lsLI[
(,,35:;1..
5\0),(.0
71,'-I(
9-1.1S"
t11/
sq,'?:>7
SS.$
b~7'\
lDaft®Jl.3.fJ..:2/l1L._
"IrDm®W®fl~=ouo::o=
1201 MW-4
1;;30 TW4-1
1';:>3 TW4-2,
1'l)'JO TW4-3
1',33'6 TW4-4
n,M TW4-5
I'??,cl TW4-6
rs:)S TW4-7
1:)32,TW4-8
13?,i\TW4-9
12,).1 TW4-10
-1:>?:J.i TW4-11
\",'=\;).TW4-12
1',>,13 TW4-13
\"?:>l:\'S TW4,·14
'Up TW4-15
IliOL TW4-16
L)SCj TW4-17
131&TW4-18
/((;0 TW4-19
,i22()TW4-20
j'?X1 TW4-21
\:'>p TW4-22
\3S\TW4-23
~TW4-24
i'~o7 TW4-25
(Depth to VVater
J))ZJ~@...1l:.'3.o -og __mmH~?L~J,·:::'l..r .to ..
"""',--
1;;2.:::'\MW-4 7').u-Q Flow l,\G.PfI.\-=Meter Q;f!Joo (,76g]
I).;:J.(",TW4-15 g:".'lS Flow 56 G-PM
,,""onc;\«t-71,;."Meter ;).100,(')
V'J Dept"
I\.OD TW4-19 717~Flow G S &PM."
Meter yg7bd-O
jJJO TW4-20 G/l.q I Flow -i.5 <i-Pf'1
Meter '1.1 Q3C.(j
Water:3077;),\
Depth to \/Vater
.~~-~.~
\41S MW-4 7().L-J9 Flow l.j dP-N\
Meter 1fJi'!6 I~Z>Q
1'-1 Dq TW4-15 ]1.f.C{j Flow b.q 6'-ell/)
Meter ).1 L~7DD
roDS TW4-19 b5·0(Flow (;L1 (.f\;VI
Meter osI &,\{&-D.
l'iP9 TW4-20 11·M Flow ;)".~Gf'/v{
Meter g)..")&,;)J)
Water:31 0 0[5
(
Depth to Water
mmHg G21.6J _
Depth Comments
Date IJ -I f Mat,
T~me We!!-
I,-s14.()MW-4 ;;l1.3?Flow 3.r !.-tPnII
Meter !JIi ,J>:'JIJfiji(;JIF,D-.,.""-"
Ijiitil{TW4-15 753/.Flow 'I 0 ra fJf1I{
Meter '}J~'tj/)!J
I/S35 TW4-19 t'5".SO Flow 9':/bft11
Meter ,L;;~l-fl./2(')/)
/3/0 TW4-20 73.51 Flow 2.I.{L-rflV\.
Meter X'27t.'1//
Water:I:-i,l J./4 ?:L
(
Date i9--:;:O-oq
Time Weii
Depth to Water
Comments
b'i~14 MW-4 /0 h,'Flow LJ.Y (,.p;Vj. I
Meter /j ><'')/'
Oq I Cj TW4-15 gil \<Flow ~.(,u>fli
,-""",1 ,,!-"',',Meter 00!.j 1(,0
","J thDet>t
Oq<.jS TW4-19 (;,.1r.:..Flow b.1f (;.pl0\
Meter r.::nJf.,()
Oqd-.G\TW4-20 (,8 04 Flow ~.8"Go P!'1
Meter !5'3Xl3(\
Water:YI~ot::s
Depth to Water
mmHg bd,D).(,3
Depth Comments
Date 0-;;2,q-Oq
Time We~~
I:,S~MW-4 71~~Flow ~W'lJ\
Meter 3S'V)
j?i,;h.TW4-15 _.,(,,.."Flow S75 G'I'pli.-0 ....
Meter ''0..'/"1'i..\Ck.,,:"<-":')'.'-'"
\3i\TW4-19 t,:,qg'-!Flow s;)&PtIJ\
Meter (,3SSCJU
13S'1 TW4-20 bfS L(,Flow ;:;2.4 &PJ'I\
Meter '-6.":)(,33 ZJ
Water:~~dgS
,
\.
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
HYDRO
GEO
CHEM, INC.APPROVED DATE REFERENCE FIGURE
SCALE IN FEET
0 300150
( buried line )Tank
Holding
Waste
Lab
5537
5576
5547
5557
5557
5583
5550
5585
5537
5553 5554
5583
5578
5565
5586
5571
5524
5549
5559
5548
55845548
5561
5580
5574
5541
5569
5599
5614
5600
5603
5607
5603
5606
5559
5600
55515553
MW-25
MW-27
MW-31
TW4-1
TW4-2
TW4-3
TW4-4
TW4-5
TW4-6
TW4-7 TW4-8
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 4th QUARTER, 2009 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
TW4-4
5550
MW-32
5548
EXPLANATION
estimated capture zone
boundary stream tubes
resulting from pumping
NOTE: MW-4, MW-26, TW4-19, and TW4-20 are pumping wells
SJS H:/718000/feb10/wl1209cz.srf
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
AND ESTIMATED CAPTURE ZONES
WHITE MESA SITE
H:/718000/feb10/wl1209cz2.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, TW4-19, and TW4-20 are pumping wells)
estimated capture zone
boundary stream tubes
resulting from pumping
HYDRO
GEO
CHEM, INC.APPROVED DATE REFERENCE FIGURE
3332
3000
SCALE IN FEET
0
5581
5503
5471
5502
5520
5501
5494
5493
5498
5586
5604
5447
5450
5496
5507
5537
5576
5542
5512
5537
5546 5557
5556
5583
5550
5584
5537
5583
5577
5564
5586
5570
5524
5545
5558
5548
558455615558
5579
5573
5592
5614
5601
5541
5539
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
5550
5553 5553MW-04
5541
5566
5588
TW4-23
TW4-24
TW4-25
(anomalous)
MW-22
PIEZ-1
5450
5592
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
5546
temporary perched monitoring well
showing elevation in feet amsl
5573
perched monitoring well installed April, 2005
showing elevation in feet amsl KRIGED 3rd QUARTER, 2009 WATER LEVELS
WHITE MESA SITE
H:/718000/nov09/wl0909.srf
EXPLANATION
temporary perched monitoring well installed
May, 2007 showing approximate elevation
in feet amsl
5541
NOTES: Locations and elevations for TW4-23, TW4-24, and TW4-25 are approximate
SJS
50.0
60.0
70.0
80.0
09
/
2
5
/
7
9
06
/
1
7
/
8
0
09
/
0
1
/
8
4
09
/
0
1
/
8
5
03
/
0
1
/
8
6
02
/
2
0
/
8
7
01
/
2
6
/
8
8
03
/
0
9
/
8
9
02
/
1
6
/
9
0
02
/
2
7
/
9
1
03
/
1
7
/
9
2
03
/
2
4
/
9
3
03
/
2
4
/
9
4
03
/
1
6
/
9
5
03
/
2
8
/
9
6
04
/
0
7
/
9
9
01
/
0
3
/
0
0
05
/
1
5
/
0
0
06
/
2
6
/
0
0
07
/
2
5
/
0
0
08
/
3
1
/
0
0
09
/
2
9
/
0
0
10
/
2
3
/
0
0
11
/
3
0
/
0
0
03
/
2
9
/
0
1
07
/
1
0
/
0
1
11
/
0
8
/
0
1
03
/
2
6
/
0
2
07
/
0
8
/
0
2
11
/
2
2
/
0
2
03
/
2
6
/
0
3
07
/
0
7
/
0
3
11
/
0
7
/
0
3
03
/
2
8
/
0
4
07
/
2
8
/
0
4
11
/
1
6
/
0
4
03
/
1
5
/
0
5
07
/
2
9
/
0
5
03
/
0
8
/
0
6
02
/
2
7
/
0
7
03
/
2
6
/
0
8
03
/
0
3
/
0
9
MW‐4 Water Depth Over Time (ft blmp)
50.0
60.0
70.0
80.0
90.0
100.0
110.0
120.0
09
/
2
5
/
7
9
06
/
1
7
/
8
0
09
/
0
1
/
8
4
09
/
0
1
/
8
5
03
/
0
1
/
8
6
02
/
2
0
/
8
7
01
/
2
6
/
8
8
03
/
0
9
/
8
9
02
/
1
6
/
9
0
02
/
2
7
/
9
1
03
/
1
7
/
9
2
03
/
2
4
/
9
3
03
/
2
4
/
9
4
03
/
1
6
/
9
5
03
/
2
8
/
9
6
04
/
0
7
/
9
9
01
/
0
3
/
0
0
05
/
1
5
/
0
0
06
/
2
6
/
0
0
07
/
2
5
/
0
0
08
/
3
1
/
0
0
09
/
2
9
/
0
0
10
/
2
3
/
0
0
11
/
3
0
/
0
0
03
/
2
9
/
0
1
07
/
1
0
/
0
1
11
/
0
8
/
0
1
03
/
2
6
/
0
2
07
/
0
8
/
0
2
11
/
2
2
/
0
2
03
/
2
6
/
0
3
07
/
0
7
/
0
3
11
/
0
7
/
0
3
03
/
2
8
/
0
4
07
/
2
8
/
0
4
11
/
1
6
/
0
4
03
/
1
5
/
0
5
07
/
2
9
/
0
5
03
/
0
8
/
0
6
02
/
2
7
/
0
7
03
/
2
6
/
0
8
03
/
0
3
/
0
9
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
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
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
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
uri
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
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
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
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
(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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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)
20
/
9
9
20
/
0
0
20
/
0
0
20
/
0
1
20
/
0
1
20
/
0
2
20
/
0
2
20
/
0
3
20
/
0
3
20
/
0
4
20
/
0
4
20
/
0
5
20
/
0
5
20
/
0
6
20
/
0
6
20
/
0
7
20
/
0
7
20
/
0
8
20
/
0
8
20
/
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
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
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
TW4‐9 Water Level Over Time (ft. blmp)
50.0
52.0
54.0
56.0
58.0
60.0
62.0
64.0
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
TW4‐18 Water Level Over Time (ft. blmp)
02 02 03 03 03 03 04 04 04 04 05 05 05 05 06 06 06 06 07 07 07 07 08 08 08 08 09 09 09 09
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
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
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
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
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
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
TW4‐19 Water Level Over Time (ft. blmp)
05 05 06 06 06 06 07 07 07 07 08 08 08 08 09 09 09 09
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
TW4‐20 Water Level Over Time (ft. blmp)
45.0
55.0
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
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
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
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
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
TW4‐20 Water Level Over Time (ft. blmp)
5 6 7 8 9
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
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
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
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
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
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
TW4‐21 Water Level Over Time (ft. blmp)
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
Mea
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐22 Water Depth Over Time
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
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
eas
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐23 Water Depth Over Time
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
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
55.40
55.60
55.80
56.00
56.20
56.40
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
ea
s
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐24 Water Depth Over Time
55.40
55.60
55.80
56.00
56.20
56.40
56.60
56.80
57.00
57.20
57.40
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
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
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
eas
u
r
i
n
g
 Po
i
n
t
 (f
t
.
)
TW4‐25 Water Depth Over Time
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
5,550.58 2/27/2007 80.28
5,563.60 5/2/2007 78.95
5,555.85 8/14/2007 65.93
5,569.10 10/10/2007 73.68
5,560.00 3/26/2008 60.43
5,539.64 6/25/2008 69.53
5,539.51 8/26/2008 89.89
5,553.00 10/14/2008 90.02
5,534.18 3/3/2009 76.53
5,558.39 6/24/2009 95.35
5,560.99 9/10/2009 71.14
5,629.53 12/11/2009 68.54
Water Levels and Data over Time
White Mesa Mill - Well TW4-20
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
Water Levels and Data over Time
White Mesa Mill - Well TW4-21
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
,
Date Depth Elevation
09/13/2007 68.48 5539.12
10/10/2007 68.57 5539.04
11/30/2007 68.12 5539.49
12/11/2007 67.88 5539.73
01/08/2008 68.18 5539.43
02/18/2008 67.93 5539.68
03/26/2008 67.83 5539.78
04/23/2008 67.66 5539.95
05/30/2008 67.89 5539.72
06/24/2008 67.84 5539.77
07/16/2008 67.93 5539.68
08/26/2008 67.69 5539.92
09/10/2008 66.19 5541.42
10/14/2008 67.8 5539.81
11/26/2008 68.08 5539.53
12/29/2008 67.82 5539.79
01/26/2009 67.22 5540.39
02/24/2009 67.63 5539.98
03/06/2009 67.51 5540.10
04/07/2009 67.65 5539.96
05/29/2009 67.53 5540.08
06/30/2009 67.25 5540.36
07/31/2009 67.25 5540.36
08/31/2009 67.1 5540.51
09/10/2009 67.24 5540.37
12/11/2009 66 73 5540 37
Water Levels and Data over Time
White Mesa Mill - Well TW4-23
12/11/2009 66.73 5540.37
Date Depth Elevation
09/13/2007 57.22 5568.48
10/10/2007 57.30 5568.40
11/30/2007 56.67 5569.03
12/11/2007 56.53 5569.17
01/08/2008 56.80 5568.90
02/18/2008 56.61 5569.09
03/26/2008 56.40 5569.30
04/23/2008 56.15 5569.55
05/30/2008 56.31 5569.39
06/24/2008 56.49 5569.21
07/16/2008 56.55 5569.15
08/26/2008 56.49 5569.21
09/10/2008 56.6 5569.10
10/14/2008 56.71 5568.99
11/26/2008 56.88 5568.82
12/29/2008 56.91 5568.79
01/26/2009 56.18 5569.52
02/24/2009 56.52 5569.18
03/06/2009 56.46 5569.24
04/07/2009 56.62 5569.08
05/29/2009 56.6 5569.10
06/30/2009 56.41 5569.29
07/31/2009 56.45 5569.25
08/31/2009 56.35 5569.35
09/10/2009 56.55 5569.15
12/11/2009 56 19 5569 51
Water Levels and Data over Time
White Mesa Mill - Well TW4-24
12/11/2009 56.19 5569.51
Date Depth Elevation
09/13/2007 43.05 5601.86
10/10/2007 43.02 5601.89
11/30/2007 42.34 5602.57
12/11/2007 42.09 5602.82
01/08/2008 42.97 5601.94
02/18/2008 45.78 5599.13
03/26/2008 47.80 5597.11
04/23/2008 49.40 5595.51
05/30/2008 50.49 5594.42
06/24/2008 50.65 5594.26
07/16/2008 58.24 5586.67
08/26/2008 50.74 5594.17
09/10/2008 50.68 5594.23
10/14/2008 50.79 5594.12
11/26/2008 50.85 5594.06
12/29/2008 50.04 5594.87
01/26/2009 49.02 5595.89
02/24/2009 48.64 5596.27
03/06/2009 48.44 5596.47
04/07/2009 48.17 5596.74
05/29/2009 47.36 5597.55
06/30/2009 46.8 5598.11
07/31/2009 46.69 5598.22
08/31/2009 46.39 5598.52
09/10/2009 46.42 5598.49
12/11/2009 45 43 5599 48
Water Levels and Data over Time
White Mesa Mill - Well TW4-25
12/11/2009 45.43 5599.48
ENERGYLABORATO~-"S,INC••2393Sail Creek Highway (82601)•Ro.
TollFree 888.235.0515 •.235.0515 •Fax [phone] •casper@energy.
LABORATORY ANALYTICAL REPORT
.3258 •Casper,WY82602
"'om •www.energylab.com
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-002
MW-4
Report Date:01/06/10
Collection Date:12/14/09 14:00
DateReceived:12/18/09
Matrix:Aqueous
MCL!
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 44 mg/L 1 A4500-CI B 12/28/0911:031 ja
Nitrogen,Nitrate+Nitrite as N 5.8 mg/L 0.2 E353.2 12/28/09 13:251jal
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride 1.6 ug/L 1.0 SW8260B 12/22/0904:361jlr
Chloroform 1800 ug/L 100 SW8260B 12/21/0915:00 I jlr
Chloromethane ND ug/L 1.0 SW8260B 12/22/09 04:361jlr
Methylene chloride ND ug/L 1.0 SW8260B 12/22/0904:361jlr
Surr:Dibromofluoromethane 107 %REC 70-130 SW8260B 12/22/09 04:361jlr
Surr:p-Bromofluorobenzene 105 %REC 80-120 SW8260B 12/22/0904:361jlr
Surr:Toluene-dB 100 %REC 80-120 SW8260B 12/22/0904:361 jlr
Surr:1,2-Dlchlorobenzene-d4 111 %REC 80-120 SW8260B 12/22/09 04:361jlr
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel -Maximum contaminant level.
NO -Not detected at the reporting limit.
Additional Lab Results
ENERGVLABORATOFIIES,(NC.•2393SarrCleekHighway(8260()'Po.Box3258 .Caspel;WV826'02
70//Free 888JlJ5.0515 .307.28/i0515 .RiX 307.234.1639 'casper@81l8lgylab,com'WMI~ef}efgy/ab,com
ANALYTICAL SUMMARY REPORT
January 11,2010
Denison Mines (USA)Corp
6425 S Hwy 191
Blanding,UT 84511
Workorder No.:C09120896
Project Name:4th Quarter Chloroform
Quote ID:C2975·Chloroform Sampling
Energy Laboratories,Inc.received the following 14 sampies for Denison Mines (USA)Corp on 12/30/2009 for analysis.
Sample ID Client Sample 10 Collect Date Receive Date Matrix Test
C09120896-001 TW4-11R
C09120896-002 TW4·7R
12/28(09 08:20 12/30109 Aqueous Chloride
Nitrogen,Nitrate +Nitrile
SW8260B vacs,Standard List.._._-_.__.._--_.•..'"-""~"..-.-_-._.._--_.-.._-,.---~-_.,.-..,-,,,,.-_..._•.•.__.._....__._""",,.._---,...
12/28/09 10:00 12/30109 Aqueous Same As Above
Same As Above
Same As Above
Same As Above
C09120896-003 TW4·1R...-_._--_.
C09120896·004 TW4-4R
C09120896-005 TW4-22R
12/28/09 11:03 12/30109
12/28/09 11:57 12/30109
12/28109 13:02 12/30109
Aqueous ---Aqueous
Aqueous
...................____-_.._.._-__-_-.
C09120896·006 TW4-2R 12/28(0914:02 12/30109 Aqueous Same As Above
C09120896-007 TW4·70 12/29/09 08:25 12/30109 Aqueous Same As Above----___-_-___--____.._..
C09120896·008 TW4-11 12/29/0908:15 12/30109 Aqueous Same As Above
C09120896·009 TW4-7 12/29/09 08:36 12/30109 Aqueous Same As Above
Same As Above
Same As AboveAqueous
Aqueous
Aqueous
12/29/09 08:46 12/30109
12/29/0908:03 12/30109
..................................-_ _-___-_..__---_..--__---
12/29/09 08:54 12/30109
....._._----C09120896·010 TW4-1
C09120896-011 TW4-4-___---
C09120896-012 TW4·22--_._.._____-____.._._-.•-.---
C09120896-013 TW4-2 12/29/0908:25 12/30/09 Aqueous Same As Above
.........__..__-____..---C09120896-014 Trip Blank 12/29/09 00:00 12/30/09 Aqueous SW8260B vacs,Standard List
As appropriate,any exceptions or problems with the analyses are noted in the Laboratory Analytical Report,the
QAlQC Summary Report,or the Case Narrative.
ifyou have any questions regarding these tests results,please call.
Report Approved By:...&--<rha M;'P &.U )J)~
Stephanie D.Waldrop
Reporting Superviso~
ENERGYLABORATORIES,INC••2393SailCreek Highway (82601)'Po.Box8258 .Casper,WV82602
TollFree 888.235.0515 .307.235.0515 •Fax [phone] •casp6'/@eller9ylab.com·ww,v.ellergylab.com---__.___..__..
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120896·001
TW4-11R
Report Date:01111110
Collection Date:1212810908:20
DateReceived:12/30109
Matrix:Aqueous
Analyses Result Units Qualifier RL
MCU
QCL Method Analysis Date I By
ND ug/L
ND ug/L
ND ug/L
ND ug/L
103 %REC
108 %REC
104 %REC
107 %REC
MAJOR IONS
Chloride
Nitrogen,Nitrate+Nitrite as N
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
MethYlene chloride
Surf:Dibromofluoromethane
Sure p.Bromofluorobenzene
Surr:Toluene-dB
Surr;1,2-Dichlorobenzene-d4
NO
0.1
mg/L
mg/L
1 A4500-CI B 12/31/09 15:48/1jl
0.1 E353.2 01/05/1012:071 jal
1.0 SW8260B 01/04/1018:10I wen
1.0 SW8260B 01/04/10 18:10/wen
1.0 SW8260B 01/0411018:10 I wen
1.0 SW8260B 01/04f10 1B:10/wen
70-130 SW8260B 01/04/1018:10I wen
80-120 SW8260B 01/04/1018:10 I wen
80-120 SW8260B 01/04/1018:10 {wen
80-120 SW8260B 01/04/10 18:10I wen
Report
Definitions:
RL w Analyte reporting limit.
QCL ~Quality control limit.
Mel-Maximum contaminant level.
ND -Not detected at the reporting limit.
ENEI?GYLABORATORIES,INC.•2393sa/n'reek Highway (82601)'P.O.Box3258 .Caspel;WY82602
Tol/iree 888.235.0515 •307.235.0515 •Fax [phone] •casper@eller9y/ab.colII·ww",ellergy/ab.colII
----_--
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
ClientSample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120896..002
TW4..7R
Report Date:01/11/10
Collection Date:12/28/0910:00
DateReceived:12/30/09
Matrix:Aqueous
1 A4500·CI B 12/31/0915:5411jl
0.1 E353.2 01/05/10 12:09/ja!
1..0 SW8260B 01/04/10 18:50/wen
1..0 SW8260B 01/04/1018:50 I wen
1..0 SWB260B 01104/101B:50/wen
1..0 SW8260B 011041101B:501wen
70·130 SWB260B 01/041101B:501wen
80..120 SW8260B 01/04/10 18:50/wen
80..120 SWB260B 01/04/10 18:50/wen
80..120 SW8260B 01/04110 18:501wen
Analyses Result Units Qualifier
MAJOR IONS
Chloride ND mg/L
Nitrogen,Nitrate+Nitrite as N NO mg/L
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride ND ug/L
Chloroform 1.1 uglL
Chloromethane NO ug/L
Methylene chloride NO ug/L
Surr:Dibromofluoromethane 102 %REC
Surr;p-Bromofluorobenzene 109 %REC
Surr:Toluene-d8 105 %REC
Sure 1,2·Dichlorobenzene-d4 105 %REC
RL
MeL!
QCL Method Analysis Date I By
--~--______._-
Report
Definitions:
RL .Analyte reporting limit.
QCL .Quality control limit.
--_.._..........-
Mel-Maximum contaminant level.
NO -Not detected at the reporting limit.
VV'."';I.·'.'~.f;;.·'.;.F'''.'';;i'''f.,.;7Ff ENE.RGV LABORATORIES,IN('~023.938,1//Cleokliigilway(826YJI)•PO Box 3258 •CRsper,WV82M2Il{ji!f};j~~!/A\t.~l!/i;Y .Toill-ree 888235.0515 '807.235,0515 •Fax [phone],Q •oRsper@ellergylab,com •www.el701gylflb,com
~i!lJf _'__~'"__'''''''"'_'~""~'~_~"_"'_"_"'"~.__.._.·_..,·._"__.m ~·....·._.~"""·••__--------,,--........
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10.
Client Sample 10.
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120896-003
TW4-1R
Report Date:01/11/10
Collection Date:12/28109 11:03
DateReceived:12/30/09
Matrix:Aqueous
-.-._-~--_...__._-_...-...._----_._....----------------~_.,-_.
Analyses Result Units QualIfier RL
MAJOR IONS
Chloride ND mg/L 1
Nitrogen,Nitrate+Nitrite as N ND mg/L 0.1
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride ND ug/L 1.0
Chloroform 1.9 ug/L 1.0
Chloromethane ND ug/L 1.0
Methylene chloride ND uglL 1.0
Surr:Dibromofluoromethane 111 %REC 70-130
Surr:p-8romofluorobenzene 110 %REC 80-120
Surr:Toluene-dB 106 %REC 80-120
Surr:1,2-Dichlofobenzene-d4 107 %REC 80-120
MCL!
QCL Method
A4500~CI B
E353.2
SW8260B
SW8260B
SW8260B
SW8260B
SW8260B
SW8260B
SW8260B
SW8260B
Analysis Date 1By
12/31/0915.58/Ijl
01/05110 12.20/jal
01/04/1022:491 wen
01/04/1022:491 wen
01/04/10 22:49 I wen
01/04/10 22A91 wen
01/04/1022.491 wen
01/04/1022:491 well
0110411022.491 wen
01/04/1022:491 wen
Report
Definitions:
RL -Analyte reporting limit.
QCL ~Quality control limit.
--~.~-~
MCl ~Maximum contaminant level.
NO ~Not detected at the reporting limit.
ENERGVLAHORATVRlES,INC-"2393Sail CreekHighway (82601)"Po.BoxJ256 "Casper,WV82602
,70//Free 8fJ8235.0515 '307.28/):0515 'Fe7X 307.234,1639 .casper@energylab,com •wWI4~el7ergyMb.com
......._--_._-------
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Qualier Chloroform
C0912089G·004
TW4-4R
Report Date:01/11/10
Collectioll Date:12/28/0911:57
DateReceived:12/30/09
Matrix:Aqueous
Analyses Result Units
MAJOR IONS
Chloride ND mg/L
Nitrogen,Nilrale+Nitrite as N NO mg/L
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L
Chloroform 2.3 ug/L
Chloromethane NO ugfL
Metllylene cll10ride NO ug/L
Surr:Dibromofluoromethane 98.0 %REC
Surr:p-Bromofluorobenzene 110 %REC
Surr:Toluene-d8 105 %REC
Surr:1,2-Dichlorobenzene-d4 105 %REC
Qualifier RL
1
0.1
1.0
1.0
1.0
1.0
70-130
80-120
80-120
80·120
MCL!
QCL Method
A4500-CIB
E353.2
SW8260B
SW82608
SW8260B
SW8260B
SW8260B
SW8260B
SW8260B
SW8260B
Analysis Date I By
12/31/0916:00/1jl
01/05/1012:21/jal
01/04/10 23:28 Iwen
01/04/1023:28 I wen
01/04/10 23:28/wen
01/04/10 23:281 wen
01 I04f1 0 23:28 I wen
01/04/1023:281wen
01/04J10 23:28 I wen
01/04/1023:281 wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality controllimil.
Mel-Maximum contamInant level.
NO H Not detected at the reporting limit.
ENERGVLABORATOfllES,INC••23938,111 Creek IIigIlWHj'(82601)'P.O.Box 32.58 .Caspel;WI'82602
.7011Aeo888.235 0515 '307.235.0515 .FBX 307.234.1639 .casper@)ollorgy/ab.com'www.6.IJorg)llalJ.com--_._-_.__.._-_..._.._-_.__.......---------_....._..._.--_.._.
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample ID:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120896·005
TW4·22R
Report Date:01111110
Collection Date:12/28/0913:02
DateReceived:12/30/09
Matrix:Aqueous
Analyses Result Units Qualifier RL
MAJOR IONS
Chloride NO mg/L 1
Nitrogen,Nitrate+Nitrite as N NO mg/L 01
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1.0
Chloroform 2.8 ug/L 1.0
Chloromethane NO ug/L 1.0
Methylene chloride NO uglL 1.0
Surr:Dibromofluoromethane 103 %REC 70-130
Surf:p-Bromofluorobenzene 106 %REC 80-120
Surr:Toluene·d8 103 %REC 80·120
Sun:1,2~Dichlorobellzene·d4 105 %REC 80·120
MCU
QCL Method
A4500-Cl B
E353.2
SW8260B
SW8260B
SW8260B
SW8260B
SW8260B
SW8260B
SW8260B
SW8260B
Analysis Date I By
1213110916:0211jl
0110511012:241 jal
01/05/1000:08/wen
01/05/1000:08/wen
0110511000:081 wen
01/05/10 00:08 Iwen
01/05/10 00:08 Iwen
01/05/10 00:08/wen
01/05110 00:08 Iwen
01105/10 00:08 Iwen
Report
Definitions:
RL -Analyte reporting limit.
QCL .Quality control limit.
Mel -Maximum contaminant level.
NO -Not detected at the reporting limit
!/~;~T'!V,;;;?"JV"2i'f;)1 ENERGVLABORATORIES,INC_-2393 SHII Creek Highway (826'01)-eo.lJox3258 -Casper,WY826'02!j,~2fdb!.&:b.\~~%?l~f0Y TollFree 888.236,()515 .307.2350516 'Fax 307.234,1639 'casper(j}enelgy/ab.cofll'www,energylab,com
tl/f6f4.r4t/IYt£,o"!l.m .._...._.___..~__.".._o..__",~."_~•••_.,,__••__.
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120896-006
TW4-2R
Report Date:01/11/10
Collection Date:12/28/09 14:02
DateReceived:12/30109
Matrix:Aqueous
----.,.","........"----_..,,,'._...._.._---
MCL!
Analyses F~esult Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride ND mglL 1 A4500-CI B 121311091B:OB /Iii
Nitrogen,Nitrate+Nilrjte as N ND mg/L 0.1 E353.2 01/05/1012:27/ial
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride ND ug/L 1.0 SW8260B 01/05/1000:47 I wen
Chloroform 8.7 ug/L 1.0 SWB260B 01l0G/10 00:47 I wen
Chloromethane ND ug/L 1.0 SW82BOB 01/05/1000:47/wen
Methylene chloride NO ug/L 1.0 SW8260B 01/05/1000:47/wen
Surr:Dibromofluoromethane 103 %REC 70-130 SW82BOB 01/05/1000:47/wen
Surr:p-Bromofluorobenzene 107 %REC 80-120 SW8260B 01/05/1000A7/wen
Surr:Toluene-d8 104 %REC 80-120 SW8260B 01/05/10 00:47 Iwen
Surr:1,2·0ichlorobenzene-d4 107 %REC 80-120 SW8260B 01/05/1000:47/wen
Report
Definitions:
RL -Analyte reporting limit
QCL -Quality control limit.
Mel -Maximum contaminant level,
NO -Not detected at the reporting limit.
ENERGVLABORATORIES,INC.•23.93 Sail CleelrHigllway(82601)'P.O,Box3258 •Caspel;WV82602
Toll Free 888.2350515 •307.235.0515 •Fax 307.234,163g •casper@ellClgylab,com'www,ellergyiab,com
LABORATORY ANALYTICAL REPORT
Analyses Result Units
MAJOR IONS
Chloride 42 mg/L
Nitrogen,Nitrate+Nitrite as N 4.4 mg/L
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride 1,9 ug/L
Chloroform 2500 ug/L
Chloromethane ND ug/L
Methylene chloride ND ug/L
SUrf:Dibromofluoromethane 104 %REC
Surf:p·8romofluorobenzene 108 %REC
Sure Toluene-d8 105 %REC
Sure 1,2·Dichlorobent:ene·d4 105 %REC
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Cbloroform
C09120896·007
TW4-70
Report Date:01111110
Collection Date:12129/0908:25
DateReceived:12130109
Matrix:Aqueous
---~~------_.__._-
MCL!
Qualifier RL QCL Method Analysis Date I By
1 A4500-CI B 12/31/0916:10/1jl
0,2 E3532 01/05/10 12:29/jal
1,0 SW8260B 01/05/1001:271 wen
500 SW8260B 01/05/10 15:30/wen
1,0 SWB260B 01/05/10 01 :27 I wen
1.0 SWB260B 01/05/1001:27 I wen
70·130 SW8260B 01105/1001 :271 wen
80·120 SW8260B 01105/10 01:27 Iwen
80-120 SW8260B 01105/10 01 :27 I wen
80·120 SW8260B 01/0511001:27/wen
Report
Definitions:
RL ~Analyle reporting limit.
QCL ~Quality control limit.
Mel·Maximum contaminant level.
ND -Not detected at the reporting limit.
£N£RGVLIi/30RATORIES,INC.•2393 Sal/Cleekliigliway(8260/)'Po.Box3258 •C,7sper,WY82602
.Toll Free 888.2350515 '807.236:0.')15 .Fax [phone] .casper@enezqylab,com I wv/w.energylab.com_._.._--_..-__-----
LABORATORY ANALYTICAL REPORT
---_..._----_.._---
Client:
Project:
Lab ID:
Client Sample ID:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120896·008
TW4·11
Report Date:01/11/10
Collection Date:12/29/0908:15
DateReceived:12/30/09
Matrix:Aqueous
MCL!
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 46 mglL 1 A4500·CIB 12/31/0916:14/1j1
Nitrogen,Nitrate+Nitrite as N 6,6 mg/L 0.2 E353,2 01/08110 11 :01 /jal
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1.0 SW8260B 01/05/10 02:06/wen
Chloroform 860 ug/L 200 SW8260B 01/05110 16:09/wen
Chloromethane NO uglL 1.0 SW8260B 01/05/1002:06/wen
Methylene chloride NO ug/L 1.0 SW8260B 01/05/1002:06/wen
Surf:Dibromofluoromettlane 104 %REC 70·130 SW8260B 01/0511002:061 wen
Sure p-Bromofluorobenzene 107 %REC 80·120 SW8260B 01/05/1002:06/wen
Surr:Toluene-dB 104 %REC 80·120 SW8260B 01/05/1002:061 wen
Sure 1,2·Dichlorobenzene·d4 105 %REC 80·120 SW8260B 01/05/1002:06/wen
Report
Definitions:
Rl ~Analyte reporting limit.
QCL -Quality control limit.
MCl -Maximum contaminant level.
ND -Not detected at the reporting limit.
1"",,""",1'",,';;)';';;';77 ENERGVLABORATORIES,INC,"2393SailCreek lfighway (82601)"Ro.Box 3258 'Casper,WV82602l~%/}7!Jit!Ji:'ilifJ;tiifJ .7011Free 888.2350515 '307.235.0515 'Fax [phone] 'casper!!PenmgylalJ.com"vllmenelgylalJ.com
i!J!Af.l?*!dVdcUWii!
LABORATORY ANALYTICAL REPORT
Result Units
MAJOR IONS
Chloride
Nitrogen,Nitrate+Nitrite as N
Denison Mines (USA)Corp
4th Quarter Chioroform
C09120896-009
TW4-7
Client:
Project:
Lab 10:
Client Sample 10:
Analyses
VOI_ATILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Sure Dibromofluorometl1ane
Surr:p·Bromof!uorobenzene
Surr:Toluene-d8
Surr;1,2-Dichlorobenzene·d4
37 mg/L
4.2 mg/L
NO ug/L
1300 ug/L
NO uglL
ND ug/l
112 %REC
105 %REC
105 %REC
105 %REC
Report Date:01111/10
Collection Date:12/29/0908:36
DateReceived:12/30/09
Matrix:Aqueous
..".-......._-_._--_.~._.,..-...~_._------
MeL!
QuaHficr RL QCL Method Analysis Date f By
1 A4500-CI B 1213110916:17/1jl
0.2 E353.2 01/0B/l0 11 :03 /jal
1.0 SWB260B 01/05110 02:46/wen
200 SWB260B 01/05/10 16:47/wen
1.0 SWB260B 01/0511002:461 wen
1.0 SWB260B 01/05/1002:461 wen
70-130 SWB260B 01/05/1002:461 wen
BO-120 SWB260B 01/05/1002:46/w8n
BO-120 SWB260B 01/05110 02:46 Iwen
BO-120 SWB260B 01/0511002:461 wen
Report
Definitions:
Rl·Analyte reporting limit.
QCl·Quality control limit.
MCl"Maximum contaminant level.
NO -Not detected at the reporting limit
!r~.•I·.·:\.Wf;'.i;.CJ.CS.'.i2;TP7!ENERGYLAIJOI1A,OHlES,INC••2393SailOsekH/gliway(IJ261!/)'eo Box 32M'Caspel;WY8P.602/t&ifs:!ii.~~"}Sf:;~ttfJ};.To//Fl'eo888.23505t5 .307235.0515 'Fax [phone] 'casper@energy/ab.com'www.ollergy/ab.com
.ff@.Ii!§1@Jl~J.!:jii w_,__.•_~__.".•"m~'._.w,,_._
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab ID:
Client Sample ID:
Denison Mines (USA)Corp
41h Quarter Chloroform
C0912089G-010
TW4-1
RepOit Date:01111110
Collection Date:1212910908:46
DatoReceived:12130109
Matrix:Aqueous
.~.~,_...,-"..._--.
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 41 mg/1.1 A4500-CI B 1213110916:2111jl
Nitrogen,Nitrate+Nitrite as N 6.8 mg/L 0.2 1::353.2 01/0811011:06/jal
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride ND uglL 1.0 SW8260B 01/05/1003:26/wen
Chloroform 1400 ug/L 200 SW8260B 01/05110 17:251 wen
Chloromethane ND ug/L 1.0 SW8260B 01/05/1003:261 wen
Methylene chloride ND ug/L 1.0 SW8260B 01105/1003:261 wen
Sure Dibromofluoromethane 108 %REC 70-130 SW8260B 0110511003:261 wen
Surf:p~Bromofluorobenzene 106 %REC 80-120 SW8260B 0110511003:26/wen
Surr:Toluene-dB 105 %REC 80-120 SW8260B 01105/1003:26 I wen
Surr:1,2-Dichlorobenzene-d4 102 %REC 80-120 SW8260B 01105/10 03:261 wen
Report
Definitions:
RL ~Analyte reporting limit.
QCL ~Quality control limit
Mel·Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGVLABORATORIES,INC••2383 Sail Cree/riliglllvB)'(82801)'Po.Box 3258 .Casper,WV82602
.lNIFree 888.2350515 •307.235.0515 •Fax [phone] •[e-mail]·ww<Y.energylab.com
LASORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120896·011
TW4·4
Report Date:01111/10
Collection Date:12/29/0908:54
DateReceived:12/30/09
Matrix:Aqueous
Analyses
MAJOR IONS
Chloride
Nitrogen,Nitrate+Nitrite as N
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr:Dibromofluoromethane
Surr:p·Bromofluorobenzene
Surr:Toluene-dB
Surr:1,2-Dichlorobenzene-d4
.._.~.....__._._-
Result Units Qualifier RL
41 mg/L 1
7.6 mg/L 0.2
1.1 uglL 1.0
950 ug/L 500
NO ug/L 1.0
NO ug/L 1.0
108 %REC 70·130
108 %REC 80-120
105 %REC 80-120
108 %REC 80·120
MCL!
QCL Method
A4500-CI B
E353.2
SW8260B
SW8260B
SW8260B
SW8260B
SW82608
SW82608
SW8260B
SW8260B
Analysis Date 1By
12/31/0916;32/Ijl
01/08/1011;08/jal
01/0611003;291 wen
01/05/10 13:37/wen
01/06/10 03:29 I wen
01/06/1003:291 wen
01/06/1003:291 wen
01/0611003:29/wen
01/06/1003:291 wen
01/06/10 03:29 /wen
Report
Definitlons:
RL .Analyte reporting limit.
QCL ~Quality control limit.
Mel"Maximum contaminant level.
NO .Not detected at the reporting limit.
tX'?""t}";i;;'1;,'~'W'''1 ENERGVLABORATOI'IfE8,INC.'2393 Sal/Creek Highway (82801)'P.O.Box 3258 •Casper,WV82802f:l6?!'!i;?:(/1!11f$_~t?0X/,TollF/ee888.235.0515 .307235.0515 'Fax [phone] .ci:/sper@enwgylab,com'wWI.y,8nergylab,com
I1%f;lQ~klfljjj£fjj§j ..._.~..._....._._.._.~.,.."..__.
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab ID:
ClientSample ID:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120896-012
TW4·22
Report Date:01/11/10
Collection Date:12/29/0908:03
DateReceived:12130/09
Matrix:Aqueous
•.......~--"'..---..""--......-.-..._._.....__._._.._------_._---_._-_._-_.
Analyses Result Units Qualifier RL
MAJOR IONS
Chloride 175 mg/L 1
Nitrogen,Nitrate+Nitrite as N 17.8 mglL 0.2
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ugJL 1.0
Chloroform 380 ug/L 100
Chloromethane NO ug/L 1.0
Methylene chloride NO ug/L 1.0
Surr:Dibromofluoromethane 104 %REC 70-130
Surr:p.Bromofluorobenzene 108 %REC 80·120
Surr:Toluene·dB 105 %REC 80-120
Sure 1,2-Dichlorobenzene-d4 105 %REC 80-120
MCU
QCL Mothod
A4500-CI B
E353.2
SW8260B
SW8260B
SW8260B
SW8260B
SW8260B
SW8260B
SW8260B
SW8260B
Analysis Date I By
12/31/09 16:36 Iljl
01108/1011:11/jal
01/06/10 04:121 wen
01/06/10 02:46 Iwen
01/06/1004:12 I wen
01/06/10 04;121 wen
01/06/1004:121 wen
01106/10 04;12 Iwen
01106/10 04:12 Iwen
01/06/1004:121 wen
Report
Definitions:
Rl .Analyte reporting limit.
QCL .Quality control limit.
Mel -Maximum contaminant level.
NO ~Not detected at the reporting limit.
ENERGVlABO/1liTORlES,INC.•2S8S :JRII CreekliiqliwB!'(8260Ij'eo Box 3258 •Caspel;WV82bYJ2
.70/1 Hoe 888.235.0515 .307235051(;'•Pax 307.234.163lJ 'casper(jPenergy/ab.com'www.energyMb.com
-_._----_.---
LABORATORY ANALYTICAL REPORT
Result Units
MAJOR IONS
Chloride
Nitrogen,Nltrate~'Nnfite as N
Denison Mines (USA)Corp
4th Quarler Chloroform
C09120896·013
lW4·2
Client:
Project:
LablD:
Client Sample ID:
Analyses
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surf:DlbromofJuoromethane
Surr:p~Bromofluorobenzene
Surr:Toluene-d8
Surr;1,2.Dichlorobenzene·d4
46
6,4
2.0
1600
ND
ND
108
lOB
108
107
mg/l
mg/L
ug/L
ug/L
ug/L
ug/L
%REC
%REC
%REC
%REC
Report Date:01111110
Collection Date:12/29/09 08:25
DateReceived:12/30109
Matrix:Aqueous
MCU
Qualifier RL QCL Method Analysis Date I By
1 A4500-CI B 12/31/09 16:45 Iljl
0.2 E353.2 01/08/1011:18 I jal
1.0 SW8260B 01106/10 Q4:54/wen
500 SW8260B 01105/10 14:521wen
1.0 SW8260B 01J06/10 04:54/wen
1.0 SW8260B 01/06/10 04:541 wen
70·130 SW8260B 01/06/10 04:54 Iwen
80·120 SW8260B 01/06/1004:541 wen
80-120 SW8260B 01/06/1004:54/wen
80-120 SW8260B 01/06'1004:54 I wen
Report
Definitions:
RL -Analyte reporting limit.
QCl .Quality control limit.
Mel ~Maximum contaminant level.
NO ~Not detected at the reporting limit.
ENERGVLABORATORIES,INC.·23938a/lCreek Higllway(821101)'1'.0.Box3258 •Caspe!;WV82602
,TollFree 888235.0515 '307.235.0515 •Fax [phone] •casper@energy/ab.com·www.energy/ab.com
LASaRATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120896-014
Trip Blank
Report Date:
Collection Date:
DateReceived:
Matrix:
01/11/10
12/29/09
12/30/09
Aqueous
....__......~.__.-........_---..--..--'-"-'''-...
MCU
Analyses Result UnIts Qualifier RL QCL Method Analysis Date I By
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1.0 SW8260B 01/05110 12:59/wen
Chloroform NO ug/L 1.0 SW8260B 01/05/10 12:591 wen
Chloromethane ND ug/L 1.0 SW8260B 01105/1012:59/wen
Methylene chloride NO ug/L 1.0 SW8260B 01 {05/1 0 12:59 !wen
Surf:Dibromofluoromelhane 101 %REC 70-130 SW8260B 01(05/1012:59/wen
Surr:p.Bromofluorobenzene 110 %REC 80-120 SW8260B 01/05110 12:59/wen
Surr:Toluene-dB 103 %REC 80-120 SW8260B 01/05/10 12:59/wen
Surr:1,2~Djchlorobenzene-d4 105 %REC 80-120 SW8260B 01/05/1012:59/wen
Report
Definitions:
RL ~Analyte reporting limit.
QCL •Quality control limit.
Mel·Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLAIJONArORlE8,fIVC.•2,9.93 Safl C/O"k Highway(82601)'Po.Box 3258 •Caspe!;WI'82602
7011ArJe 888.285.0515 .307.235.0515 'Fax [phone] 'casper@enelgylalJ,corJJ'wWJ¥.energy/ab.com
QAfQC Summary Report
Client:Denison Mines (USA)Corp r,eport Date:01/11110
Project:4th Quarter Chloroform Work Order:C09120896
r·;~~·;;~~.Count Result Units RL %REC Low limit High Limit RPJ)RPDLimit '~~~;-1
Method:A4500-CI B Batch:091231A-Cl-TTR-W
Sample ID:MBLK9-091231A Method Blank Run:TITRATION_0912318 12/3110915:38
Chloride ND mglL 0.4
Sample ID:C09120896-010AMS Sample Matrix Spike Run:TITRATION_0912318 1213110916:26
Chloride 217 mg/L 1.0 100 90 11O
Sample 10:C09120896·Q10AMSD Sample Matrix SpUw Duplicate Run:TITRATION_091231B 12131/09 16:28
Chloride 215 mgJL 1.0 99 90 110 0.8 10
Sample ID:C09120896-013AMS Sample Matrix 8pil(e Run:TITRATION_0912318 12t31f0916:45
Chloride 224 mg/l 1.0 101 90 110
Sample 10:C09120896-013AMSD Sample Matrix Spil\e Duplicate Run:TITRATION_0912318 1213110916:48
Chloride 221 mg!L 1.0 99 90 110 1.6 10
Sample 10:LCS35-091231A Laboratory Control Sample Run:TITRATION_0912318 12131/0916:51
Chloride 3570 mg/L 1.0 101 90 110
Method:E353.2 Batch:R128300
Sample ID:MBLK-1 Method Blank Run:TECHNICON_100105A 01/05/1009:59
Nitrogen,Nitrate+Nitrite as N ND mgll 0.03
Sample ID:LCS-2 Laboratory Control Sample Run:TECHNICON_l00105A 01/05/10 10:02
Nitrogen,Nitrate+Nilrite as N 2.53 mg/l 0.10 101 90 110
Sample 10:C09120896·002BMS Sample Matrix Spike Run:TECHNICON_1 00105A 0110511012:12
Nitrogen,Nitrate+Nitrite as N 1.96 mg/L 0.10 95 90 110
Sample 10:C09120896·002BMSD Sample Matrix Spike Duplicate Run:TECHNICON_l00l05A 01105/1012:14
Nitrogen,Nitrate+Nitrite as N 2.02 mg/L 0.10 98 90 110 3 10
Method:E353.2 Batch:R128408
Sample ID:MBLK-1 Method Blank Run:TECHNICON_l00108A 01108/1010:36
Nitrogen,Nitrate+Nitrite as N 0.04 mg/L 0.Q3
Sample 10:LCS-2 Laboratory Control Sample Run:TECHNICON_100108A 01108/1010:38
Nitrogen,Nitrate+Nitrjte as N 2.70 mgfL 0.10 106 gO 110
SamplelD:C10010128·001AMS Sample Matrix Spike Run:TECHNICON_l00108A 01108/1010:53
Nitrogen,Nltrate+Nitrite as N 2.82 mg/l 0.10 107 gO 110
Sample ID:C10010128-001AMSD Sample Matrix Spike Duplicate Run:TECHNICON_100108A 01/0811010:56
Nitrogen,Nitrate+Nilrite as N 2.64 mgll 0.10 98 90 110 6.6 10
Sample ID:C09120909-001CMS Sample Matrix Spike Run;TECHNICON_100108A 01/08/1011:31
Nitrogen,Nitrate+Nitrite as N 2.02 mg/L 0.10 95 gO 110
Sample ID:C09120909-001 CMSD Sample Mat(ix Spike Duplicate Run:TECHNICON_l00108A 01/0811011:33
Nitrogen,Nitrate+Nitrite as N 1.98 mgll 0.10 92 90 11O 2 10
-----_.._-----_._------._._..._._._._--~.~-_...~_._-_.-.,.-_.._---_...-.._--_...._-~,--.--.--_._----_..
Qualifiers:
RL .Analyte reporting limit.NO·Not detected at the reporting limit.
ENERGVLAI30RATORlES,INC,'2393SailCreekHighway (82601)'PO Box3258 'Casper,WV82602
,TollFree 888.235.{J5!5 •807.235.0515 •Fax [phone] •cMper({{Jenelgyltib,coll7'lilwl-v.Dnergylab.com
Glient:Denison Mines (USA)Corp
Project:4th QUfllier Chloroform
Report Date:01106/10
Work Order:C09120896
r---.-----_.,-,
i Analyle Result Units RL %REC Low Limit High Limit RPO RPDLimit Qual,---_.---_!
Method:SW3260B Batch:R128289
Sample 10:04-Jan·10-LCS_3 Laboratory Control Sample Run:GCMS2_100104B 01/04/1009:47
Carbon tetr8chloride 11 ug/L 1.0 113 70 130
CI)loroform 10 ug/L 1,0 105 70 130
Chloromethane 7,7 ug/L 1.0 77 70 130
Methylene chloride 8.1 uglL 1.0 81 70 130
Sure Dibromofluorornelhane 1.0 105 70 130
Surr:p"Bromofluorobenzene 1.0 101 30 130
Surr:Toluene-d8 1.0 104 80 120
Surr:1,2-Dicl)lorobenzene-d4 1.0 '104 80 120
Sample 10:04.Jan-10_MBLK_6 Method Blanl<Run:GCMS2-100104B 01/04/10 11:46
Carbon tetrachloride NO ug/L 1.0
Chloroform NO ug/L 1.0
Chloromethane NO uglL 1,0
Methylene chloride NO ug/L 1,0
Sure DlbromofluoromeU13ne 1.0 95 70 130
Surr:p-Bromolluorobenzenc 1,0 108 80 120
Surr:Toluene-dB 1.0 102 30 120
Surr;1,2-Dichlorobenzene-d4 1.0 104 80 120
Sample 10:C091207BB·004AMS Sample Matrix Spike r,un:GCMS2_100104B 01/04/1020:09
Carbon tetracllioride 200 uglL 20 98 70 130
ChloroForm 210 ug/L 20 106 70 130
Chloromethane 190 ug/L 20 97 70 130
Methylene chloride 200 ug/L 20 100 70 130
Surr:Dibromofluoromethane 20 101 70 130
Surr:p-Bromofluorobenzene 20 95 80 120
Surr:Toluene-dB 20 108 80 120
Surr:1,2·Dichlorobenzene-d4 20 102 80 120
Sample 10:C09120788,004AMSO Sample MatriX Spike Duplicate Run:GCMS2_100104B 01/04/1020:49
Carbon tetrachloride 210 ug/L 20 105 70 130 6.7 20
Cilloroform 220 ug/L 20 109 70 130 2,6 20
Chloromethane 200 ug/L 20 100 70 130 2.8 20
Methylene chloride 200 ug/L 20 101 70 130 0.4 20
Surr:Dibromofluorofliethane 20 101 70 130 0 10
Surr:p-BromoOuorobenzene 20 104 80 120 0 10
Surr:Toluene-dB 20 105 80 120 0 10
Surr:1,2-Diclllorobenzene-d4 20 102 80 120 0 10
Sample ID:05.Jan·10_LCS_3 LaboratoryControl Sample Run:GCMS2__1001048 01/05/1010:25
Carbon tetrachloride 11 ug/L 1,0 112 70 130
Chloroform 12 ug/L 1.0 122 70 130
Cilloromethane 11 ug/L 1,0 112 70 130
Methylene chloride 12 ug/L 1.0 122 70 130
----~----_._..._......_------------.._._--._--,-----------._'".,-.-.--------~._-
Qualifiers:
RL -Analyle reporting limit.NO H Notdetected at the reporting limit.
ENENGVLA/30rlATOF/lt:!8,INC.'2393Sail Creek Highway(82001)'p.o.Box 3258 •Casper,WV82b'02
-To//Free 888.2850515 .301,235.0515 •Fax [phone] •[e-mail]·vl1wl.energylab,com
Client:Denison Mines (USA)Corp Report Date:01/06/10
Project:4tl1 Quarter Chloroform Worl<Order:C09120896
Analyte Result Units RL %REC Low Limit High Limit RPD I~PPUlllit Qual
Method:SWS260B Batch:R12S2S9
Sample 10:05..Jan~10_LCS_3 Laboratory Control Sample Run:GCMS2_1001040 01105/1010:25
Surr:Dibromofluorornethan8 1.0 106 70 130
Surr:p-Brornofluorobenzene 1.0 98 SO 130
Surf:Toluene-dB 1.0 10S 80 120
Surr:1,2vDichlorobenzene-d4 1.0 104 80 120
Sample ID:05..Janv 10_MBLK_6 Mettlod Blank Run:GCMS2_100104B 0110511012:21
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:Dlbrornofluoromethane 1.0 102 70 130
Surr:p-Bromofluorobenzcne 1.0 111 80 120
Surt:Toluene-dB 1.0 102 80 120
Surr:1>2~DjchlorobGnzene"d4 1.0 102 80 120
Sample 10:C09120896·010CMS Sample Matrix Spike I~un;GCMS2_1001048 01/05/1018:03
Carbon tetrachloride 2000 ug/L 200 102 70 130
Chloroform 3600 ug/L 200 109 70 130
Chloromethane 2000 uglL 200 99 70 130
Methylene chloride 2100 ug/L 200 104 70 130
Surr:DibromofJuorornelhan8 200 100 70 '130
Surr:p-Bromofluorobenzene 200 97 80 120
Surr:Toluene-d8 200 105 80 120
Surr:1,2-Dic)'llorobenzene-d4 200 103 SO 120
Sample 10:C09120896·010CMSD Sample Matrix Spike Duplicate Run:GCMS2_100104B 0110511018:43
Carbon tetracl)loride 2100 uglL 200 103 70 130 1.2 20
Chloroform 3700 ug/L 200 113 70 130 2 20
Chloromethane 2000 uglL 200 98 70 130 0.4 20
Methylene chloride 2000 ug/L 200 102 70 130 2.3 20
Surr:Dibromofluoromethane 200 99 70 130 0 10
Surr:p~8romofluorobenzene 200 99 80 120 0 10
Surr:Toluene-d8 200 106 80 120 0 10
Surr:1,2~Dichlorobcnzene-d4 200 103 SO 120 0 10
Qualifiers:
RL ~Analy(e reporting limit.ND -Not detected at the reporling limit
EPA/State Compliance:
Yes 0 No 0
Qudte/Bottle Order:
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SAMPLE IDENTIFICATION I Coliection I Coliectlon I MATRIX I I,~i£t~~tum (!)N II(Name,Location,Interval,etc.)Date Trme !I ;1
Report~d,:,"~~1St)j~IIJI1Jh~a (;f{%L/SI/
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compa~e:,'-'\eAliSO/oj
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Custody Received by (print):Dalel1"ime-Signafu~e:
Record Received by(print):Datemme-Signature:
Ml!ST be'I---~,t..--------------------/------------------i=.""''''"Offi\7,l',,",,o,''''"'.o:;;,,;;"===9'i',""'f''',m''''''========'''/2:'''~''~'''''''"''',=--?=''~,,--='''=5-.?'''===I,
SIgned Sample Dispesal:Relum toCHent:Lab Disposal:<-fW /;::}.--:<0 -~q~(...~
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 w'Nw.energy!ab.com for additional information,downloadablefee schedule,forms,and Jinks.
pageLof 2_
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l#l.;fflJlifl Chain of Custody and Analytical Request Record
&!Iti,:,,,@u,,];It"""PLEASE PRINT Provide as much information as ossible.
Camp arne:Project Name,PWS,Permit,Etc.I Sample Origin EPA/State Compliance:
1 t,,.I State:UL7
Email:
Purchase Order:iiiiI
Special Report/Formats:i $:8I}!]&[b)7@O@ Cffiili®(lDI]j@'jj'I]j[ID .1 Contact ELI priorto ,1f;':'ipP'~bY:Ii°~IRUSH sample suomlttal I~t>'Lt -('f 1
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In certain circumstances,samples submitted to Energy Laboratories,Inc.may be subcontracted to other certified laboratories in order to comprete the analysis r~~ted.
This serves as notice ofthis possibllity.All sub-contract data will be clearly notated on your analytical report.
Visit our web site atwww.energylab.comforadditional information,downloadable fee schedule,forms,and links.
Eli1elrgy labolraltories ~Ii1C
Workolrdelr Receopt Check~ist
Denison Mines USA Corp
1111111111111111111111111111111111111111111111111111111
C09120896
Login completed by:Diane Downing
Reviewed by:
Reviewed Date:
Date and Time Received:1213012009 9:20 AM
Received by:al
Carrier name:FedEx
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 lest?
All samples received within holding time?
ContalnerfTemp Blank temperature:
Water"VOA vials have zero headspace?
Water·pH acceptable upon receipt?
Contact and Corrective Action Comments:
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
NoD
No 0
No 0
No 0
No 0
No 0
No D
No 0
No 0
No 0
No 0
No 0
Not Present 0
Not Present 0
Not Present 0
No VOA vials submitted 0
NotApplicable 0
!F,,""!:7"':FYi'''Si;:Yi;y EMERGVLABORATORIES,INC.,,23938f)/1 Creek Highway (82601)·IW.Box 3268 •Casper,WY82602dfF!jj:;?ffX!J\(i!fiiJJ!;/'INI Free 888.235.0515 •30~235.0515 •Fax 30~234.1639 •easper(iJ'energylab.com·wWi1<ellergylab.eom
A@J..-I~fit{~.__.,".._...._._."
CLIENT:Denison Mines (USA)Corp
Project:4th Quarter Chloroform
Sample Delivery Group:C09120896
ORIGINAL SAMPLE SUBMITTAL(S)
All original sample sLlbmittals have been returned with tl18 data package.
Date:11-Jan-10
CASE NARRATIVE
SAMPLE TEMPERATURE COMPLIANCE:4°C (±2°C)
Temperature of samples received may not be considered properly preselved by accepted standards.Samples that are
hand delivered immediately after collection shall be considered acceptable ifthere is evidence that the chilling process has
begun.
GROSS ALPHA ANALYSIS
Method 900.0 for gross alpha and gross beta is intended as a drinking water method for low TDS waters.Data provided by
this method for non potable waters sllOUJd 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.
SOIUSOLID 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 refiects the results for seven
individual Aroclors.When the resliits for all seven are ND (not detected),the sample meets EPA compliance criteria for
PCB monitoring.
SUBCONTRACTING ANALYSIS
Subcontracting ofsample 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 Reporl.
BRANCH LABORATORY LOCATIONS
eli-b -Energy laboratories,Inc.-Billings,MT
eli-g -Energy Laboratories,Inc.-Gillette,WY
eliMh M Energy Laboratories,Inc.-Helena,MT
eli-r -Energy Laboratories,Inc.·Rapid City,SD
eli-t ~Energy Laboratories,Inc.M 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 ofthis Analytical Reporl 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 Ell'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 LASORATOf""!S,INC••2393Salt CreekHighway (82601)•P.O.P 'v3258 •Casper,WY82602
To//Free 888.235.0515·f '235.0515,Fax [phone] •casper@energy :om •www.energylab.com
ANALYTICAL SUMMARY REPORT
January 06,2010
Denison Mines (USA)Corp
6425 S Hwy 191
Blanding,UT 84511
Workorder No.:C09120811
Project Name:4th Quarter Chloroform
Quote iD:C2975 -Chloroform Sampling
Energy Laboratories,Inc,received the following 11 samples for Denison Mines (USA)Corp on 12/23/2009 for analysis.
Sample ID Collect Date Receive Date Matrix Test
C09120811-001 TWN-5R
C09120811-002 TWN-10R
C09120811-003 TWN-6R
C09120811-004 TWN-18R
C09120811-005 TWN-21R
C09120811-006 TWN-5
C09120811-007 TWN-10
C09120811-008 TWN-6
C09120811-009 TWN-18
C09120811-010 TWN-21
C09120811-011 Trip Blank
12/21/0908:50 12/23/09
12/21/0914:39 12/23/09
12/21/0913:39 12/23/09
12/21/0909:59 12/23/09
12/21/0911:1712/23/09
12/22/0909:10 12/23/09
12/22/0909:1612/23/09
12/22/0900:00 12/23/09
Aqueous
Aqueous
Aqueous
Aqueous
Aqueous
Aqueous
Aqueous
Aqueous
Aqueous
Aqueous
Aqueous
Chloride
Nitrogen,Nitrate +Nitrite
SW8260B vacs,Standard List
Same As Above
Same As Above
Same As Above
Same As Above
Same As Above
Same As Above
Same As Above
Same As Above
Same As Above
SW8260B vacs,Standard List
-----.------_..~~~~~~~~~~~~~~-
As appropriate,any exceptions or problems with the analyses are noted in the Laboratory Analytical Report,the
QAlQC Summary Report,or the Case Narrative.
Ifyou have any questions regarding these tests results,please call.
Report Approved By:&~a..0 D·uJ&~e
Step~nie D.Waldrop 0
Reporting Supervisor
ENERGYLABORA T0F!'''9,INC••2393SailCreek Highway (82601)•P.O !1"v3258 •Casper,WY82602
TollFree 888.235.0515 .,?35.0515·Fax [phone] •casper@energy/i 'm •www.energylab.com
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab ID:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120811-001
TWN-5R
Report Date:01/06/10
Collection Date:12/21/0908:50
DateReceived:12/23/09
Matrix:Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride NO mg/L 1 A4500-CI B 12/28/09 12:291ia
Nitrogen,Nitrate+Nitrite as N NO mg/L 0.1 E353.2 12/29/0914:291 ial
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO uglL 1.0 SW8260B 12/29109 14:081 wen
Chloroform NO ug/L 1.0 SW8260B 12/29109 14:081 wen
Chloromethane NO ug/L 1.0 SW8260B 12/29/09 14:081 wen
Methylene chloride NO ug/L 1.0 SW8260B 12/29109 14:081 wen
Surr:Dibromofluoromethane 99.0 %REC 70-130 SW8260B 12/2910914:08/wen
Surf:pMBromofluorobenzene 109 %REC 80-120 SW8260B 12/29109 14:081 wen
Sure Toluene-dB 103 %REC 80-120 SW8260B 12/2910914:08/wen
Surr:1,2-Dichlorobenzene-d4 104 %REC 80-120 SW8260B 12/29109 14:081 wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel-Maximum contaminant level.
ND -Not detected at the reporting limit.
ENERGYLABORATO!7'"'c;,INC.•2393Sail Creek Highway(82601)•P.O,flo"3258 •Casper,WY82602
TollFree 888.235.0515 •,?35.0515 •Fax [phone] •casper@energy4 1m'www.energylab,com
LASORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120811-002
TWN-10R
Report Date:
Coltection Date:
DateReceived:
Matrix:
01/06/10
12/21/0914:39
12/23/09
Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride NO mglL 1 A4500-CI B 1212810912:311ja
Nitrogen,Nitrate+Nitrite as N NO mglL 0,1 E353,2 12/29109 14:321jal
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1,0 SW8260B 12/29/0914:461 wen
Chloroform NO ug/L 1,0 SW8260B 12/2910914:461 wen
Chloromethane NO ug/L 1,0 SW8260B 12/29/0914:461 wen
Methylene chloride NO ug/L 1,0 SW8260B 12/29/0914:461 wen
Surr:Dibromofluoromethane 102 %REC 70-130 SW8260B 12/29/09 14:461wen
Surr:p-Bromofluorobenzene 106 %REC 80-120 SW8260B 12/2910914:461 wen
Surr:Toluene-dB 105 %REC 80-120 SW8260B 12/29/09 14:461wen
SUfr:1,2-Dichlorobenzene-d4 103 %REC 80-120 SW8260B 12/29/09 14:461wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORATOP'CS,INC••2393 Salt Craak Highway(82601)•PO.fh3258 •Caspar,WY82602
7011Fraa 888.235.0515 •235.0515 •Fax [phone] •[e-mail]'www.anargylab.com
LASORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample ID:
Denison Mines (USA)Corp
4th Quarter Chioroform
C09120811-003
TWN-6R
Report Date:01/06/10
Collection Date:12/21/0913:39
DateReceived:12/23/09
Matrix:Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride NO mg/L 1 A4500-CI B 12/28/09 12:321ia
Nitrogen,Nitrate+Nitrite as N NO mg/L 0.1 E353.2 12/29/09 14:34/ial
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1.0 SW8260B 12/29/09 15:24 /wen
Chloroform NO ug/L 1.0 SW8260B 12/29/09 15:241 wen
Chloromethane NO ug/L 1.0 SW8260B 12/29/09 15:241 wen
Methylene chloride NO ug/L 1.0 SW8260B 12/29/09 15:24/wen
Surf:Dibromofluoromethane 99.0 %REC 70-130 SW8260B 12/29/0915:241 wen
Surr:p-Bromofluorobenzene 102 %REC 80-120 SW8260B 12/29/09 15:24/wen
Surf:Toluene-dB 102 %REC 80-120 SW8260B 12/29/0915:241 wen
Surr:1,2~Dichlorobenzene-d4 103 %REC 80-120 SW8260B 12/29/09 15:241 wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
MeL -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORATOP"=S,INC••2393SailCreek Highway (8260 I)•P.0.p,v3258 •Casper,WY82602
TollFree 888.235.0515 •(235.0515 •Fax [phone] •[e-mail]'www.energylab.com
LASORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120811-004
TWN-18R
Report Date:01/06/10
Collection Date:12/21/0909:59
DateReceived:12/23109
Matrix:Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis DateI By
MAJOR IONS
Chloride NO mglL 1 A4500-CI B 1212810913:14 I ja
Nitrogen,Nitrate+Nitrite as N NO mglL 0.1 E353.2 1212910914:37 I ial
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO uglL 1.0 SW8260B 12129109 16:02 I wen
Chloroform NO ug/L 1.0 SW8260B 12/2910916:021 wen
Chloromethane NO ug/L 1.0 SW8260B 12/2910916:021 wen
Methylene chloride NO ug/L 1.0 SW8260B 12/2910916:021 wen
Surr:Dibromofluoromethane 97.0 %REC 70-130 SW8260B 12/29/0916:021 wen
Surr:p-Bromofluorobenzene 105 %REC 80-120 SW8260B 12/29/09 16:021 wen
Surr:Toluene-dB 103 %REC 80-120 SW8260B 12/29/09 16:02/wen
Surr:1,2-Dichlorobenzene-d4 104 %REC 80-120 SW8260B 12/29/09 16:02/wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORATOP''''S,INC••2393Sal/CreekHighway (82601)•P.O.80v3258 •Casper,WY82602
Toll Free 888.235.0515 •235.0515 •Fax [phone] •casper@energjli Jm •www.energylab.com
LASaRATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120811-005
TWN-21R
Report Date:01106/10
Collection Date:12/21/0911:17
DateReceived:12/23/09
Matrix:Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 1 mglL 1 A4500-CI B 12/28/0913:20 I ja
Nitrogen,Nitrate+Nitrite as N NO mglL 0.1 E353.2 12/29/0914:391 jal
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1.0 SW8260B 12/29/0916:40 I wen
Chloroform NO u9/L 1.0 SW8260B 12/29/09 16:40 I wen
Chloromethane NO ug/L 1.0 SW8260B 12/29/09 16:40 I wen
Methylene chloride NO ug/L 1.0 SW8260B 12/29/09 16:40 I wen
Surr:Dibromofluoromethane 98.0 %REC 70-130 SW8260B 12/29/0916:40 I wen
Surr:p-Bromofluorobenzene 106 %REC 80-120 SW8260B 12/29/0916:40 I wen
Surr:Toluene~d8 105 %REC 80-120 SW8260B 12/29/09 16:40 I wen
Surr:1,2-Dichlorobenzene-d4 104 %REC 80-120 SW8260B 12/29/09 16:40 I wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel -Maximum contaminant level.
ND -Not detected at the reporting limit.
ENERGYLABORATOI1"=S,INC.•2393 Sail CreekHighway(82601)•P.O.8 M 3258 •Casper,WY82602
Toll Free 888.235.0515 •(?35.0515 •Fax [phone] •casper@energy/)m'www.energylab.com
LASORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120811-006
TWN-5
Report Date:
Collection Date:
DateReceived:
Matrix:
01/06/10
12/22/0909:10
12/23109
Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 41 mg/L 1 A4500-CI B 12/2810913:241ja
Nitrogen,Nitrate+Nitrite as N 7.5 mg/L 0.2 E353.2 12/29/0914:491ial
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1.0 SW8260B 12/29/0917:19/wen
Chloroform 8.5 ug/L 1.0 SW8260B 12/29/0917:19/wen
Chloromethane NO ug/L 1.0 SW8260B 12/29/0917:19/wen
Methylene chloride NO ug/L 1.0 SW8260B 12/29/0917:191 wen
Surr:Dibromofluoromethane 102 %REC 70-130 SW8260B 12/29/0917:19/wen
Surr:pMBromofluorobenzene 104 %REC 80-120 SW8260B 12/29/0917:19/wen
Surr:Toluene-dB 103 %REC 80-120 SW8260B 12/29/0917:19/wen
Surr:1,2-DichlorobenzeneMd4 106 %REC 80-120 SW8260B 12/29/0917:19/wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel -Maximum contaminant level.
ND -Not detected at the reporting limit.
ENERGYLABORAT08'~S,INC.•2393 Sail Creek Highway (82601)•P.O.B~v 3258 •Casper,WY82602
Toll Free 888.235.0515 • ,?35.0515·Fax [phone] •casper@energyl Jm •www.energylab.com
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120811·007
TWN·10
Report Date:01/06110
Collection Date:12/22/0909:16
DateReceived:12/23/09
Matrix:Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 51 mglL 1 A4500·CI B 12/28/09 13:26 I ia
Nitrogen,Nitrate+Nitrite as N 3.5 mglL 0.2 E353.2 12/29/09 14:52 /ial
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride ND ug/L 1.0 SW8260B 12/29/09 17:58/wen
Chloroform 300 U9/L 100 SW8260B 12/30/0917:10 I wen
Chloromethane ND U9/L 1.0 SW8260B 12/29/0917:58/wen
Methylene chloride ND ug/L 1.0 SW8260B 12/29/0917:581 wen
Surr:DibromofJuoromethane 100 %REC 70·130 SW8260B 12/29/09 17:58/wen
Surr:p-Bromofluorobenzene 105 %REC 80·120 SW8260B 12/29/0917:581 wen
Surr:Toluene-dB 103 %REC 80·120 SW8260B 12/29/09 17:58/wen
Surr:1,2~Dichlorobenzene-d4 106 %REC 80·120 SW8260B 12/29/09 17:581 wen
Report
Definitions:
RL -Analyte reporting limit.
OCL -Quality control limit.
Mel -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORATOR't:.S,INC••2393Sal/CreekHighway (82601)'p.D.Bf'V3258 •Casper,WY82602
TollFree 868.235.0515 •,'35.0515·Fax [phone] •casper@energy/.>m •www.energylab.com
LASORATORY ANALYTICAL REPORT
Client:
Project:
Lab ID:
Client Sample ID:
Denison Mines (USA)Corp
4th Quarter Chioroform
C09120811-008
TWN-6
Report Date:
Collection Date:
DateReceived:
Matrix:
01/06/10
12/22/0908:58
12123109
Aqueous
----_._-_.,
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 41 mglL 1 A4500-CI B 12128109 13:281 ia
Nitrogen,Nitrate+Nitrite as N 6.1 mglL 0.2 E353.2 1212910914:541ial
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO uglL 1.0 SW8260B 12129109 18:381wen
Chloroform 250 uglL 100 SW8260B 12130109 17:50I wen
Chloromethane NO uglL 1.0 SW8260B 12129109 18:381wen
Methylene chloride NO uglL 1.0 SW8260B 12129109 18:381wen
Surf:Dibromofluoromethane 108 %REC 70-130 SW8260B 12129109 18:381wen
Surr:p-Bromofluorobenzene 106 %REC 80-120 SW8260B 12129109 18:381wen
Surf:Toluene-dB 101 %REC 80-120 SW8260B 12129109 18:381wen
Surr:1,2-Dichlorobenzene-d4 105 %REC 80-120 SW8260B 12129109 18:381wen
Report
Definitions:
RL -Analyte reporting limit.
QCL ~Quality control limit.
Mel-Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORATOR""S,INC.•2393Sail CreekHighway (82601)'p.D.B~v3258 •Casper,WY82602
Toll Free 888.235.0515 •,?35.0515·Fax [phone] •casper@energyk 1m'www.energylab.com
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120811-009
TWN-18
Report Date:
Collection Date:
DateReceived:
Matrix:
01/06/10
12/22/09 08:26
12/23/09
Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 30 mg/L 1 A4500-CI B 12/28/09 13:291 ia
Nitrogen,Nitrate+Nitrite as N 5.4 mg/L 0.2 E353.2 12/29/0914:571 ial
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride ND ug/L 1.0 SW8260B 12/29/0919:18/wen
Chloroform 8.2 ug/L 1.0 SW8260B 12/29/0919:18/wen
Chloromethane ND ug/L 1.0 SW8260B 12/29/0919:181 wen
Methylene chloride ND ug/L 1.0 SW8260B 12/29/0919:18/wen
Surr:Dibromofluoromethane 104 %REC 70-130 SW8260B 12/29/0919:18/wen
Surr:p-Bromofluorobenzene 108 %REC 80-120 SW8260B 12/29/0919:18/wen
Surr:Toluene-dB 104 %REC 80-120 SW8260B 12/29/0919:18/wen
Surr:1,2-Dichlorobenzene-d4 106 %REC 80-120 SW8260B 12/29/0919:18/wen
Report
Definitions:
RL ~Analyte reporting limit.
OCL -Quality control limit.
Mel-Maximum contaminant level.
ND -Not detected at the reporting limit.
ENERGYLABORATO!1'c.'>,INC••2393Sail CreekHighway (82601)•Po.Bev3258 •Casper,WY82602
TollFree 888.235.0515 •L ?35.0515·Fax [phone] •casper@energyh Jm •www.energylab.com
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample ID:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120811-010
TWN-21
Report Date:01106/10
Collection Date:12122/0908:45
DateReceived:12/23109
Matrix:Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 256 mglL 1 A4500-CI B 12/28/09 13:33/ja
Nitrogen,Nitrate+Nitrlte as N 8.4 mglL 0.2 E353.2 12/29/09 15:09 I ial
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1.0 SW8260B 12/29/0919:581 wen
Chloroform 160 ug/L 100 SW8260B 12/30/0918:27/wen
Chloromethane NO ug/L 1.0 SW8260B 12/29109 19:58/wen
Methylene chloride NO ug/L 1.0 SW8260B 12/29/09 19:58/wen
Surr:Dlbromofluoromethane 111 %REC 70-130 SW8260B 12/29109 19:58/wen
Surr:p-Bromofluorobenzene 108 %REC 80-120 SW8260B 12/29/09 19:58 I wen
Surr:Toluene-dB 103 %REC 80-120 SW8260B 12/29/09 19:58 I wen
Surr:1,2-Dichlorobenzene-d4 106 %REC 80-120 SW8260B 12/29/0919:581 wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORATORIC<;,INC••2393 Sail Creek Highway (82601)•P.0.Brv .1258 •Casper,WY82602
milFree 888.235.0515 •,'35.0515 •Fax [phone] •casper@energyli 'In'www.energylab.co'ln
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120811-011
Trip Blank
Report Date:
Collection Date:
DateReceived:
Matrix:
01/06/10
12/22109
12/23109
Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1.0 SW8260B 12/29/0920:37 I wen
Chloroform NO ug/L 1.0 SW8260B 12/29/09 20:37 I wen
Chloromethane NO uglL 1.0 SW8260B 12/29/0920:37 I wen
Methylene chloride NO ugiL 1.0 SW8260B 12/2910920:37 I wen
Surr:DibromofJuoromethane 107 %REC 70-130 SW8260B 12129/0920:37 I wen
Surr:p-Bromofluorobenzene 107 %REC 80-120 SW8260B 12129/0920:37 I wen
Surr:Toluene-dB 103 %REC 80-120 SW8260B 12/29/0920:37 I wen
Surr:1,2-Dichlorobenzene-d4 105 %REC 80-120 SW8260B 12/2910920:37 I wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORA TOR''''c;,INC.•2393Sail Creek Highway(82601)'PO.Ef~"3258 •Casper,WY82602
TollFree 888.235.0515 •,.'35.0515 •Fax [phone] •casper@energyli m'www.energylab.com
QA/QC Summary Report
Client:Denison Mines (USA)Corp Report Date:01/06/10
Project:4th Quarter Chloroform Work Order:C09120811
Analyte Count Result Units RL %REC Low Limit High Limit RPO RPOLimit Qu:l
Method:A4500·CI B Batch:091228-CL-TTR·W
Sample 10:MBLK9-091228 Method Blank Run:TITRATION_091228A 12/28/0909:49
Chloride NO mg/L 0:4
Sample 10:LCS35-091228 Laboratory Control Sample Run:TITRATION_091228A 12/28/0910:57
Chloride 3530 mg/L 1.0 100 90 110
Sample 10:C09120811-004AMS Sample Matrix Spike Run:TITRATION_091228A 12/28/0913:16
Chloride 35.0 mg/L 1.0 99 90 110
Sample 10:C09120811-004AMS Sample Matrix Spike Duplicate Run:TITRATION_091228A 12/28/0913:18
Chloride 35.7 mg/L 1.0 101 90 110 2 10
Sample 10:C09120811-010AMS Sample Matrix Spike Run:TITRATION_091228A 12/28/0913:35
Chloride 1140 mg/L 1.0 100 90 110
Sample 10:C09120811-010AMS Sample Matrix Spike Duplicate Run:TITRATION_091228A 12/28/0913:37
Chloride 1160 mg/L 1.0 102 90 110 1.5 10
Method:E353.2 Batch:R128102
Sample 10:MBLK-1 Method Blank Run:TECHNICON_091229A 12/29/09 11 :50
Nitrogen,Nitrate+Nitrite as N ND mg/L 0.03
Sample 10:LCS-2 Laboratory Control Sample Run:TECHNICON_091229A 12/2910911 :54
Nitrogen,Nitrate+Nitrite as N 2.61 mg/L 0.10 102 90 110
Sample 10:C09120796-001AMS Sample Matrix Spike Run:TECHNICON_091229A 12/29/0914:22
Nitrogen,Nitrate+Nitrite as N 2.12 mg/L 0.10 104 90 110
Sample 10:C09120796-001AMSO Sample Matrix Spike Duplicate Run:TECHNICON_091229A 12/29/0914:24
Nitrogen,Nitrate+Nltrite as N 2.07 mg/L 0.10 101 90 110 2.4 10
Sample 10:C09120833-001AMS Sample Matrix Spike Run:TECHNICON_091229A 12/29/09 15:02
Nitrogen,Nitrate+Nitrlte as N 1.95 mg/L 0.10 94 90 110
Sample ID:C09120833-001AMSD Sample Matrix Spike Duplicate Run:TECHNICON_091229A 12/29/0915:04
Nitrogen,Nitrate+Nitrite as N 1.96 mg/L 0.10 94 90 110 0.5 10
Qualifiers:
RL ~Analyte reporting limit.NO -Not detected at the reporting limit.
ENERGYLABORATORIF~INC••2393SaltCreekHighway(82601)•P.O.80("'58 •Casper,WY82602
TollFree 888.235.0515 •30.5.0515 •Fax [phone] •casper@energylalJ.•www.energylab.com
QAlQC Summary Report
Client:Denison Mines (USA)Corp
Project:4th Quarter Chloroform
Report Date:12131109
Work Order:C09120811
IAnalyle Result Units RL %REC Low Limit High Limit RPO RPDLimit Qual
Method:SW8260B Batch:R128172
Sample 10:29-0ec·09_LCS_3 Laboratory Control Sample Run:GCMS2_091229A 12/29/09 11 :28
Carbon tetrachloride 9.9 ug/L 1.0 99 70 130
Chloroform 10 ug/L 1.0 103 70 130
Chloromethane 8.6 uglL 1.0 86 70 130
Methylene chloride 9.6 ug/L 1.0 96 70 130
Surf:Dibromofluoromethane 1.0 104 70 130
Surr:p-Bromofluorobenzene 1.0 98 80 130
Surr:Toluene-dB 1.0 106 80 120
Surr:1,2-Dichlorobenzene-d4 1.0 103 80 120
Sample ID:29-0ec-09_MBLK_6 Method Blank Run:GCMS2_091229A 12129/0913:30
Carbon tetrachloride NO ug/L 1.0
Chloroform NO ug/L 1.0
Chloromethane NO uglL 1.0
Methylene chloride NO ug/L 1.0
Surf:Dibromofluoromethane 1.0 102 70 130
Surr:p-Bromofluorobenzene 1.0 110 80 120
Surf:Toluene-dB 1.0 106 80 120
Surr:1,2-DichJorobenzene-d4 1.0 106 80 120
Sample 10:C09120775-001AMS Sample Matrix Spike Run:GCMS2_091229A 12/29/0921:55
Carbon tetrachloride 980 ug/L 100 98 70 130
Chloroform 1100 ug/L 100 105 70 130
Chloromethane 930 ug/L 100 93 70 130
Methylene chloride 1000 uglL 100 101 70 130
Surr:DibromofJuoromethane 100 103 70 130
Surr:p-Bromofluorobenzene 100 97 80 120
Surr:Toluene-dB 100 105 80 120
Surr:1,2-0ichlorobenzene-d4 100 104 80 120
Sample ID:C09120775-001AMSO Sample Matrix Spike Duplicate Run:GCMS2_091229A 12129/0922:34
Carbon tetrachloride 1000 ug/L 100 104 70 130 5.9 20
Chloroform 1100 ug/L 100 111 70 130 5.5 20
Chloromethane 960 ug/L 100 96 70 130 3 20
Methylene chloride 1000 ug/L 100 104 70 130 3.1 20
Surr:Dibromofluoromethane 100 104 70 130 0 10
Surr:p-Bromofluorobenzene 100 99 80 120 0 10
Surr:Toluene-dB 100 106 80 120 0 10
Surr:1,2-DichJorobenzene~d4 100 105 80 120 0 10
Sample ID:30-0ec-09_LCS_3 Laboratory Control Sample Run:GCMS2_091229A 12/30/0910:21
Carbon tetrachloride 10 ug/L 1.0 102 70 130
Chloroform 11 ug/L 1.0 108 70 130
Chloromethane 9.0 ug/L 1.0 90 70 130
Methylene chloride 10 ug/L 1.0 105 70 130
----_.._-
Qualifiers:
RL -Analyte reporting limit.NO -Not detected at the reporting limit.
ENERG YLABORATORIS"INC..2393Saft Creek Highway (82601)•P.0.Boy 0"58 •Casper,WY82602rolfFree888.235.0515 •3rJ.1.0515'Fax [phone] •casper@energylatf.•www.energylab.com
QAlQC Summary Report
Client:Denison Mines (USA)Corp
Project:4th Quarter Chloroform
Report Date:12/31109
Work Order:C09120811
rIAnalyte Result Units RL %REC Low Limit High Limit RPO RPDLimit Qual
I
Method:SW8260B Batch:R128172
Sample 10:30·0ec-09_LCS_3 Laboratory Control Sample Run:GCMS2_091229A 12/30/0910:21
Surr:Dibromofluoromethane 1.0 108 70 130
SUff:p~Bromofluorobenzene 1.0 106 80 130
Surr:Toluene-dB 1.0 108 80 120
Surr:1,2-Dichlorobenzene-d4 1.0 105 80 120
Sample 10:30-0ec-09_MBLK_6 Method Blank Run:GCMS2_091229A 12/30/0912:40
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 1.0 109 80 120
Surr:TolueneMd8 1.0 105 80 120
Surr:1,2-Dichlorobenzene-d4 1.0 103 80 120
Sample ID:C09120811-010CMS Sample Matrix Spike Run:GCMS2_091229A 12/3010920:26
Carbon tetrachloride 1100 ug/L 100 114 70 130
Chloroform 1300 ug/L 100 111 70 130
Chloromethane 780 ug/L 100 78 70 130
Methylene chloride 880 ug/L 100 88 70 130
Surr:Dibromofluoromethane 100 104 70 130
Surr:p-Bromofluorobenzene 100 100 80 120
Surr:Toluene-dB 100 104 80 120
Surr:1,2-Dichlorobenzene-d4 100 102 80 120
Sample ID:C09120811-010CMSO Sample Matrix Spike Duplicate Run:GCMS2_091229A 12/3010921:06
Carbon tetrachloride 1200 ug/L 100 117 70 130 2.8 20
Chloroform 1300 ug/L 100 116 70 130 3.7 20
Chloromethane 780 ug/L 100 78 70 130 1 20
Methylene chloride 880 ug/L 100 88 70 130 0.9 20
Surr:Dibromofluoromethane 100 102 70 130 0 10
Surf:p-Bromofluorobenzene 100 102 80 120 0 10
Surr:Toluene-dB 100 106 80 120 0 10
Surr:1,2-Dichlorobenzene-d4 100 101 80 120 0 10
Qualifiers:
RL -Analyte reporting limit.ND -Not detected at the reporting limit.
1_...."....._......."I I .....V .............................••................................................
comD::r1 ~()JJ (YJ /Adfj-<"PjfIJ
Name
,~;S,~~t;;~/11t Sample Origin EPA/State Compliance:
State:U-r Yes 0 No 0
Report Ma~.d$~ssB,?'JX g~r c0;z;;me4,/,ucL PhO~;r It§Email:Sampler:(Please Print)
II2I1-AI AI1)-,-(,~L;fAf %I.fslf #
Invoice Address:j Invoide Contact &Phone:Purchase Order:Quote/Bottle Order:
;::;'alM~~~
Special Report/Formats:&"[J:!]&"[1)J@O@ [KJ[]l®(\[J~'iJ'[]l[Q)..Contact ELI prior to Shipped by:
S RUSH sample submittal0Q;~O(J)£~;::-for charges and Cooler lD(s):
~CO~OI2 0 ;::R scheduling -See Cfr'-eAf0_>°>-ro W Instruction PageDOWDEOO/EOT(Electronic Data)l'l(J)(J)'"SCU>(J)I05:=~C':l ~"0 ReceiP~pDPOTW/wWTP Format:u °ae:0 <::Comments:_«0)105132 OJ UDState:D LEVEL IV o ~<::,~<{e °co.Q)e:0-I-m~~co.QODOther:D NELAC ~F'Slro '~<::('0'5 On Ice:
:::J Q)-=Q)5:l-Szo..«l~o W -e Custody Seal g~E >1 ~W m On BoUIe'"(j)"0(J)<::On CoolergjHIntact
SAMPLE IDENTIFICATION Collection Collection MATRIX Signature 0 N(Name,Location,Interval,etc.)Date Time Match
f-wN"-5!2-1/2 -2f ·07 fH60 6--Y0 !)(~
'-rwtV.--/tf IL 1/·2/·01 14:s1 I 'f ~CCAI2-D'"6 \)
TWill"t £.Oll.tJ1 13.3'Q ('f..\Ql
Hn"
':orII./N"/J(t2..'1·'1.(.09 M,$'"1 )Ix @))<=g
YwI'I-z./tl If7.J1./J9 II 11 /IX ~
TWIt/-,'5'17 ·7.1.tff /Jqll'J I IX ~
JrIAJN"J()7?n.m f'J1 r1J07i p \'y,Iq,,"'I/Ie;TIM....rIlJ£~
Y"IVN'!"'J.n·/)d8hf5 )Ix •~0
-rWN,,/f(1f7..22-tJ IMJ..~I IX ao.,:;;
JJrI1J11/"&I /1.-22,tfI 1~)(l(S-.5~W r'X.1/"\-r,.;~.{"Jh y (~...-~""
Custody Ke~by (pc;nt12.1 ~Da7?~~7_1r ,2',-at 7L'/Received by (print)"DalefTime:"'I 1fi(3-07 Signature:
Jl .1RecordRelinquisryooy(print):Date/Time:,/SignalUl'e"Received by (print)"DatelTime:Signature
MUST be
Signed 117L1V~;,r.«L3DoralOry:Ie ua:Q'~.)Cf /d'30~:------Samole 015005al:Return toClient:Lab Disposal:'''''A~)<!l--0 ~.:.-----,,--
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
I11111111111111111111111111111111111111111111111111111I
C09120811
Login completed by:Halley Ackerman
Reviewed by:
Reviewed Date:
Date and Time Received:12/23/200910:50 AM
Received by:al
Carrier name:FedEx
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 M pH acceptable upon receipt?
Contact and Corrective Action Comments:
None
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
4'C On Ice
Yes 0
Yes 0
No 0
No 0
No 0
No 0
No 0
No 0
No 0
No 0
No 0
No 0
No 0
No 0
Not Present 0
Not Present 0
Not Present 0
No VOA vials submitted 0
NotApplicable 0
ENERGYLABORA T0!1''''c;,INC.•2393SailCreek Highway (82601)•P.D.E!""3258 •Casper,WY82602
TollFree 888.235.0515 •,'35.0515 •Fax [phone] •casper@energyl,'m •www.energylab.com
CLIENT:Denison Mines (USA)Corp
Project:4th Quarter Chloroform
Sample Delivery Group:C09120811
ORIGINAL SAMPLE SUBMITIAL(S)
All original sample submittals have been returned with the data package.
Date:06-Jan-10
CASE NARRATIVE
SAMPLE TEMPERATURE COMPLIANCE:4°C (±2°C)
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 ifthere is evidence that the chilling process has
begun.
GROSS ALPHA ANALYSIS
Method 900.0 for gross alpha and gross beta is intended 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 ofexposure to
beginning ofcounting should not exceed 8 days.
SOIUSOLID 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 NO (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 ofthis 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 oforigin.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
ENERGYLABORATO ~s,INC..2393 Sail Creek Highway (82601)•P.O,3258 •Casper,WY82602
Toll Free 888.235.0515 •,235.0515 •Fax [phone] •casper@energy"com'www.energylab,com
ANALYTICAL SUMMARY REPORT
January 06,2010
Denison Mines (USA)Corp
6425 S Hwy 191
Blanding,UT 84511
Workorder No,:C09120647
Project Name:4th Quarter Chloroform
Quote iD:C2975 -Chioroform Sampling
Energy Laboratories,Inc,received the following 28 samples for Denison Mines (USA)Corp on 12/18/2009 for analysis,
--~~~~~~------------
Sample ID Client Sample ID Collect Date Receive Date Matrix Test
C09120647-001 TW4-15 12/14/0914:20 12/18/09 Aqueous Chloride
Nitrogen,Nitrate +Nitrite
SW8260B vacs,Standard List----
C09120647-002 MW-4 12/14/0914:00 12/18/09 Aqueous Same As Above
C09120647-003 TW4-19 12/14/0915:50 12/18/09 Aqueous Same As Above
C09120647-004 TW4-20 12/14/0913:25 12/18/09 Aqueous Same As Above
C09120647-005 TW4-3R 12/15/09 08:20 12/18/09 Aqueous Same As Above
C09120647-006 TW4-12R 12/15/09 09:40 12/18/09 Aqueous Same As Above
C09120647-007 TW4-13R 12/15/0911:1512/18/09 Aqueous Same As Above
C09120647-008 TW4-14R 12/15/0913:1312/18/09 Aqueous Same As Above---_.._....__.•..•..._._..
C09120647-009 TW4-25R 12/15/09 15:55 12/18/09 Aqueous Same As Above-_..•....~....•_..._.._..-._,._._._~-~
C09120647-010 TW4-23R 12/15/0914:1212/18/09 Aqueous Same As Above
C09120647-011 TW4-3 12/16/09 10:07 12/18109 Aqueous Same As Above
C09120647-012 TW4-12 12/16/09 08:27 12/18/09 Aqueous Same As Above
C09120647-013 TW4-13 12/16/09 08:36 12/18/09 Aqueous Same As Above
C09120647-014 TW4-14 12/16/09 08:45 12/18/09 Aqueous Same As Above
C09120647-015 TW4-17 12/16/09 13:46 12/18/09 Aqueous Same As Above
C09120647-016 TW4-23 12/16/0909:57 12/18/09 Aqueous Same As Above
C09120647-017 TW4-25 12/16/0907:41 12/18/09 Aqueous Same As Above
C09120647-018 TW4-8 12/1710909:3012/18/09 Aqueous Same As Above
C09120647-019 TW4-9 12/1710909:2212/18/09 Aqueous Same As Above
C09120647-020 TW4-16 12/17109 09:40 12/18/09 Aqueous Same As Above
C09120647-021 TW4-24 12/1710909:0612/18/09 Aqueous Same As Above
C09120647-022 TW4-8R 12/16/09 10:54 12/18/09 Aqueous Same As Above
C09120647-023 TW4-9R 12/16/0912:45 12/18/09 Aqueous Same As Above
C09120647-024 TW4-16R 12/16/0914:3212/18/09 Aqueous Same As Above
ENERGY LABORATq·"'s,INC••2393 SaltCreek Highway (82601)•P.0,·3258'Casper,WY82602
TollFrea 888.235.0515 •:235.0515 •Fax [phone] •casper@energy,•.com·www.energylab.com
ANALYTICAL SUMMARY REPORT
----------~--------------------------
C09120647-025 TW4-24R
C09120647-026 TW4-60
C09120647-027 TW4-65
C09120647-028 Trip Blank
12/16/09 16:15 12/18/09
12/17/0910:00 12/18/09
12/16/09 13:46 12/18/09
12/17/0900:0012/18109
Aqueous
Aqueous
Aqueous
Aqueous
Same As Above
Same As Above
Same As Above
SW8260B vacs,Standard List
As appropriate,any exceptions or problems with the analyses are noted in the Laboratory Analytical Report,the
QNQC Summary Report,or the Case Narrative.
If you have any questions regarding these tests results,please call.
ReportApproved By:
ENERGYLABORATQ"'~s,INC••2393 Salt Creek Highway (82601)•RO,.3258 •Casper,WY82602
TollFree 888.235.0515 •.235.0515 •Fax [phone] •casper@energf,.com'www.energylab.comPll!#fl'lb'f
'ft.f;-i"Mfi.ml¥'"-------------------------------------------
LASORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
ClientSample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-001
TW4-15
Report Date:01/06/10
Collection Date:12/14/0914:20
DateReceived:12/18/09
Matrix:Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 60 mg/L 1 A4500-CI B 12/28/0910:511ia
Nitrogen,Nitrate+Nitrite as N 2.3 m9/L 0.1 E353.2 12/28/09 13:221ial
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride ND ug/L 1.0 SW8260B 12/21/0916:461 ilr
Chloroform 1100 ug/L 500 SW8260B 12/23/09 13:20 I wen
Chloromethane ND ug/L 1.0 SW8260B 12/21/0916:461 ilr
Methylene chloride 40 ug/L 1.0 SW8260B 12/21/0916:461 ilr
Surr:Dibromofluoromethane 103 %REC 70-130 SW8260B 12/21/0916:461 ilr
Surr:p-Bromofluorobenzene 103 %REC 80-120 SW8260B 12/21/0916:461 ilr
Surr:Toluene-dB 99.0 %REC 80-120 SW8260B 12/21/0916:461 ilr
Surr:1,2~Dichlorobenzene-d4 109 %REC 80-120 SW8260B 12/21/0916:461 ilr
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORATO~'-:S,INC••2393SailCreek Highway (82601)•PO..3258 •Casper,WY82602
TollFree 888.235.0515 •.235.0515 •Fax [phone] •casper@energy,""'Om'www.energylab.com
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-002
MW-4
Report Date:01106/10
Collection Date:12/14/0914:00
DateReceived:12/18/09
Matrix:Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 44 mg/L 1 A4500-CI B 12/28/09 11 :03 /ia
Nitrogen,Nitrate+Nitrite as N 5.8 mg/L 0.2 E353.2 12/28/09 13:25/ial
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride 1.6 ug/L 1.0 SW8260B 12/22/09 04:36/ilr
Chloroform 1800 ug/L 100 SW8260B 12121/0915:00/jlr
Chloromethane ND ug/L 1.0 SW8260B 12/22/09 04:36/jlr
Methylene chloride ND ug/L 1.0 SW8260B 12/22/0904:36/jlr
Surr:Dibromofluoromethane 107 %REC 70-130 SW8260B 12/22/0904:36/jlr
Surr:pMBromofluorobenzene 105 %REC 80-120 SW8260B 12/22/0904:36/jlr
Surr:Toluene-dB 100 %REC 80-120 SW8260B 12122/0904:361jlr
Surr:1,2-Dichlorobenzene-d4 111 %REC 80-120 SW8260B 12/22/0904:36/jlr
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel M Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORATOr-"'s,INC_-2393SaIICreekHighway(82601)'P.D.:''3258'Casper,WY82602
lOllFree 888.235.0515 •.235.0515 •Fax [phone] -casper@energy,.X1m'www.energylab.com
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab ID:
Client Sample ID:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-003
TW4-19
Report Date:01/06/10
Collection Date:12/14/0915:50
DateReceived:12/18/09
Matrix:Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 124 mg/L 1 A4500-CI B 12/28/09 11:04 /ja
Nitrogen,Nitrate+Nitrite as N 26.7 mg/L 0.2 E353.2 12/28/09 13:27/jal
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride 16 ug/L 1.0 SW8260B 12/22/0905:12/jlr
Chloroform 4700 ug/L 1000 SW8260B 12/23/09 13:55/wen
Chloromethane ND ug/L 1.0 SW8260B 12/22/0905:12/jlr
Methylene chloride ND ug/L 1.0 SW8260B 12/22/0905:12/jlr
Surr:Dibromoftuoromethane 93.0 %REC 70-130 SW8260B 12/22/0905:12/jlr
Surr:p~Bromofluorobenzene 105 %REC 80-120 SW8260B 12/22/0905:12/jlr
Surr:Toluene-dB 102 %REC 80-120 SW8260B 12/22/0905:12/jlr
Surr:1,2-Dichlorobenzene-d4 108 %REC 80-120 SW8260B 12/22/0905:12/jlr
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORATOF'''S,INC.,2393Sail CreekHighway (82601)•P.O./'3258'Casper,WY82602
Toll Free 888.235.0515 •235.0515 •Fax [phone] •casper@energy../om'www.energylab.com
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-004
TW4-20
Report Date:01106110
Collection Date:12/14/09 13:25
DateReceived:12/18109
Matrix:Aqueous
MCL!
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 187 mg/L 1 A4500-CI B 12/28/09 11 :061 ia
Nitrogen,Nitrate+Nitrite as N 5.3 mg/L 0.1 E353.2 12/28/09 13:30 I ial
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride 14 ug/L 1.0 SW8260B 12/22/0905:471ilr
Chloroform 15000 ug/L 1000 SW8260B 12/23/0914:30 I wen
Chloromethane ND ug/L 1.0 SW8260B 12122/09 05:47 I ilr
Methylene chloride 3.0 ug/L 1.0 SW8260B 12/22/09 05:47 I ilr
Surr:Dibromofluoromethane 66.0 %REC S 70-130 SW8260B 12/22/0905:471jlr
Surr:p-Bromofluorobenzene 106 %REC 80-120 SW8260B 12/22/0905:471ilr
Surr:Toluene-dB 104 %REC 80-120 SW8260B 12/22/09 05:47 I ilr
Surr:1,2-Dichlorobenzene-d4 107 %REC 80-120 SW8260B 12/22/09 05:47 1ilr
Report
Definitions:
RL -Analyte reporting limit.
Qel -Quality control limit.
S -Spike recovery outside of advisory limits.
Mel -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORATCJP'~S,INC••2393Sail CreekHighway (82601)'PD.r ·3258·Casper,WY82602
Toll Free 888.235.0515 •235.0515 •Fax [phone] •casper@energy,.om'www.energylab.com
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab ID:
Client Sample ID:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-005
TW4-3R
Report Date:01/06/10
Collection Date:12/15/09 08:20
DateReceived:12/18/09
Matrix:Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride ND mglL 1 A4500-CI B 12/28/09 11 :081 ja
Nitrogen,Nitrate+Nitrite as N ND mglL 0.1 E353.2 12/28/0913:40 I jal
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1.0 SW8260B 12/22/0915:081 wen
Chloroform NO ug/L 1.0 SW8260B 12/22/0915:081 wen
Chloromethane NO ug/L 1.0 SW8260B 12/22/0915:08/wen
Methylene chloride NO ug/L 1.0 SW8260B 12/22/09 15:08 /wen
Surr;Dibromofluoromethane 106 %REC 70-130 SW8260B 12/22/09 15:08/wen
Surf:p-Bromofluorobenzene 112 %REC 80-120 SW8260B 12/22/0915:081 wen
Surr:Toluene-dB 105 %REC 80-120 SW8260B 12/22/09 15:08/wen
Surr:1,2-Dichlorobenzene-d4 102 %REC 80-120 SW8260B 12/22/09 15:081 wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel-Maximum contaminant level.
ND -Not detected at the reporting limit
ENERGYLABORATO!"""5,INC.•2393 Salt Creek Highway(82601)•P.Of-3258 •Casper,WY82602rollFree888.235.0515 •"235.0515'Fax [phone] •casper@energyi,om'www.energy/ab.com
LASaRATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-006
TW4-12R
Report Date:
Collection Date:
OateReceived:
Matrix:
01/06/10
12/15/09 09:40
12/18/09
Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 1 mg/L 1 A4500-CI B 12/28/0911:11/ja
Nitrogen,Nitrate+Nitrite as N NO mg/L 0.1 E353.2 12/28/0913:421 jal
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1.0 SW8260B 12/22/09 15:431 wen
Chloroform 6.1 ug/L 1.0 SW8260B 12/22/09 15:431 wen
Chloromethane NO ug/L 1.0 SW8260B 12/22/09 15:431 wen
Methylene chloride NO ug/L 1.0 SW8260B 12/22/09 15:431 wen
Surr:Dibromofluoromethane 104 %REC 70-130 SW8260B 12/22/09 15:431 wen
Surr:p-Bromofluorobenzene 108 %,REC 80-120 SW8260B 12/22/09 15:431 wen
Surr:Toluene-dB 105 %REC 80-120 SW8260B 12/22/09 15:431 wen
Surr:1,2~Dichlorobenzene-d4 104 %REC 80-120 SW8260B 12/22/09 15:431 wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel-Maximum contaminant level.
ND -Not detected at the reporting limit.
ENERGYLASORATOIr=s,INC••2393 Salt Creek Highway (82601)•P.0.E'--.3258 •Casper,WY82602
TollFree 888.235.0515 •l ?35.0515 •Fax [phone] •[e-mail] •www.energylab.com
LASORATORY ANALYTICAL REPORT
Client:
Project:
Lab ID:
Client Sample ID:
Denison Mines (USA)Corp
4th Quarter Chioroform
C09120647-007
TW4-13R
Report Date:
Collection Date:
DateReceived:
Matrix:
01/06/10
12/15/0911:15
12/18/09
Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride NO mg/L 1 A4500-CI B 12/28/0911:14/ja
Nitrogen,Nitrate+Nitrite as N NO mg/L 0.1 E353.2 12/28/09 13:47 I jal
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1.0 SW8260B 12/22/0916:18/wen
Chloroform NO ug/L 1.0 SW8260B 12/22/0916:18/wen
Chloromethane NO ug/L 1.0 SW8260B 12/22/0916:18/wen
Methylene chloride NO ug/L 1.0 SW8260B 12/22/0916:18/wen
Surr:Dibromofluoromethane 104 %REC 70-130 SW8260B 12/22/0916:18/wen
Surr:p-Bromofluorobenzene 108 %REC 80-120 SW8260B 12/22/0916:18/wen
Surr:Toluene~d8 102 %REC 80-120 SW8260B 12/22/0916:18/wen
Surr:1.2-Dichlorobenzene~d4 106 %REC 80-120 SW8260B 12/22/0916:18/wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORATO!1'''"S,INC.•2393Sa/I Creek Highway (82601)•PO.B'"3258 'Casper,WY82602
70//Free 888.235.0515 •i '35.0515 •Fax [phone] •[e-mail]'www.energylab,com
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-008
TW4-14R
Report Date:01106/10
Collection Date:12/1510913:13
DateReceived:12/18/09
Matrix:Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 1 mg/L 1 A4500-CI B 12/28109 11 :151ia
Nitrogen,Nitrate+Nitrite as N ND mg/L 0.1 E353.2 12/28/09 13:50 Iial
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride ND ug/L 1.0 SW8260B 12/22/0916:531 wen
Chloroform ND ug/L 1.0 SW8260B 12/22/09 16:531 wen
Chloromethane ND ug/L 1.0 SW8260B 12/22/09 16:531 wen
Methylene chloride ND ug/L 1.0 SW8260B 12/22/09 16:531 wen
Surf:Dibromofluoromethane 99.0 %REC 70-130 SW8260B 12/22/09 16:531 wen
Surr:p~Bromofluorobenzene 104 %REC 80-120 SW8260B 12/22/09 16:531 wen
Surr:Toluene~d8 104 %REC 80-120 SW8260B 12/22/0916:531 wen
Surr:1,2-Dichlorobenzene-d4 103 %REC 80-120 SW8260B 12/22/0916:531 wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORAT0'1,E:$,INC••2393Sal/CreekHighway (82601)•PD.'1""3258 •Casper,WY82602
TollFree 888.235.0515 •,?35.0515 •Fax [phone] •casper@energyli Jm •www.energylab.com
LASORATORY ANALYTICAL REPORT
Client:
Project:
Lab ID:
Client Sample ID:
Denison Mines (USA)Corp
4th Quarter Chioroform
C09120647-009
TW4-25R
Report Date:
Collection Date:
DateReceived:
Matrix:
01/06/10
12/15/0915:55
12/18/09
Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride ND mg/L 1 A4500-CI B 12/28/0911:171 ja
Nitrogen,Nitrate+Nitrite as N ND mg/L 0.1 E353.2 12/28/09 13:521 jal
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride ND ug/L 1.0 SW8260B 12/22/09 17:281 wen
Chloroform ND ug/L 1.0 SW8260B 12/22/09 17:281 wen
Chloromethane ND ug/L 1.0 SW8260B 12/22/09 17:281 wen
Methylene chloride ND ug/L 1.0 SW8260B 12/22/09 17:281 wen
Surr:Dibromofluoromethane 101 %REC 70-130 SW8260B 12/22/09 17:281 wen
Surr:pRBromofluorobenzene 106 %REC 80-120 SW8260B 12/22/09 17:281 wen
Surr:Toluene~d8 104 %REC 80-120 SW8260B 12/22/09 17:281 wen
Surr:1,2-Dichlorobenzene-d4 104 %REC 80-120 SW8260B 12/22/09 17:281 wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel-Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORATOR/&;<;,INC.•2393 Salt CreekHighway (82801)•P.0 E1~".J258 •Casper,WY82802
7iJII Free 888.235.0515 •J '35.0515 •Fax [phone] •casper@energYk 1m'www.energylab.com
LASORATORY ANALYTICAL REPORT
Client:
Project:
Lab ID:
ClientSample 10:
Denison Mines (USA)Corp
41h Quarter Chloroform
C09120647-010
TW4-23R
Report Date:
Collection Date:
DateReceived:
Matrix:
01/06110
12/15/0914:12
12/18/09
Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 1 mg/L 1 A4500-CI B 12/28/0911:19/ja
Nitrogen,Nitrate+Nitrite as N NO m9/L 0.1 E353.2 12/28/0914:02/jal
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1.0 SW8260B 12/22/09 18:03 I wen
Chloroform 1.7 ug/L 1.0 SW8260B 12/22/09 18:03 I wen
Chloromethane NO ug/L 1.0 SW8260B 12/22/0918:031 wen
Methylene chloride NO U9/L 1.0 SW8260B 12/22/09 18:03 I wen
Surf:Dibromofluoromethane 105 %REC 70-130 SW8260B 12/22/09 18:031 wen
Surf;p-Bromofluorobenzene 105 %REC 80-120 SW8260B 12/22/0918:031 wen
Surr:Toluene-dB 104 %REC 80-120 SW8260B 12/22/09 18:031 wen
Surf:1,2-Dichlorobenzene-d4 104 %REC 80-120 SW8260B 12/22/09 18:031 wen
Report
Definitions:
RL -Analyte reporting limit.
Oel -Quality control limit.
MeL -Maximum contaminant level.
ND -Not detected at the reporting limit.
ENERGYLABORATORI"'C;,INC••2393 SailCreekHighway (82601)'Po.~f'''1258 •Casper,WY82602
TollFree 888.235.0515 •j 35.0515'Fax [phone] •casper@energyle m •www.energylab.com
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample ID:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-011
TW4-3
Report Date:01/06/10
Collection Date:12/16/0910:07
DateReceived:12/18/09
Matrix:Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 22 mg/L 1 A4500-cr B 12/28/09 11 :22 /ia
Nitrogen,Nitrate+Nitrite as N 2.5 mg/L 0.1 E353.2 12/28/0914:05/iar
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride ND ug/L 1.0 SW8260B 12/23/09 12:451 wen
Chloroform ND uglL 1.0 SW8260B 12/23/09 12:45/wen
Chloromethane ND uglL 1.0 SW8260B 12/23/09 12:45/wen
Methylene chloride ND uglL 1.0 SW8260B 12123/09 12:451 wen
Surr:Dibromofluoromethane 104 %REC 70-130 SW8260B 12123/09 12:451 wen
Surr:p-Bromofluorobenzene 105 %REC 80-120 SW8260B 12123/09 12:45 I wen
Surr:Toluene-dB 102 %REC 80-120 SW8260B 12123/09 12:45/wen
Surr:1,2-Dichlorobenzene~d4 104 %REC 80-120 SW8260B 12123/09 12:45 I wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel-Maximum contaminant level.
ND -Not detected at the reporting limit.
ENERGYLABORATORI"9,INC••2393SaltCreekHighway (82601)•P.D.Sr .1258 •Casper,WY82602
TollFree 888.235.0515 •S '35.0515'Fax [phone] •casper@energy/~m •www.energylab.com
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-012
TW4-12
Report Date:01/06/10
Collection Date:12/16/0908:27
DateReceived:12/18/09
Matrix:Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 23 mg/L 1 A4500-CI B 12/28/09 11:30 I ja
Nitrogen,Nitrate+Nitrite as N 3.6 mg/L 0.1 E353.2 12/28/0914:07/jal
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1.0 SW8260B 12/21/0917:56/jlr
Chloroform NO ug/L 1.0 SW8260B 12/21/0917:56/jlr
Chloromethane NO ug/L 1.0 SW8260B 12/21/09 17:56I jlr
Methylene chloride NO ug/L 1.0 SW8260B 12/21/0917:56/jlr
Surr:Dibromofluoromethane 105 %REC 70-130 SW8260B 12/21/0917:56/jlr
Surf:p-Bromofluorobenzene 103 %REC 80-120 SW8260B 12/21/0917:56/jlr
Surf:Toluene-dB 98.0 %REC 80-120 SW8260B 12/21/0917:561 jlr
Surr:1,2MDichlorobenzene-d4 110 %REC 80-120 SW8260B 12/21/0917:561 jlr
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
MeL -Maximum contaminant level.
ND -Not detected at the reporting limit.
ENERGYLABORATORI1"9,INC••2393 Sail Creek Highway (82601)'P.O.8p"8258 •Casper,WY82602
TollFree 888.235.0515 •j 35.0515 •Fax [phone] •casper@energyl",m •www.energylab.com
LASORATORY ANALYTICAL REPORT
Client:
Project:
Lab ID:
Client Sample ID:
Denison Mines (USA)Corp
4th Quarter Chioroform
C09120647-013
TW4-13
Report Date:
Collection Date:
DateReceived:
Matrix:
01/06/10
12/16/09 08:36
12/18/09
Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chlo,ide 60 mg/L 1 A4500-CI B 12/28/0911:31/ia
Nitrogen,Nitrate+Nitrite as N 4.1 mg/L 0.1 E353.2 12/28/0914:10 I ial
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1.0 SW8260B 12/21/09 18:321 ii'
Chloroform NO ug/L 1.0 SW8260B 12/21/0918:321 ii'
Chloromethane NO ug/L 1.0 SW8260B 12/21/0918:321ii'
Methylene chloride NO ug/L 1.0 SW8260B 12/21/09 18:321ii'
Surr:Dibromofluoromethane 102 %REC 70-130 SW8260B 12/21/0918:32/ii'
Surr:p~Bromofluorobenzene 103 %REC 80-120 SW8260B 12/21/0918:32/ilr
Surr:Toluene-dB 98.0 %REC 80-120 SW8260B 12/21/0918:32/ii'
Surr:1,2-Dichlorobenzene-d4 110 %REC 80-120 SW8260B 12/21/0918:32/ii'
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel-Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORATORIF"I.INC••2393 SailCreek Highway (82601)•P.O.Boy 1258 •Casper,WY82602
TollFree 888.235.0515 •3,15.0515'Fax [phone] •casper@energylaJ n •www.energylab.com
LASaRATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-014
TW4-14
Report Date:
Collection Date:
DateReceived:
Matrix:
01/06/10
12/16/09 08:45
12/18/09
Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 34 mg/L 1 A4500-CI B 12/28/09 11 :33 I ia
Nitrogen,Nitrate+Nitrite as N 1.4 mg/L 0.1 E353.2 12128/09 14:121 iai
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride ND ug/L 1.0 SW8260B 12/21/09 19:071 ilr
Chloroform ND ug/L 1.0 SW8260B 12/21/0919:071 ilr
Chloromethane ND ug/L 1.0 SW8260B 12/21/0919:071ilr
Methylene chloride ND ug/L 1.0 SW8260B 12/21/0919:071ilr
Surr:Dibromofluoromethane 109 %REC 70-130 SW8260B 12/21/0919:071jlr
Surr:p~Bromofluorobenzene 104 %REC 80-120 SW8260B 12/21/0919:071jlr
Surr:Toluene-dB 98.0 %REC 80-120 SW8260B 12/21/0919:071jlr
Surr:1.2-Dichlorobenzene~d4 110 %REC 80-120 SW8260B 12/21/0919:071jlr
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
MeL -Maximum contaminant level.
ND -Not detected at the reporling limit.
ENERGYLABORATORIFc;.INC••2393SailCreek Highway (8260I)'PO 89v ~258 .Casper,WY82602
TOilFree 888.235.0515 •3i 15.0515 •Fax [phone] •casper@energyla;".www.energylab.com
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-015
TW4-17
Report Date:01/06/10
Collection Date:12/16/0913:46
DateReceived:12/18/09
Matrix:Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 34 mg/L 1 A4500-CI B 12/28/09 11 :351ja
Nitrogen,Nitrate+Nitrite as N NO mg/L 0.1 E353.2 12/28/0914:20 Ijal
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1.0 SW8260B 12/22/09 13:241 wen
Chloroform NO ug/L 1.0 SW8260B 12/22/09 13:241 wen
Chloromethane NO ug/L 1.0 SW8260B 12/22/09 13:241 wen
Methylene chloride NO ug/L 1.0 SW8260B 12/22/09 13:241 wen
Surr:Dibromofluoromethane 119 %REC 70-130 SW8260B 12/22/09 13:241wen
Surr:p·Bromofluorobenzene 113 %REC 80-120 SW8260B 12/22/09 13:241 wen
Surr:Toluene·d8 104 %REC 80-120 SW8260B 12/22/09 13:241 wen
Surr:1,2-Dichlorobenzene-d4 109 %REC 80-120 SW8260B 12/22/09 13:241 wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORATORIF~.INC••2393Sal/CreekHighway (82601)'P.O.Bo'°'258 •Casper,WY82602
Toll Free 888.235.0515 •3,'5.0515'Fax [phone] •casper@energylal 7'www.energylab.com
LASORATORY ANALYTICAL REPORT
Client:
Project:
Lab ID:
Client Sample ID:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-016
TW4-23
Report Date:
Collection Date:
DateReceived:
Matrix:
01/06/10
12/16/09 09:57
12/18/09
Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 37 mg/L 1 A4500-CI B 12/28/09 11 :37 I ja
Nitrogen,Nitrate+Nitrite as N ND mg/L 0.1 E353.2 12/28/0914:221jal
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride ND ug/L 1.0 SW8260B 12/22/09 13:581 wen
Chloroform ND ug/L 1.0 SW8260B 12/22/09 13:581 wen
Chloromethane ND ug/L 1.0 SW8260B 12/22/09 13:581wen
Methylene chloride ND ug/L 1.0 SW8260B 12/22/09 13:581wen
Surr:Dibromofluoromethane 115 %REC 70-130 SW8260B 12/22/09 13:581wen
SUfr:p~Bromofluorobenzene 111 %REC 80-120 SW8260B 12/22/09 13:581wen
Surr:Toluene-dB 105 %REC 80-120 SW8260B 12/22/09 13:581wen
Surr:1,2-Djchlorobenzene~d4 106 %REC 80-120 SW8260B 12/22/09 13:581wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel -Maximum contaminant level.
ND -Not detected at the reporting limit.
ENERGYLABORATORJ"'S,INC••2393 SailCreekHighway(82601)•RD.8 r .•1258 •Casper,WY82602
Toll Free 888.235.0515 •~'35.0515'Fax [phone] •casper@energyl!m'www.energylab.com
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-017
TW4-25
Report Date:01/06/10
Collection Date:12/16/0907:41
DateReceived:12/18/09
Matrix:Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 371 mg/L 1 A4500-CI B 12/28/09 11 :40 1ia
Nitrogen,Nitrate+Nitrite as N 14.2 mg/L 0.2 E353.2 12/28/0914:251ial
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1.0 SW8260B 12/22/09 14:331wen
Chloroform NO ug/L 1.0 SW8260B 12/22/09 14:331wen
Chloromethane NO ug/L 1.0 SW8260B 12/22/09 14:331wen
Methylene chloride NO ug/L 1.0 SW8260B 12/22/09 14:331wen
Surr:Dibromofluoromethane 107 %REC 70-130 SW8260B 12/22/09 14:331wen
Surr:p-Bromofluorobenzene 112 %REC 80-120 SW8260B 12/22/09 14:331wen
Surf:Toluene-dB 105 %REC 80-120 SW8260B 12/22/0914:33/wen
Surf:1,2-Dichlorobenzene-d4 106 %REC 80-120 SW8260B 12/22/0914:33/wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel-Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORATORI£"INC••2393Sa/I Creek Highway(82601)'P.O.BoxO?58 •Casper,WY82602
To//Free 888.235.0515 •30;:0515,Fax [phone] •casper@energylab.'•www.energylab.com
LASORATORY ANALYTICAL REPORT
Client:
Project:
Lab ID:
Client Sample ID:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-018
TW4-8
Report Date:
Collection Date:
DateReceived:
Matrix:
01/06/10
12/17/0909:30
12118/09
Aqueous
MCLt
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 51 mglL 1 A4500-Cl B 12/28/09 11 :42 I ia
Nitrogen,Nitrate+Nitrite as N NO mglL 0.1 E353.2 12/28/0914:271ial
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1.0 SW8260B 12/22/09 18:38 I wen
Chloroform NO ug/L 1.0 SW8260B 12/2210918:381 wen
Chloromethane NO ug/L 1.0 SW8260B 12/22/0918:381 wen
Methylene chloride NO ug/L 1.0 SW8260B 12/22/09 18:38 I wen
Surr:Dibromofluoromethane 106 %REC 70-130 SW8260B 12/22/0918:381 wen
Surr:p-Bromofluorobenzene 104 %REC 80-120 SW8260B 12/22/0918:381 wen
Surr:Toluene-d8 102 %REC 80-120 SW8260B 12/22/0918:381 wen
Surr:1,2-Dichlorobenzene-d4 102 %REC 80-120 SW8260B 12/22/09 18:381 wen
Report
Definitions:
RL -Analyte reporting limit.
OCL -Quality control limit.
Mel -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORATOR/~f"INC••2393Sail Creek Highway (82801)•Po.Box3?58 •Casper,WY 82802
701/Free 888.235.0515 •30i :0515 •Fax [phone] •casper@energylab.:•www.energylab.com
LASORATORY ANALYTICAL REPORT
Client:
Project:
Lab ID:
Client Sample ID:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647·019
TW4-9
Report Date:
Collection Date:
DateReceived:
Matrix:
01/06/10
12/17/0909:22
12/18/09
Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 37 mg/L 1 A4500-CI B 12/28/09 11 :44 /ia
Nitrogen,Nitrate+Nitrite as N 1.7 mg/L 0.1 E353.2 12/28/0914:30/ial
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride ND uglL 1.0 SW8260B 12/22/09 22:43 /wen
Chloroform ND uglL 1.0 SW8260B 12122/09 22:43 /wen
Chloromethane ND uglL 1.0 SW8260B 12/22/09 22:43 /wen
Methylene chloride ND uglL 1.0 SW8260B 12/22/09 22:43 /wen
Surr:Dibromofluoromethane 104 %REC 70-130 SW8260B 12122/09 22:43 /wen
Surr:p-Bromofluorobenzene 101 %REC 80-120 SW8260B 12/22/09 22:43 /wen
Surr:Toluene-dB 104 %REC 80-120 SW8260B 12122/09 22:43 /wen
Surr:1,2-Dichlorobenzene-d4 103 %REC 80-120 SW8260B 12122/09 22:43 /wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORATORIE;c INC••2393Sail CreekHighway (82601)•P.0.Box.01.,8 •Casper,WY82602
7011Free 888.235.0515 •30i :0515 •Fax [phone] •casper@energylab.i •www.energylab.com
LASORATORY ANALYTICAL REPORT
Client:
Project:
Lab ID:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-020
TW4-16
Report Date:01106/10
Collection Date:12/1710909:40
DateReceived:12/18/09
Matrix:Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 76 mg/L 1 A4500-CI B 12/28/09 11 :451ia
Nitrogen,Nitrate+Nitrite as N 5.2 mg/L 0.2 E353.2 12/28/0914:40 I ial
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride ND ug/L 1.0 SW8260B 12/22/09 19:481wen
Chloroform ND ug/L 1.0 SW8260B 12/22/09 19:481wen
Chloromethane ND ug/L 1.0 SW8260B 12122/09 19:481wen
Methylene chloride ND uglL 1.0 SW8260B 12122/09 19:481wen
Surr:Dibromofluoromethane 114 %REC 70-130 SW8260B 12122/09 19:481wen
Surr:p-Bromofluorobenzene 107 %REC 80-120 SW8260B 12122/09 19:481wen
Surr:Toluene-dB 104 %REC 80-120 SW8260B 12122/09 19:481wen
Surr:1,2-Dichlorobenzene-d4 107 %REC 80-120 SW8260B 12122/09 19:481wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORATORIF<:,INC••2393Sail CreekHighway (82601),P.0.So·1258 •Casper,WY82602
TollFree 688.235.0515 '8,15.0515'Fax [phone] •casper@energyla.n •www.energylab.comJ#jm{i,7
It#meJ;?!:"iot;Pit'_
LASORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-021
TW4-24
Report Date:
Collection Date:
DateReceived:
Matrix:
01106/10
12/1710909:06
12/18/09
Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 1080 mg/L 1 A4500-CI B 12/28/09 11:59/ia
Nitrogen,Nitrate+Nitrite as N 28.3 mg/L D 0.3 E353.2 12/28/0914:421ial
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride ND ug/L 1.0 SW8260B 12/22/0923:531 wen
Chloroform 1.2 ug/L 1.0 SW8260B 12/22/0923:531 wen
Chloromethane ND ug/L 1.0 SW8260B 12/22/0923:531 wen
Methylene chloride ND ug/L 1.0 SW8260B 12/22/0923:531 wen
Surr:Dibromofluoromethane 111 %REC 70-130 SW8260B 12/22/0923:531 wen
Surr:p-Bromofluorobenzene 102 %REC 80-120 SW8260B 12/22/0923:531 wen
Surr:Toluene-dB 102 %REC 80-120 SW8260B 12/22/09 23:531 wen
Sure 1,2-Dichlorobenzene-d4 106 %REC 80-120 SW8260B 12/22/09 23:531 wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
o-RL increased due to sample matrix interference.
Mel -Maximum contaminant level.
ND -Not detected at the reporting limit
ENERGYLABORATORIE/':INC.•2393SaIl Creek Highway(82601)•P.0.80,"8:;58 •Casper,WY82602
TollFree 888.235.0515 •30;:0515 •Fax [phone] •casper@energylab.•www.energylab.com
LASORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-022
TW4-8R
Report Date:
Collection Date:
DateReceived:
Matrix:
01106/10
12/16/09 10:54
12/18/09
Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride NO mg/L 1 A4500-CI B 12/28/09 12:11 I ia
Nitrogen,Nitrate+Nitrlte as N NO mg/L 0.1 E353.2 12/28/09 14:451ial
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1.0 SW8260B 12/23/0900:281 wen
Chloroform NO ug/L 1.0 SW8260B 12/23/0900:281 wen
Chloromethane NO ug/L 1.0 SW8260B 12/23/09 00:281 wen
Methylene chloride NO ug/L 1.0 SW8260B 12/23/09 00:281 wen
$urr:DibromofJuoromethane 107 %REC 70-130 SW8260B 12/23/0900:281wen
Surr:p-Bromofluorobenzene 106 %REC 80-120 SW8260B 12/23/09 00:281 wen
Surr:Toluene-dB 103 %REC 80-120 SW8260B 12/23/0900:281 wen
Surr:1,2-Dichtorobenzene-d4 107 %REC 80-120 SW8260B 12/23/09 00:281 wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel -Maximum contaminant level.
ND -Not detected at the reporting limit.
ENERGYLABORATORIE."WC••2393 Sail Creek Highway (82601)•P.O.Bo~3:J58 •Casper,WY82602
7iJ11Free 888.235.0515 •30!.:0515 •Fax [phone] •casper@energylab.•www.energylab.com
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample ID:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-023
TW4-9R
Report Date:01/06/10
Collection Date:12/16109 12:45
DateReceived:12/18/09
Matrix:Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride NO mg/L 1 A4500-CI B 12/28/0912:121 ja
Nitrogen,Nitrate+Nitrite as N NO mg/L 0.1 E353.2 12/28/0914:471 jal
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1.0 SW8260B 12/23/0901 :03/wen
Chloroform NO ug/L 1.0 SW8260B 12/23/09 01 :03/wen
Chloromethane NO ug/L 1.0 SW8260B 12/23/09 01 :03/wen
Methylene chloride NO ug/L 1.0 SW8260B 12/23/09 01 :031 wen
Surr:DibromofJuoromethane 103 %REC 70-130 SW8260B 12/23109 01 :031 wen
Surf:p-Bromofluorobenzene 106 %REC 80-120 SW8260B 12/23/0901 :031 wen
Surr:Toluene-dB 103 %REC 80-120 SW8260B 12/23/09 01 :031 wen
Surr:1,2-Dichlorobenzene-d4 106 %REC 80-120 SW8260B 12/23/09 01 :03/wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORATORIEf'INC••2393Salt CreekHighway (82801)'p.D.80)(3:>58 •Casper,WY82802
TollFree 888.235.0515 •30;:0515 •Fax [phone] •casper@energylab.(•www.energylab.com
LASORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-024
TW4-16R
Report Date:
Collection Date:
DateReceived:
Matrix:
01106/10
12/16/0914:32
12/18/09
Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride NO mg/L 1 A4500-CI B 12/28/0912:14/ia
Nitrogen,Nitrate+Nitrite as N NO mg/L 0.1 E353.2 12/28/0914:50/ial
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1.0 SW8260B 12/23/09 01 :38/wen
Chloroform NO ug/L 1.0 SW8260B 12/23/09 01 :38/wen
Chloromethane NO ug/L 1.0 SW8260B 12/23/09 01 :38/wen
Methylene chloride NO ug/L 1.0 SW8260B 12/23/09 01 :38/wen
Surr:Dibromofluoromethane 107 %REC 70-130 SW8260B 12/23/0901:38/wen
Surr:p-Bromofluorobenzene 105 %REC 80-120 SW8260B 12/23/09 01 :38/wen
Surr:Toluene-dB 105 %REC 80-120 SW8260B 12/23/09 01 :38/wen
Surr:1,2-Dichlorobenzene-d4 104 %REC 80-120 SW8260B 12/23/09 01 :38 I wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel-Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORATORIF~.INC••2393Salt Creek Highway (82601)'Po.BqY 9258 •Casper,WY82602
milFree 888.235.0515 •3f '5.0515 •Fax [phone] •casper@energylai 7'www.energylab.com
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample ID:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-025
TW4-24R
Report Date:01/06/10
Collection Date:12/16/0916:15
DateReceived:12/18/09
Matrix:Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis DateI By
MAJOR IONS
Chloride NO mg/L 1 A4500-CI B 12/28/0912:161ja
Nitrogen,Nitrate+Nitrite as N NO mg/L 0.1 E353.2 12/28/0915:00 I jal
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1.0 SW8260B 12/23/09 02:13 I wen
Chloroform NO ug/L 1.0 SW8260B 12/23/09 02:13 I wen
Chloromethane NO ug/L 1.0 SW8260B 12/23/09 02:13 I wen
Methylene chloride NO ug/L 1.0 SW8260B 12/23/09 02:13 I wen
Surr:Dibromofluoromethane 106 %REC 70-130 SW8260B 12/23/0902:13/wen
Surr:p-Bromofluorobenzene 108 %REC 80-120 SW8260B 12/23/0902:131 wen
Surr:Toluene-d8 103 %REC 80-120 SW8260B 12/23/0902:131 wen
Surr:1,2-Dichlorobenzene-d4 107 %REC 80-120 SW8260B 12/23/09 02:131 wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel -Maximum contaminant level.
NO -Not detected at the reporting limit.
ENERGYLABORATORIFC:.INC••2393Sal/CreekHighway (82601)'PD.BoY ~258 .Casper,WY82602
TollFree 888.235.05/5 •36 '5.0515 •Fax [phone] •casper@energylaL 7'www.energylab.comPIlJ:ftlifj'fU"iel;t''''.Up¥''_
LASORATORY ANALYTICAL REPORT
Client:
Project:
Lab 10:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-026
TW4-60
Report Date:
Collection Date:
DateReceived:
Matrix:
01106/10
12/17/0910:00
12/18/09
Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 1 mg/L 1 A4500-CI B 12/28/0912:181 ia
Nitrogen,Nitrate+Nitrite as N NO mg/L 0.1 E353.2 12/28/09 15:021 ial
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO uglL 1.0 SW8260B 12/23/09 02:481 wen
Chloroform NO uglL 1.0 SW8260B 12/23/09 02:48/wen
Chloromethane NO uglL 1.0 SW8260B 12123/09 02:48/wen
Methylene chloride NO uglL 1.0 SW8260B 12123/09 02:48/wen
Surr:Dibromofluoromethane 108 %REC 70-130 SW8260B 12/23/09 02:48/wen
SUfr:p-Bromofluorobenzene 105 %REC 80-120 SW8260B 12123/09 02:48/wen
Surr:Toluene-dB 106 %REC 80-120 SW8260B 12/23/0902:48/wen
Surr:1,2-Dichlorobenzene-d4 103 %REC 80-120 SW8260B 12/23/0902:48 I wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel -Maximum contaminant level.
ND -Not detected at the reporting limit.
ENERGYLABORATORIF<;,INC••2393 Salt Creek Highway (82801)•P.O.Bpv 9258 •Casper,WY82802
lOllFree 888.235.0515 •3(15.0515 •Fax [phone] •casper@energyl",n'www.energylab.com
LABORATORY ANALYTICAL REPORT
Client:
Project:
Lab ID:
Client Sample 10:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-027
TW4-65
Report Date:01/06/10
Collection Date:12/16/09 13:46
DateReceived:12/18/09
Matrix:Aqueous
MCU
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
MAJOR IONS
Chloride 33 mg/L 1 A4500-CI B 12/28/09 12:20 Iia
Nitrogen,Nitrate+Nitrite as N NO m9/L 0.1 E353.2 12/28/0915:051 ial
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1.0 SW8260B 12/2310903:231 wen
Chloroform NO ug/L 1.0 SW8260B 12/23/0903:231 wen
Chloromethane NO ug/L 1.0 SW8260B 12/23/0903:231 wen
Methylene chloride NO ug/L 1.0 SW8260B 12/23/0903:231 wen
Surr:DibromofJuoromethane 113 %REC 70-130 SW8260B 12/23/0903:231 wen
Surr:p-Bromofluorobenzene 104 %REC 80-120 SW8260B 12/23/0903:231 wen
Surr:Toluene-dB 101 %REC 80-120 SW8260B 12/23/09 03:231 wen
Surr:1,2~Dichlorobenzene-d4 109 %REC 80-120 SW8260B 12/23/09 03:231 wen
Report
Definitions:
RL -Analyte reporting limit.
OCL ~Quality control limit.
Mel -Maximum contaminant level.
ND -Not detected at the reporting limit.
ENERGYLABORATOR/f"S,INC••2393Sail CreekHighway (82601)'PD.Bp"9258 •Casper,WY82602
Toll Free 888.235.0515 •3,J5.0515·Fax [phone] •casper@energyla:77'www.energylab.com
LASORATORY ANALYTICAL REPORT
Client:
Project:
Lab ID:
Client Sample ID:
Denison Mines (USA)Corp
4th Quarter Chloroform
C09120647-028
Trip Blank
Report Date:
Collection Date:
DateReceived:
Matrix:
01106/10
12117/09
12118/09
Aqueous
MCLt
Analyses Result Units Qualifier RL QCL Method Analysis Date I By
VOLATILE ORGANIC COMPOUNDS
Carbon tetrachloride NO ug/L 1.0 SW8260B 12/22/09 19:13 /wen
Chloroform NO ug/L 1.0 SW8260B 12/22/09 19:13 /wen
Chloromethane NO ug/L 1.0 SW8260B 12/22/09 19:13 /wen
Methylene chloride NO ug/L 1.0 SW8260B 12/22/09 19:13 /wen
Surr:Dibromofluoromethane 101 %REC 70-130 SW8260B 12/22/09 19:13 I wen
Surr:p-Bromofluorobenzene 106 %REC 80-120 SW8260B 12/22/09 19:13 I wen
Surr:ToluenewdB 101 %REC 80-120 SW8260B 12/22/09 19:13 /wen
Surr:1,2-Dichlorobenzene-d4 104 %REC 80-120 SW8260B 12/22/09 19:13 /wen
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Mel -Maximum contaminant level.
ND -Not detected at the reporting limit.
ENERGYLABORATOBIE5,INC••2393 Sal/Creek Highway (82601)'PD.,~·v 3258 •Casper,WY82602
Toll Free 888.235.0515 .,'235.0515 •Fax [phone] •casper@energj Jam'www.energylab.com
QA/QC Summary Report
Client:Denison Mines (USA)Corp
Project:4th Quarter Chioroform
Report Date:01/06/10
Work Order:C09120647
IAnalyte
~_.~.~'_~--~~----~..'~'~,_.'~~-'-'
Count Result Units RL %REe Low Limit High Limit RPO RPOLimit Qual
Method:A4500-CI B Batch:091228-CL-TIR-W
Sample 10:MBLK9-091228 Method Blank Run:TITRATION_091228A 12/28/09 09:49
Chloride NO mg/L 0.4
Sample 10:C09120638-008AMS Sample Matrix Spike Run:TITRATION_091228A 12/28/09 10:53
Chloride 252 mg/L 1.0 102 90 110
Sample 10:C09120638-008AMS Sample Matrix Spike Duplicate Run:TITRATION_091228A 12/28/0910:55
Chloride 249 mg/L 1.0 100 90 110 1.4 10
Sample 10:LCS35-091228 Laboratory Control Sample Run:TITRATION_091228A 12/28/09 10:57
Chloride 3530 mg/L 1.0 100 90 110
Sample 10:C09120647-003AMS Sample Matrix Spike Run:TITRATION_091228A 12/2810911:24
Chloride 477 mg/L 1.0 100 90 110
Sample 10:C09120647-003AMS Sample Matrix Spike Duplicate Run:TITRATION_091228A 12/28/09 11 :27
Chloride 477 mg/L 1.0 100 90 110 °10
Sample 10:C09120647-021AMS Sample Matrix Spike Run:TITRATION_091228A 12/28/09 12:01
Chloride 2840 mg/L 1.0 100 90 110
Sample 10:C09120647-021AMS Sample Matrix Spike Duplicate Run:TITRATION_091228A 12/28/0912:03
Chloride 2840 mg/L 1.0 100 90 110 °10
Sample 10:C09120811·004AMS Sample Matrix Spike Run:TITRATION_091228A 12/28/0913:16
Chloride 35.0 mg/L 1.0 99 90 110
Sample 10:C09120811-004AMS Sample Matrix Spike Duplicate Run:TITRATION_091228A 12/28/0913:18
Chloride 35.7 mg/L 1.0 101 90 110 2 10
Qualifiers:
RL -Analyte reporting limit.NO ~Not detected at the reporting limit.
ENERGYLABORATORIIgS,INC••2393SailCreek Highway (82601)•PD.Box3258 •Casper,WY82602/l:fi!Gi(((f!!iiiI TollFree 888.235.0515 •3('15.0515'Fax [phone] •casper@energyla(11'www.energylab.com
'tH~l.t;&Uc"in¥"r ..:.-_
QA/QC Summary Report
Client:Denison Mines (USA)Corp Report Date:01/06/10
Project:4th Quarter Chloroform Work Order:C09120647
i .~-~-------_._--------
IAnalyte Count Result Units RL %REC Low Limit High Limit RPO RPDLimit Qual
Method:E353.2 Batch:R128055
Sample 10:MBLK·1 Method Blank Run:TECHNICON_091228A 12/28/0912:15
Nitrogen,Nitrate+Nitrite as N NO m9/L 0.03
Sample 10:LCS·2 Laboratory Control Sample Run:TECHNICON_091228A 12/28/0912:17
Nitrogen,Nitrate+Nitrite as N 2.60 mg/L 0.10 102 90 110
Sample 10:C09120638·0050MS Sample Matrix Spike Run:TECHNICON_091228A 12/28/0913:12
Nitrogen,Nitrate+Nitrite as N 3.79 mg/L 0.10 112 90 110 S
Sample 10:C09120638·0050MSO Sample Matrix Spike Duplicate Run:TECHNICON_091228A 12/28/0913:15
Nitrogen,Nitrate+Nitrite as N 3.75 mg/L 0.10 110 90 110 1.1 10
Sample 10:C09120647·009BMS Sample Matrix Spike Run:TECHNICON~091228A 12/28/09 13:55
Nitrogen,Nitrate+Nitrite as N 1.92 mg/L 0.10 95 90 110
Sample 10:C09120647·009BMSO Sample Matrix Spike Duplicate Run:TECHNICON_091228A 12/28/0913:57
Nitrogen,Nitrate+Nitrite as N 1.99 mg/L 0.10 98 90 110 3.6 10
Sample 10:C09120647·019BMS Sample Matrix Spike Run:TECHNICON_091228A 12/28/09 14:32
Nitrogen,Nitrate+Nitrite as N 3.54 mg/L 0.10 90 90 110
Sample 10:C09120647·019BMSO Sample Matrix Spike Duplicate Run:TECHNICON_091228A 12/28/0914:35
Nitrogen,Nitrate+Nitrite as N 3.66 mg/L 0.10 96 90 110 3.3 10
Sample 10:C09120579·016FMS Sample Matrix Spike Run:TECHNICON~091228A 12/28/0915:12
Nitrogen,Nitrate+Nitrite as N 2.51 mg/L 0.10 94 90 110
Sample 10:C09120579·016FMSO Sample Matrix Spike Duplicate Run:TECHNICON_091228A 12/28/0915:15
Nitrogen,Nitrate+Nitrite as N 2.49 mg/L 0.10 93 90 110 0.8 10
Qualifiers:
RL ~Analyte reporting limit.
S ~Spike recovery outside of advisory limits.
NO ~Not detected at the reporting limit.
ENERGYLABORATORIEc INC••2393Sail CreekHighway (82601)•P.0.80)("'58 .Caspar,WY82602
Toll Free 888.235.0515 •3m ,0515 •Fax [phone] •casper@energylabJ •www.energylab.com
QAlQC Summary Report
Client:Denison Mines (USA)Corp
Project:4th Quarter Chloroform
Report Date:12/23109
Work Order:C09120647
Analyle Result Units RL %REC Low Limit High Limit RPD RPDLimit Qual
Method:SW8260B Balch:R127911
Sample ID:21-Dec-09_LCS_3 Laboratory Control Sample Run:5975VOC1_091221A 12/21/0912:38
Carbon tetrachloride 12 uglL 1.0 119 70 130
Chloroform 12 uglL 1.0 118 70 130
Chloromethane 7.7 ug/L 1.0 77 70 130
Methylene chloride 11 uglL 1.0 112 70 130
Surr:Dibromofluoromethane 1.0 101 70 130
Surr:p~Bromofluorobenzene 1.0 102 80 130
Surf:Toluene-dB 1.0 104 80 120
Surr:1,2~DichlorobenzeneMd4 1.0 94 80 120
Sample ID:21-Dec-09_MBLK_6 Method Blank Run:5975VOC1-091221A 1212110914:23
Carbon tetrachloride NO uglL 1.0
Chloroform NO uglL 1.0
Chloromethane NO uglL 1.0
Methylene chloride NO uglL 1.0
Surf:Dibromofluoromethane 1.0 96 70 130
Surr:p-Bromofluorobenzene 1.0 103 80 120
Surf:Toluene-dB 1.0 98 80 120
Surr:1,2-Dichlorobenzene-d4 1.0 110 80 120
Sample 10:C09120647-002CMS Sample Matrix Spike Run:5975VOC1_091221A 12121/0919:43
Carbon tetrachloride 1300 uglL 100 126 70 130
Chloroform 3400 uglL 100 158 70 130 S
Chloromethane 800 uglL 100 80 70 130
Methylene chloride 1200 uglL 100 119 70 130
Surr:Dibromofluoromethane 100 110 70 130
SUfr:p~Bromofluorobenzene 100 101 80 120
Surr:Toluene-dB 100 104 80 120
SUfr:1,2~Dichlorobenzene-d4 100 95 80 120
Sample ID:C09120647-002CMSD Sample Matrix Spike Duplicate Run:5975VOC1_091221A 12121/0920:18
Carbon tetrachloride 1200 uglL 100 120 70 130 4.9 20
Chloroform 3200 uglL 100 145 70 130 3.9 20 S
Chloromethane 760 uglL 100 76 70 130 4.6 20
Methylene chloride 1200 uglL 100 116 70 130 2.7 20
SUfr:DibromofJuoromethane 100 106 70 130 0 10
Surr:p-Bromofluorobenzene 100 101 80 120 0 10
Surr:Toluene-dB 100 104 80 120 0 10
Surr:1,2-Dichlorobenzene-d4 100 94 80 120 0 10
Qualifiers:
RL -Analyte reporting limit.
S -Spike recovery outside of advisory limits.
NO -Not detected at the reporting limit.
ENERGYLABORATORIJ:"'"INC••2393 SaltCreek Highway (82601)'Po.Bor "?58 •Casper,WY82602
TollFree 888235.0515 •30 W515 •Fax [phone] •casper@energylab •www.energylab.com
QAlQC Summary Report
Client:Denison Mines (USA)Corp
Project:4th Quarter Chloroform
Report Date:12/23109
Work Order:C09120647
Analyte Result Units RL %REC Low Limit High Limit RPD RPDLimit Qual
Method:SW8260B Batch:R127944
Sample 10:22-Dec-09_LCS_3 Laboratory Control Sample Run:GCMS2_091222A 12/22/09 11 :06
Carbon tetrachloride 13 ug/L 1.0 130 70 130
Chloroform 12 ug/L 1.0 119 70 130
Chloromethane 8.5 ug/L 1.0 85 70 130
Methylene chloride 8.8 ug/L 1.0 88 70 130
Surf:DibromofJuoromethane 1.0 100 70 130
Surf:p~BromofJuorobenzene 1.0 100 80 130
Surr:Toluene-d8 1.0 104 80 120
Surr:1,2~Dichlorobenzene-d4 1.0 104 80 120
Sample 10:22-Dec-09_MBLK_6 Method Blank Run:GCMS2_091222A 12122109 12:49
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 1.0 100 70 130
Surf:p-Bromofluorobenzene 1.0 112 80 120
Surf:Toluene-d8 1.0 104 80 120
Surf:1,2-Dichlorobenzene-d4 1.0 104 80 120
Sample 10:C09120647-020CMS Sample Matrix Spike Run:GCMS2_091222A 12/22109 20:23
Carbon tetrachloride 110 ug/L 10 108 70 130
Chloroform 120 ug/L 10 116 70 130
Chloromethane 110 ug/L 10 113 70 130
Methylene chloride 110 ug/L 10 111 70 130
Surr:Dibromofluoromethane 10 105 70 130
Surr:p-Bromofluorobenzene 10 96 80 120
Surr:Toluene-dB 10 104 80 120
Surr:1>2~Dichlorobenzene-d4 10 104 80 120
Sample 10:C09120647-020CMSD Sample Matrix Spike Duplicate Run:GCMS2_091222A 12/22/0920:58
Carbon tetrachloride 110 ug/L 10 108 70 130 0.4 20
Chloroform 110 ug/L 10 113 70 130 2.4 20
Chloromethane 110 ug/L 10 111 70 130 1.4 20
Methylene chloride 110 ug/L 10 108 70 130 3.3 20
Surr:Dibromofluoromethane 10 100 70 130 0 10
Surr:p-Bromofluorobenzene 10 95 80 120 0 10
Surr:Toluene-dB 10 105 80 120 0 10
Sure 1,2~Djchlorobenzene-d4 10 102 80 120 0 10
Qualifiers:
RL -Analyte reporting limit.NO -Not detected at the reporting limit.
UNmltJ7
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Chain of Custody and Analytical Request Record
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Signed Sam Ie Dis osal:Return to Client:Lab Disposal:Id-
In certain circumstances,samples submitted to Energy Laboratories,Inc.may be subcontracted to other certified laboratories in order to complete the analysis requeste
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.
ICustody IRe~ed by ("""'If)/__Date/Time,-:;-'.--;--~a('}"I//'IL.,AIIl I'JIIYI1~12 1.2 '/7-V7 12J1l l.e::.--UA
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•'~elveC\tlYLalloratOry:uatel Irq~1 ~I q .~aure:~;~~Signed SamnleDisnosal:Return to Client:Lab Disposal:......~.'"I -Ia/D qy /y//"_.'
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.
~of3ChainofCustodyandAnalyticalRequestRecordJdgtM7
R'4ot;?$.ioJj1l4t'.-_.-.-._-..,..".• •.....................................,......u"""...........................
Company Name:Project Name,PWS,Permit,Etc.Sample Origin EPA/State Compliance:..
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Report Mail Address:po p->Cl')(goct Contact Name:Phone/Fax:Email:Sampler:(Please Print)
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Record Relinquisned by (print):DalefTime:7 ture:'1 -Received by (print):Daternme:Signature:
MUSTbe 1\I~X L.alJorawry:uae');)./;;Ioq q ,D l'ff~/Signed Sarnole DisDosal:Return to Client:Lab Disposal:..N2)
pies submitted to Energy Laboratories,Inc.may be SUbcontracted to other certitied laboratories In order to camp
This serves as notice ofthis possibility.All subwcontract data wlll be clearly notated on your analytical report.
Visit our web site at www.energylab.com for additional information,downloadable fee schedule,forms,and links.
I)!.1:1
Energy Laboratories Inc
Workorder Receipt Checklist
Denison Mines USA Corp
1111111111111111111111111111111111111111111111111111111
C09120647
Login completed by:Corinne Wagner
Reviewed by:
Reviewed Date:
Date and Time Received:12/18/20099:10 AM
Received by:at
Carrier name:FedEx
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 ofcustody agrees with sample labels?
Samples in proper container/bottle?
Sample containers intact?
Sufficient sample volume for indicated test?
All samples received within holding time?
Containerrremp 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
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
No 0
No 0
No 0
No 0
No 0
No 0
No 0
No 0
No 0
No 0
No 0
No 0
Not Present D
Not Present 0
Not Present 0"
No VOA vials submitted 0
Not Applicable 0
ENERGYLABORATO!J'ES,INC.•2393 Sal/Creek Highway(82601)•POBn){3258 •Casper,WY82602
lOllFree 888.235.0515'('235.0515'F8!{307.234./639 •casper@energy 'om'www.energylab.com
CLIENT:Denison Mines (USA)Corp
Project:4th Quarter Chloroform
Sample Delivery Group:C09120647
ORIGINAL SAMPLE SUBMITTAL(S)
All original sample submittals have been returned with the data package.
Date:D6-Jan-!D
CASE NARRATIVE
SAMPLE TEMPERATURE COMPLIANCE:4°C (±2°C)
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 ifthere is evidence that the chilling process has
begun.
GROSS ALPHA ANALYSIS
Method 900.0 for gross alpha and gross beta is intended 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 ofcounting should not exceed 8 days.
SOIUSOLID 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 refiects 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,SD
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 ofthis 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
Tab I
CSV Transmittal Letter
Jo Ann Tischler
From:
Sent:
To:
Cc:
SUbject:
Attachments:
Dear Mr.Finerfrock,
Jo Ann Tischler
Thursday,February 25,2010 1:33 PM
'dfinerfrock@utah,gov'
David Frydenlund
Transmittal of CSV files White Mesa Mill 2009 04 chloroform monitoring
C09120647,csv;C09120811,csv;C09120896,csv
Attached to this email is an electronic copy oflaboratory results for chloroform monitoring conducted at the White Mesa
Mill during the 41h Quarter,2009,in Comma Separated Value (CSV)format.
Please contact me at 303-389-4132 if you have any questions,
Yours Truly,
Jo Ann Tischler
Denison Mines (USA)Corp,
Director,Pennitting and Compliance
1
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 1400
1600
ND
950
9
250
ND
300
860
ND
ND
ND
1100
ND
ND
84700
15000
160
380
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
1300
1800 NDMW-04
ND
1
ND
MW-26
TW4-20
MW-4
PIEZ-1
2000
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)
1700
MW-32
ND
temporary perched monitoring well
showing concentration in uG/l
200
perched monitoring well installed April, 2005
showing concentration in uG/l KRIGED 4th QUARTER, 2009 CHLOROFORM (uG/L)
WHITE MESA SITE
H:/718000/feb10/chl1209.srf
EXPLANATION
NOTES: ND = not detected, NS = not sampled;
temporary perched monitoring well installed
May, 2007 showing concentration in uG/lND SJS
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
10/15/2008 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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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
15-Sep-09 ND <1 <1 ND 33
16-Dec-09 ND ND ND ND ND 34

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-08 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

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-07 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-08 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

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-08 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

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

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
06/14/06 280 ND ND ND 14.3 221
07/20/06 864 ND ND ND 14.5 221
11/08/06 350 ND 1.6 ND 15.9 236
28-Feb-07 440 ND ND ND 20.9 347
06/27/07 740 ND ND ND 19.3 273
Aug-15-07 530 ND ND ND 19.3 259
Oct-10-08 440 ND ND ND 18.8 238
03/26/08 1400 ND ND ND 39.1 519
06/25/08 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

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
Aug-15-07 ND ND ND ND ND 46
Oct-10-08 ND ND ND ND ND 43
03/26/08 ND ND ND ND ND 41
06/25/08 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

TW4-24

Chloroform
(ug/l)
Carbon
tetrachloride
(ug/l)
Chloromethane
(ug/l)
Methylene
Chloride
(ug/l)
Nitrate
(mg/l)
Chloride
(mg/l)
06/27/07 0 ND ND ND 26.1 770
Aug-15-07 0 ND ND ND 29.0 791
Oct-10-08 1.5 ND ND ND 24.7 692
03/26/08 2.9 ND ND ND 24.4 740
06/25/08 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

TW4-25

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 17.1 395
Aug-15-07 ND ND ND ND 16.7 382
Oct-10-08 ND ND ND ND 17.0 356
03/26/08 ND ND ND ND 18.7 374
06/25/08 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

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
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
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
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
100.0
150.0
200.0
250.0
300.0
(u
g
/
L
)
TW4-6 Chloroform Values
(50.0)
0.0
50.0
6-
J
u
n
-
0
0
26
-
M
a
r
-
0
1
7-
N
o
v
-
0
1
12
-
S
e
p
-
0
2
23
-
J
u
n
-
0
3
29
-
M
a
r
-
0
4
17
-
N
o
v
-
0
4
31
-
A
u
g
-
0
5
14
-
J
u
n
-
0
6
28
-
F
e
b
-
0
7
10
-
O
c
t
-
0
7
10
-
S
e
p
-
0
8
24
-
J
u
n
-
0
9
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
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
400
600
800
1000
1200
1400
(u
g
/
L
)
TW4-10 Chloroform Values
-400
-200
0
200
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
)
TW4-11 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
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
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
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
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
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