Supervising Engineer California Regional Water Quality Control … · 2017-03-02 · 2016 Second...

EESLPIRED

February 22, 2017

Mr. Lonnie WassSupervising EngineerCalifornia Regional Water Quality Control BoardCentraL ValLey Region - Region 5 Fresno Office1685 E StreetFresno, CaLifornia 93706-2007

RE: Hitmar Cheese Company, Inc. (“HCC”)Hitmar, Merced County, CaliforniaCleanup and Abatement Order (“Order”) R5-2004-0722

Dear Mr. Wass:

Pursuant to the requirements of the Cteanup a Abatement Order No. R5-2004-0722 (“Order”),at the request of Hitmar Cheese Company (“HCC”), Jacobson James and Associates (“JJ&A”)has prepared the encLosed 2016 Second Semi-AnnuaL Upper Aquifer Performance MonitoringReport. The report incLudes the information specified in the Order.

I certify under penatty of taw that I have personatty examined and am famitiar with theinformation submitted in these documents and alt attachments and that, based on my inquiryof those individuals immediately responsible for obtaining the information, I believe that theinformation is true, accurate, and complete. I am aware that there are significant penaltiesfor submitting false information, including the possibility of fine and imprisonment.

Any questions on the above can be addressed to my attention at (209) 656-2271.

Sincerety,Hitmar Cheese Company Inc.

Burton N. FteischerEnvironmental Director

cc: Jan Atfson, RWQCBRusseLL Watts, RWQCBRonald Weitmer, Hitmar Cheese CompanyDavid Ahiem, Hitmar Cheese Company

Headquarters & Innovation Center

8901 North Lander Avenue, P.O. Box 910, Hilmar, CA 95324 USA T: 209.667.6076 Fax: 209,6341408 hilmarcheese.com

Hilmar Manufacturing Site & Visitor Center: 9001 North Lander Avenue, P.O. Box 910, Hilmar, CA 95324 USA 1: 209.667.6076Turlock Manufacturing Site: 3600 West Canal Drive, lurlock, CA 95380, Mail: P.O. Box 910, Hilmar, CA 95324 USA T: 209.667.6076

Daihart Manufacturing Site: 12400 US Highway 385, P.O. Box 1300, Dalhart, TX 79022 USA 1: 806.244.8800

HCC 2016 Second SA MS Report 20170222 Final.docx

February 22, 2017

Mr. Burton N. Fleischer Environmental Director Hilmar Cheese Company 9001 North Lander Avenue Hilmar, California 95324

Subject: 2016 Second Semi‐Annual Upper Aquifer Performance Monitoring Report Hilmar Cheese Company, Hilmar, California

Dear Mr. Burton Fleischer:

On behalf of Hilmar Cheese Company (HCC), Jacobson James & Associates (JJ&A) has prepared this 2016

Second Semi Annual Upper Aquifer Performance Monitoring Report (Report) for the HCC facility located

in Hilmar, California (the Site), shown on Figure 1. This Report describes the work performed and

presents the results obtained from monitoring and sampling conducted from July 1 through

December 31, 2016. This Report also includes data collected by HCC in accordance with the Central

Valley Regional Water Quality Control Board (CVRWQCB) Waste Discharge Requirements (WDR) Order

R5‐2010‐00081, as this data is relevant for monitoring the Site conditions. WDR reports are submitted

quarterly under separate cover by HCC.

This Report is provided in accordance with the Clean‐up and Abatement Order (CAO) R5 2004 07222

issued by the (CVRWQCB), dated December 2, 2004, and CVRWQCB correspondence 3 , dated

May 13, 2014. The Report includes additional data evaluation and presentation per the revised Upper

Aquifer Remedial Action Plan4 (RAP), dated February 28, 2013. The data collection methods and

procedures have been designed to accomplish the following objectives:

Confirm that the RAP is progressing as expected and consistent with the timeframe

estimates to achieve the Remedial Action Objectives (RAO).

Monitor for potential changes in environmental conditions at the Site.

The data presented herein indicates that groundwater quality continues to improve at and

downgradient of HCC. In the Upper Aquifer Supply Zone, the primary constituents of concern (COCs)

1 Monitoring wells sampled pursuant to the WDR include MW‐04, ‐06, ‐08, ‐09, ‐11, ‐12, ‐16 through ‐19, and ‐21 through 23; effluent monitoring data collected pursuant to the WDR are also included. 2 CVRWQCB, 2004. Cleanup and Abatement Order No. R5‐2004‐0722 for Hilmar Cheese Company, Inc., Hilmar Whey, Inc., and Kathy and Delton Nyman, Cheese Processing Plant, Merced County. December 2. 3 CVRWQCB, 2014. Correspondence regarding Proposed Modifications to the Monitoring and Sampling Program, Hilmar Cheese Company, Hilmar, Merced County, from Ms. Pamela C. Creedon (CVRWQCB) to Mr. Burton Fleischer (HCC). May 13. 4 JJ&A, 2013. Upper Aquifer Remedial Action Plan, Hilmar Cheese Company, Hilmar, California. Revised February 28.

2016 Second Semi‐Annual Upper Aquifer Performance Monitoring Report Hilmar Cheese Company, Hilmar, California February 22, 2017 Page 2 of 12

total dissolved solids, sodium, and chloride have been below their respective RAOs in all of the sampling

locations since April 2016. The groundwater in the Upper Aquifer Shallow Zone continues to exhibit

overall decreasing trends for most wells, which is consistent with the timeframe estimates to achieve

the RAOs. Based on the data presented herein, the RAP‐defined approach is continuing to have the

desired effect of reducing concentrations of the COCs as predicted.

GROUNDWATER MONITORING AND SAMPLING WORK PERFORMED AND RESULTS

Groundwater Elevation Monitoring

Groundwater levels were measured in WDR wells on July 18, and October 12, 2016, and in wells

addressed in the RAP on October 12, 2016 as noted on Table 1. At each monitoring well, the depth to

groundwater was measured to the nearest 0.01 foot using an electronic water level meter with respect

to the surveyed top of well casing. The field monitoring forms are provided in Attachment 15 and the

water level monitoring results are presented in Table 1. The locations of the monitoring wells are

provided on Figure 2. Historical groundwater elevations from January 2010 through October 2016 for

the Upper Aquifer Shallow Zone and Upper Aquifer Supply Zone monitoring wells are presented

graphically in Attachment 2.

Potentiometric surface maps, depicting groundwater flow direction for the Upper Aquifer Shallow Zone

and Upper Aquifer Supply Zone, were constructed from the October 2016 water level data and are

provided as Figures 3 and 4, respectively. Approximate groundwater flow directions and estimated

horizontal gradients are summarized as follows:

Upper Aquifer Shallow Zone: southwest at approximately 0.0014 feet per foot (ft/ft),

between MW‐04 and MW‐17.

Upper Aquifer Supply Zone: southwest at approximately 0.0008 ft/ft, between MW‐22

and MW‐19.

Water elevation charts for well clusters used to evaluate vertical gradient in July 2016 and October 2016

are provided in Attachment 3. The estimated vertical gradients are presented in Table 2 and

summarized below:

Upper Aquifer Shallow Zone to Upper Aquifer Supply Zone:

o Well pair MW‐06 and MW‐22: downward gradient of 0.012 ft/ft in July 2016; and,

0.007 ft/ft in October 2016.

Upper Aquifer Supply Zone to Lower Aquifer:

o Well pair MW‐22 and MW‐23: downward gradient of 0.745 ft/ft in July 2016; and,

0.623 ft/ft in October 2016.

5 Field forms for monitoring wells MW‐04, ‐06, ‐08, ‐09, ‐11, ‐12, ‐16 through ‐19, ‐22, and ‐23 are summarized in the Waste Discharge Requirements (WDR) quarterly reports, submitted under separate cover by HCC.


Groundwater Sampling and Analysis

Nineteen (19) monitoring wells6 were sampled on October 12, 2016 pursuant to the Upper Aquifer

Remedial Action Plan. Monitoring well MW‐21 was not sampled during this event due to insufficient

water present (i.e., well was dry).

The groundwater monitoring and sampling was completed by Del‐Tech Geotechnical Support Services,

Inc. (of Oakdale, California) on July 18, 2016 and October 12, 2016. The analytical data set allows for a

complete review of constituent trends throughout the Site as discussed in the following sections.

The groundwater samples from the nineteen wells sampled pursuant to the CAO and RAP were analyzed

as follows:

Anions: sulfate, chloride, and nitrate as nitrogen by U.S. Environmental Protection Agency

(USEPA) Method 300.0;

Dissolved calcium, iron, magnesium, manganese, potassium, and sodium by USEPA

Method 6010B;

Total Alkalinity (as calcium carbonate) with bicarbonate by Standard Method (SM) 2320B;

Total Dissolved Solids (TDS) by SM 2540C;

Electrical Conductivity USEPA 120.1; and,

Total Kjeldahl Nitrogen by USEPA Method 351.2.

The monitoring wells sampled pursuant to the CAO and RAP were purged using a centrifugal (MW‐01,

MW‐03, MW‐05, MW‐07, MW‐13, and MW‐15) or submersible pump (MW‐25) until water‐quality

parameters (pH, temperature, electrical conductivity, oxidation‐reduction potential, and turbidity)

stabilized and/or until at least three well casing volumes of groundwater were removed.

Field monitoring forms are provided in Attachment 1. Field forms for monitoring wells sampled

pursuant to the WDR are submitted under separate cover.

Groundwater samples were collected from each well using sample containers supplied by

the laboratory. Samples were labeled and immediately placed on ice (water‐based) in an insulated

cooler and submitted under strict chain‐of‐custody control to a California State certified laboratory.

Groundwater samples for dissolved calcium, iron, magnesium, manganese, potassium, and sodium

analyses were filtered in the field, using disposable 0.45‐micron filters, and subsequently preserved with

nitric acid.

The analytical results for the subject monitoring wells are presented in Table 3. Laboratory reports with

chain‐of‐custody forms are provided in Attachment 4. A summary of historical analytical results is

provided as Attachment 5. A discussion of TDS, dissolved sodium, chloride, dissolved iron, dissolved

manganese, sulfate, and nitrate as nitrogen is provided below for wells sampled pursuant to the CAO

and RAP.

6 It is noted that there are several routine sampling programs at the Site including monitoring pursuant to the Cleanup and Abatement Order (CAO), WDR and the Remedial Action Plan (RAP). Monitoring wells may be included in more than one of the subject programs.


Total Dissolved Solids

Concentrations of TDS in the Upper Aquifer Shallow Zone groundwater samples ranged from

460 milligrams per liter (mg/L) at well MW‐04 to 1,400 mg/L at well MW‐16 on July 18, 2016; and,

400 mg/L at MW‐04 to 2,890 mg/L at well MW‐15 on October 12, 2016. Concentrations of TDS in the

Upper Aquifer Supply Zone groundwater samples ranged from 560 mg/L at well MW‐18 to 700 mg/L at

well MW‐22 on July 18, 2016; and, 396 mg/L at well MW‐25 to 680 mg/L at wells MW‐19 and MW‐22 on

October 12, 2016. The Lower Aquifer C‐Zone well MW‐23 for TDS concentration was 720 mg/L on

July 18, 2016 and October 12, 2016.

In the Upper Aquifer Shallow Zone, TDS was observed above the RAO (i.e., 912 mg/L) in the following

wells:

MW‐06: Exhibited stable conditions from 980 mg/L (April 14, 2016) to 940 mg/L (July 18,

2016) and 950 mg/L (October 12, 2016);

MW‐07: Decreased from 1,470 mg/L (April 14, 2016) to 1,050 mg/L (October 12, 2016);

MW‐09: Exhibited stable conditions from 1,000 mg/L (April 14, 2016) to 1,300 mg/L (July 18,

2016) and 1,100 mg/L (October 12, 2016);

MW‐12: Exhibited stable condition of 950 mg/L (April 14, 2016) to 1,000 mg/L (July 18,

2016) and 980 mg/L (October 12, 2016);

MW‐15: Increased from 837 mg/L (April 14, 2016) to 2,890 mg/L (October 12, 2016);

MW‐16: Exhibited variable to stable conditions from 900 mg/L (April 14, 2016) to 1,400

mg/L (July 18, 2016) and 880 mg/L (October 12, 2016); and,

MW‐17: Exhibited variable to stable conditions from 680 mg/L (April 14, 2016) to 1,000

mg/L (July 18, 2016) and 860 mg/L (October 12, 2016).

Analytical results for TDS for the July and October 2016 groundwater sampling events are presented in

Table 3. The TDS concentrations in groundwater for the Upper Aquifer Shallow Zone and Upper Aquifer

Supply Zone for the October 2016 sampling event are illustrated in Figures 5‐1 and 5‐2.

Dissolved Sodium

Dissolved sodium was detected in groundwater samples collected in the Upper Aquifer Shallow Zone

ranging from 66 mg/L at well MW‐08 to 320 mg/L at well MW‐06 on July 18, 2016; and 62 mg/L at well

MW‐16 to 320 mg/L at well MW‐06 on October 12, 2016. Dissolved sodium was detected in

groundwater samples in the Upper Aquifer Supply Zone ranging from 44 mg/L at well MW‐18 to

130 mg/L at well MW‐22 on July 18, 2016; and, 47 mg/L at well MW‐18 to 130 mg/L at well MW‐22 on

October 12, 2016. Dissolved sodium concentrations detected in the groundwater samples from the

Lower Aquifer C‐Zone well MW‐23 were 180 mg/L on July 18, 2016 and 200 mg/L on October 12, 2016.

Sodium was not detected above the RAO (i.e., 346 mg/L) in groundwater samples collected during the

reporting period. Analytical results for dissolved sodium for the July and October 2016 groundwater

sampling events are presented in Table 3. Dissolved sodium in groundwater for the Upper Aquifer


Shallow Zone and Upper Aquifer Supply Zone as measured during the October 2016 sampling event are

illustrated in Figures 6‐1 and 6‐2.

Chloride

Chloride was detected in groundwater samples collected in the Upper Aquifer Shallow Zone ranging

from 43 mg/L at well MW‐08 to 190 mg/L at well MW‐09 on July 18, 2016; and 26 mg/L at well MW‐11

to 200 mg/L at well MW‐07 on October 12, 2016. Chloride was detected in groundwater samples in the

Upper Aquifer Supply Zone ranging from 52 mg/L at well MW‐18 to 100 mg/L at well MW‐22 on July 18,

2016; and 50 mg/L at well MW‐25 to 100 mg/L at well MW‐22 on October 12, 2016.

Chloride concentrations detected in groundwater samples from the Lower Aquifer C‐Zone well MW‐23

were 280 mg/L on July 18, 2016 and 290 mg/L on October 12, 2016.

Chloride was not detected above the RAO (i.e., 239 mg/L) in groundwater samples collected during the

reporting period. Analytical results for chloride for the July and October 2016 groundwater sampling

events are presented in Table 3. Chloride in groundwater for the Upper Aquifer Shallow Zone and

Upper Aquifer Supply Zone as measured during the October 2016 sampling event, are illustrated in

Figures 7‐1 and 7‐2.

Other Constituents of Concern

The concentrations of iron, nitrate as nitrogen, dissolved manganese, and sulfate are discussed below.

Dissolved iron was detected in groundwater samples collected on October 12, 2016 in four

of the 15 monitoring wells in the Upper Aquifer Shallow Zone in concentrations ranging

from 1.18 mg/L at well MW‐15 to 7.12 mg/L at well MW‐07. Dissolved iron was not

detected in the Upper Aquifer Supply Zone or Lower Aquifer C‐Zone. Iron was detected

above the RAO (i.e., 0.3 mg/L) during the reporting period in the following wells:

o MW‐03: Iron was stable at 6.95 mg/L (April 14, 2016) and 6.73 mg/L

(October 12, 2016);

o MW‐05: iron decreased from 6.19 mg/L (April 14, 2016) to 3.83 mg/L

(October 12, 2016);

o MW‐07: Iron stable at from 5.55 mg/L (April 14, 2016) to 7.12 mg/L

(October 12, 2016; and,

o MW‐15: Iron increased from not detected (<0.20 mg/L) in April 14, 2016 to

1.18 mg/L in October 12, 2016.

Nitrate as nitrogen was detected in groundwater samples collected in the Upper Aquifer

Shallow Zone at concentrations ranging from 0.53 mg/L at well MW‐06 to 120 mg/L at well

MW‐16 on July 18, 2016; and 0.11 mg/L at well MW‐07 to 100 mg/L at well MW‐15 on

October 12, 2016. Nitrate as nitrogen was detected in groundwater samples in the Upper

Aquifer Supply Zone ranging from 4.5 mg/L at well MW‐19 to 27 mg/L at well MW 18 on

July 18, 2016; and, 4.6 mg/L at well MW‐19 to 26 mg/L at well MW‐18 on October 12, 2016.

Nitrate as nitrogen was detected in the groundwater sample from the Lower Aquifer C‐Zone


well MW‐23 on July 18, 2016 at a concentration of 0.35 mg/L, but was not detected on

October 12, 2016.

In the Upper Aquifer Shallow Zone, nitrate was detected above the RAO (i.e., 52 mg/L)

during the reporting period in the following wells7:

o MW‐11: Nitrate was stable at 34 mg/L (April 14, 2016) and 36 mg/L (July 18, 2016),

but increased to 73 mg/L (October 12, 2016);

o MW‐157: Nitrate increased from 34.1 mg/L (April 14, 2016) to 100 mg/L

(October 12, 2016;

o MW‐167: Nitrate exhibited variable to stable concentrations from 81 mg/L

(April 14, 2016) to 120 mg/L (July 18, 2016) and 78 mg/L (October 12, 2016); and,

o MW‐177: Nitrate exhibited stable concentrations from 54 mg/L (April 14, 2016) to

70 mg/L (July 18, 2016) and 55 mg/L (October 12, 2016);

Dissolved manganese was detected in groundwater samples collected in the Upper Aquifer

Shallow Zone ranging from 0.068 mg/L at well MW‐11 to 0.7 mg/L at wells MW‐04 and

MW‐06 on July 18, 2016; and 0.023 mg/L at well MW‐12 to 3.66 mg/L at well MW‐07 on

October 12, 2016. Dissolved manganese was detected in groundwater samples in the Upper

Aquifer Supply Zone in concentrations ranging from 0.011 mg/L at well MW‐18 to 0.96 mg/L

at well MW‐22 on July 18, 2016; and 0.011 mg/L at well MW‐18 to 1 mg/L at well MW‐22 on

October 12, 2016. Dissolved manganese was detected in groundwater samples from the

Lower Aquifer C Zone well MW‐23 in concentrations of 0.21 mg/L on July 18, 2016 and

0.2 mg/L on October 12, 2016. In the Upper Aquifer Shallow Zone, dissolved manganese

was detected above the RAO (0.34 mg/L) during the reporting period in the following wells:

o MW‐03: Manganese exhibited stable conditions from 3.02 J8 mg/L (April 14, 2016)

to 2.78 mg/L (October 12, 2016);

o MW‐04: Manganese decreased from 0.91 mg/L (April 14, 2016) to 0.67 mg/L

(July 18, 2016) and then to 0.55 mg/L (October 12, 2016);

o MW‐05: Manganese exhibited stable conditions from 2.34 J mg/L (April 14, 2016) to

2.81 mg/L (October 12, 2016);

o MW‐06: Manganese exhibited stable conditions from 0.92 mg/L (April 14, 2016) to

0.72 mg/L (July 18, 2016) and 0.70 mg/L (October 12, 2016);

o MW‐07: Manganese exhibited stable conditions from 3.53 J mg/L (April 14, 2016) to

3.66 mg/L (October 12, 2016);

o MW‐08: Manganese exhibited variable concentrations from 0.42 mg/L

(April 14, 2016) to 0.12 mg/L (July 18, 2016); then increased to 0.74 mg/L

(October 12, 2016);

7 Wells MW‐15, MW‐16, and MW‐17 are perimeter wells located upgradient or away from the former Primary Lands; the current nitrate concentrations and trends are not attributed to historic HCC discharges. 8J A data validation flag that indicates the analyte was positively identified but the associated numerical value may not represent the actual concentration of the analyte in the sample due to an analytical bias in precision or accuracy, or because the resulting concentration has been reported at a confidence level of less than 99 percent.


o MW‐16: Manganese exhibited stable conditions from 0.22 mg/L (April 14,

2016) to 0.39 mg/L (July 18, 2016) and 0.16 mg/L (October 12, 2016);

o MW‐17: Manganese exhibited stable conditions from 1.0 mg/L (April 14,

2016) to 0.22 mg/L (July 18, 2016) and 0.41 mg/L (October 12, 2016);

Sulfate was not detected above the RAO (i.e., 250 mg/L) in groundwater samples collected

during the reporting period. Sulfate was detected in groundwater samples collected in the

Upper Aquifer Shallow Zone in concentrations ranging from 14 mg/L at well MW‐08 to 110

mg/L at well MW‐06 on July 18, 2016; and 28 mg/L at wells MW‐01 and MW‐04 to 230 mg/L

at well MW‐07 on October 12, 2016. Sulfate was detected in groundwater samples in the

Upper Aquifer Supply Zone ranging from 13 mg/L at well MW‐22 to 53 mg/L at well MW‐18

on July 18, 2016; and 12 mg/L at well MW‐22 to 61 mg/L at well MW‐18 on October 12,

2016. Sulfate was not detected in the groundwater samples from the Lower Aquifer C‐Zone

well MW‐23 on July 18, 2016 or on October 12, 2016.

Charts illustrating the constituent trends are provided in Attachment 6.

FORMER PRIMARY LAND USE STATUS

Partially treated wastewater was historically discharged to lands surrounding the HCC facility that were

identified as Primary Lands.9 Discharge to the former Primary Lands ceased in December 2010; these

parcels are currently used for agricultural purposes. Attachment 7 provides the historical land use

timeline for the former Primary Lands beginning with January 2011 (the month following the final

application of partially treated wastewater) through December 2016. Figure 8 provides a land use

timeline for the former Primary Lands from January through December of 2016. As shown on

Attachment 7, portions of the former Primary Lands became Reuse Areas S‐63 and S‐64 in March 2011,

and S‐65 in April 2011; Former Primary Land S‐67 became a Reuse Area in the first quarter 2013.

Reuse Areas may receive HCC Reuse water, Turlock Irrigation District (TID) water, and/or

dairy wastewater.

From January 2011 through December 2016, approximately 827 million gallons of water was applied to

Reuse Areas S‐63 through S‐65, including approximately 153 million gallons of HCC Reuse water,

650 million gallons of TID water, and 23 million gallons of dairy wastewater.

A review of the collective information on Figure 8 indicates the following for the period of July through

December 2016:

Reuse Area S‐63 received HCC Reuse Water and TID water during the second half of 2016.

Reuse Areas S‐64 and S‐65 received TID water during July through October 2016.

Reuse Area S‐67 did not receive HCC Reuse water, TID water, or dairy wastewater during the

second half of 2016.

9 Fully treated waste water was historically discharged to parcels (typically further away from the HCC facility) known as Secondary Lands.


Quarterly WDR reports, submitted to the CVRWQCB under separate cover, identify the type, volume,

and quality of water applied to the Reuse Areas. The information from the quarterly WDR reports was

used to construct Figure 8 and Attachment 7.

The breakdown by quarter for the current reporting period is as follows:

Third Quarter 2016

o HCC Reuse water: no discharge to Reuse Areas S‐63, S‐64, and S‐65;

o TID: 61.9 million gallons discharged to Reuse Areas S‐63, S‐64, and S‐65; and,

o Dairy wastewater: no discharge to Reuse Area S‐63, S‐64, and S‐65.

Fourth Quarter 2016

o HCC Reuse water: 12.1 million gallons discharged to Reuse Areas S‐63;

o TID: 17.7 million gallons discharged to Reuse Areas S‐63, S‐64 and S‐65; and,

o Dairy wastewater: no discharge to Reuse Areas S‐63, S‐64, or S‐65.

A comprehensive summary of water quality data from January 2011 through the current reporting

period for Reuse Areas S‐63, S‐64, S‐65, and S‐67 is presented in Table 4.

GROUNDWATER QUALITY TREND EVALUATION

As recommended in the RAP, charts were prepared for use as a graphical tool to evaluate the trends of

COCs in each well sampled and to provide a comparison to the Site RAOs. The RAOs for each COC are

presented on Table 5 and are depicted in the charts provided in Attachment 6 (Concentrations of COCs

over Time) and Attachment 8 (2‐Year Moving Average of COCs in Monitoring Wells). These charts also

illustrate analyte‐specific trends for each aquifer zone.

Moving averages for COC concentrations were calculated on a bi‐annual interval (2‐year) period using

four data points. The monitoring wells selected for the moving average calculations have exceeded their

RAOs within the past two years. As shown on Table 6, and indicated below, the number of wells that

have reported TDS, chloride and sodium (i.e., primary COCs) above their respective RAOs over the last

two years has decreased:

Nine (9) wells from the upper aquifer shallow zone exceeded the RAO for TDS;

Two (2) wells from the upper aquifer shallow zone exceeded the RAO for chloride; and.

Four (4) wells from the upper aquifer shallow zone exceeded the RAO for sodium;

Moving average graphical analyses are provided in Attachment 8.

Charts of the historical trends of COCs at each monitoring well location are provided in Attachment 9.

Concentrations of TDS provide a general indicator parameter to illustrate the overall progress at

the Site. The 2‐year moving average trends of TDS in the Upper Aquifer Shallow Zone monitoring wells

are presented in Figure 9. The data are presented on this figure relative to Site features and the

October 2016 groundwater elevation contours to illustrate the current land use and groundwater

flow regime. As shown on the figure, concentrations of TDS continue to exhibit a declining trend with

the majority of the wells reporting concentrations below the RAO (i.e., less than [<] 912 mg/L).


The trends of TDS at the Site are confirmed by a review of the time versus concentration charts

(Attachment 9) from January 2011 to October 2016. The charts document the stable to decreasing

concentrations of COCs at, and downgradient of, the Site in the Upper Aquifer Shallow and Upper

Aquifer Supply Zones with the following exception.

The Upper Aquifer Shallow Zone monitoring well MW‐15 exhibited an increase in select constituent

concentrations (e.g., nitrate and TDS) during the October 2016 sampling event. This well is upgradient

of historic Primary Lands and the water quality conditions observed are not considered representative

of historical HCC discharges.

Groundwater Quality Trend Summary

Fluctuations in COC concentrations will occur in response to: (1) changes in groundwater elevation and

groundwater gradients due to seasonal conditions (e.g., drought), pumping, and irrigation activities;

(2) agricultural activities; (3) physical, chemical, and biological processes in the Upper Aquifer Shallow

Zone and Upper Aquifer Supply Zone under the current and seasonal land use; and, (4) localized, non‐

HCC operations and/or conditions near the subject wells.

The groundwater in the Upper Aquifer Shallow Zone, as illustrated by the 2‐year moving average charts

(see Attachment 8), continues to exhibit overall decreasing trends for most wells, which is consistent

with the timeframe estimates to achieve the RAOs. Based on the data presented herein, the

RAP‐defined approach is continuing to have the desired effect of reducing concentrations of HCC‐related

COCs in groundwater.

EVALUATION OF GROUNDWATER MODELING PREDICTIONS

In August 2012, a groundwater model was prepared which estimated the time to achieve RAOs for

chloride, sodium, and TDS under the recommended remedial alternative10. The model provided a

generalized estimate of the time to achieve these RAOs. This was based on model calibration and a set

of reasonable estimates for future conditions. The model simulations estimated that the RAOs would be

achieved in approximately 2016 and 2022 for the Upper Aquifer Shallow Zone and the Upper Aquifer

Supply Zone, respectively, with an estimated variability due to the estimates for hydraulic conductivity

and effective porosity used in the calibrated model.

Actual field conditions as of October 2016 indicate that all four (4) of the Upper Aquifer Supply Zone

monitoring wells achieved the RAOs for chloride, sodium, and TDS. The Upper Aquifer Shallow Zone

achieved the RAOs for chloride and sodium at all fourteen sampling locations; and, TDS at nine of the

fourteen sampling locations, during the October 2016 sampling event, consistent with the model

estimate time frame. The following sections provide COC specific discussions for the Upper Aquifer

Shallow Zone and Supply Zone, respectively.

10 Kennedy/Jenks Consultants, 2012. Groundwater Modeling for Remedial Alternatives Evaluation. August 9, 2012.


Upper Aquifer Shallow Zone

A review of the 2‐year moving average charts prepared for TDS, sodium and chloride (Attachment 8), is

provided below for the Upper Aquifer Shallow Zone:

Chloride: All Upper Aquifer Shallow Zone monitoring wells achieved a moving average below

the RAO (i.e., < 239 mg/L) with the exception of monitoring well MW‐07, although the

October 2016 chloride concentration of 200 mg/L is below the RAO.

Sodium: All Upper Aquifer Shallow Zone monitoring wells achieved a moving average below

the RAO (i.e., < 346 mg/L) with the exception of monitoring well MW‐07. The moving

average of sodium in MW‐07 was below the RAO until the October 2015 data (i.e.,

446 mg/L. Subsequent sampling results indicate sodium concentrations have decreased

from October 2015 and recent concentrations are reported below the RAO.

TDS: There are currently seven Upper Aquifer Shallow Zone wells (MW‐06, ‐07, ‐09, ‐12,

‐13, ‐15, and ‐16) where the 2‐year moving average is above the RAO (i.e., 912 mg/L). As

indicated on the moving average charts, most of these wells exhibit decreasing

concentrations slightly above or below the RAO, with the exception of monitoring well

MW‐15 (discussed above).

The data suggest that the RAOs for chloride, sodium, and TDS will likely be met at each monitoring point

in the Upper Aquifer Shallow Zone within the model‐estimated cleanup timeframe.

As discussed in prior monitoring reports, monitoring wells MW‐03, ‐05 and ‐07 are subject to bio‐fouling

that has resulted in elevated iron and manganese concentrations. These elevated concentrations are a

localized affect at the well and not representative of aquifer conditions. Based on these conditions,

attainment of the RAOs for iron and manganese at these wells cannot be currently predicted with any

reasonable degree of accuracy.

Upper Aquifer Supply Zone

A review of the 2‐year moving average charts prepared for chloride (well MW‐25 in Attachment 8)

indicates the trend for chloride is under the RAO and stable. The data trend for manganese in the Upper

Aquifer Supply Zone wells is stable. Manganese is naturally occurring at the site and was not a significant

component of historic HCC discharges. The elevated manganese observed is likely due to localized

reducing conditions.

QUALITY CONTROL SAMPLING

The quality assurance/quality control (QA/QC) procedures for the semi‐annual monitoring and sampling

program include steps to evaluate the precision and accuracy of the laboratory analytical results and

assess the integrity of the field procedures, sample handling, and laboratory procedures.

Field QC Samples

Field QC samples, including equipment rinsate blanks and field duplicate samples, were collected during

the October 2016 groundwater sampling event. Field duplicate samples were collected from monitoring


well MW‐07. A duplicate summary evaluation is provided as Table 7. Equipment rinsate blanks were

collected during the October 2016 sampling event from monitoring and sampling equipment to evaluate

the potential for cross contamination. De‐ionized water for rinsate samples was obtained from

the laboratory. The analytical results of the equipment rinsate blanks are provided on Table 8.

Data Validation

Data validation was employed to evaluate the completeness, precision and accuracy of the

analytical results. The procedures used for validating the data are consistent with those referenced in

the National Functional Guidelines for Inorganic Data Review11 , with guidance from the appropriate

Region 9 Data Quality Indicator Tables for USEPA Methods 160.1, 200.7, 300.0, and 351.2, and for

Standard Method 2320. Data collected were checked for the following:

o Data completeness;

o Analytical holding times and sample preservation;

o Blank samples;

o Laboratory control samples/laboratory control sample duplicates;

o Surrogate recoveries;

o Laboratory duplicate sample results;

o MS/MSD samples;

o Inductively Coupled Plasma serial dilution results;

o Comparison of field duplicate results;

o Compound identification and quantification; and

o Verification of electronic data deliverable database.

Detailed data validation results are documented in a data validation report corresponding to the specific

laboratory reports reviewed during the validation process. The data validation report is included as

Attachment 10. Where validation results indicated bias or poor quality, data qualifiers are assigned to

the respective analytical data. The validation indicated that certain data were qualified due to

laboratory duplicate results, inductively coupled plasma serial dilution results, and very low average

percent recovery for MS/MSD, as described in the data validation report. The following data were

rejected: analytical results for total kjeldahl nitrogen for monitoring wells MW‐01, MW‐05, MW‐13, and

MW‐25, (based on very low percent recovery for MS/MSD analyses), all collected during October 2016.

The results from data validation indicate that the data results are considered usable, as qualified, for

future decision making purposes.

CONCLUSIONS

The groundwater data presented in this report indicate the following:

11 USEPA, 2014. National Functional Guidelines for Inorganic Data Review. August.

2016 Second Semi‐Annual Upper Aquifer Performance Monitoring Report Hilmar Cheese Company, Hilmar, California February 22, 2017

LIST OF TABLES

Table 1 Well Construction Summary and Groundwater Elevation Data

Table 2 Vertical Gradient Summary

Table 3 Summary of Analytical Results for Groundwater

Table 4 Water Quality Data for Potential Irrigation Sources to S‐63, S‐64, S‐65, and S‐67

Table 5 Remedial Action Objectives

Table 6 Monitoring Wells Selected for Moving Average Graphical Analysis

Table 7 QC Analytical Summary: Duplicate Sample Evaluation

Table 8 QC Analytical Summary: Equipment Blank Analytical Results

LIST OF FIGURES

Figure 1 Site Location Map

Figure 2 Site Plan

Figure 3 Upper Aquifer Shallow Zone Potentiometric Surface Map (October 2016)

Figure 4 Upper Aquifer Supply Zone Potentiometric Surface Map (October 12, 2016)

Figure 5‐1 Total Dissolved Solids Detected in Groundwater, Upper Aquifer Shallow Zone (October 2016)

Figure 5‐2 Total Dissolved Solids Detected in Groundwater, Upper Aquifer Supply Zone (October 2016)

Figure 6‐1 Sodium Detected in Groundwater, Upper Aquifer Shallow Zone (October 2016)

Figure 6‐2 Sodium Detected in Groundwater, Upper Aquifer Supply Zone (October 2016)

Figure 7‐1 Chloride Detected in Groundwater, Upper Aquifer Shallow Zone (October 2016)

Figure 7‐2 Chloride Detected in Groundwater, Upper Aquifer Supply Zone (October 2016)

Figure 8 Former Primary Land Reuse Area Application Timeline, 2016

Figure 9 Site Plan with TDS 2‐Year Moving Average Trend Graphs, January 2011 – October 2016, Upper Aquifer Shallow Zone


LIST OF ATTACHMENTS

Attachment 1 Monitoring and Sampling Forms (Electronic Format)

Attachment 2 Hydrographs

Attachment 3 Well Cluster Water Level Data for Vertical Data Evaluations

Attachment 4 Laboratory Analytical Results and Chain‐of‐Custody Documentation (Electronic Format)

Attachment 5 Historical Analytical Results for Groundwater (Electronic Format)

Attachment 6 Concentrations of COCs Over Time

Attachment 7 Historical Former Primary Land Reuse Area Application Timeline (January 2011 December 2015)

Attachment 8 2‐Year Moving Average of COCs in Monitoring Wells

Attachment 9 Historical Trend Charts

Attachment 10 Data Validation Report (Electronic Format)

TABLES


LIST OF TABLES

Table 1 Well Construction Summary and Groundwater Elevation Data

Table 2 Vertical Gradient Summary

Table 3 Summary of Analytical Results for Groundwater

Table 4 Water Quality Data for Potential Irrigation Sources to S‐63, S‐64, S‐65, and S‐67

Table 5 Remedial Action Objectives

Table 6 Monitoring Wells Selected for Moving Average Graphical Analysis

Table 7 QC Analytical Summary: Duplicate Sample Evaluation

Table 8 QC Analytical Summary: Equipment Blank Analytical Results

TABLE 1

WELL CONSTRUCTION SUMMARY AND GROUNDWATER ELEVATION DATA

2016 Second Semi‐Annual Upper Aquifer Performance Monitoring Report

Hilmar Cheese Company

Hilmar, California

Date Monitored

Measured

Depth to Water

(ft below TOC)

Groundwater

Elevation

(ft msl)

Total Depth

(ft bgs)

Well Diameter

(inches)

Top of Screen

(ft bgs)

Bottom of

Screen

(ft bgs)

MW‐01 UA Shallow 93.72 10/12/2016 9.80 83.92 20 2 10 20

MW‐03 UA Shallow 92.89 10/12/2016 8.69 84.20 20 2 10 20

7/18/2016 7.40 85.87

10/12/2016 9.18 84.09

MW‐05 UA Shallow 92.05 10/12/2016 8.20 83.85 20 2 10 20

7/18/2016 8.94 85.34

10/12/2016 10.47 83.81

MW‐07 UA Shallow 93.63 10/12/2016 10.02 83.61 20 2 10 20

7/18/2016 8.24 86.32

10/12/2016 11.40 83.16

7/18/2016 9.82 84.72

10/12/2016 12.24 82.30

7/18/2016 9.54 83.30

10/12/2016 9.10 83.74

7/18/2016 6.06 83.36

10/12/2016 8.03 81.39

MW‐13 UA Shallow 97.34 10/12/2016 15.64 81.70 20 2 10 20

MW‐15 UA Shallow 96.50 10/12/2016 12.93 83.57 20 2 10 20

7/18/2016 10.33 82.27

10/12/2016 11.43 81.17

7/18/2016 10.28 81.79

10/12/2016 12.56 79.51

7/18/2016 9.30 83.30

10/12/2016 8.84 83.76

Groundwater Elevation Data Well Construction Summary

Location

Identification

Water Bearing

Zone

Reference

Elevation [TOC]

(ft msl)

2 10 20

MW‐06 UA Shallow 94.28 20 2 10 20

MW‐04 UA Shallow 93.27 20

10 20

MW‐09 UA Shallow 94.54 20 2 10 20

MW‐08 UA Shallow 94.56 20 2

10 20

MW‐12 UA Shallow 89.42 20 2 10 20


10 20

MW‐17 UA Shallow 92.07 20 2 10 20


50 60MW‐18 UA Supply 92.60 62 2

Page 1 of 2

TABLE 1

WELL CONSTRUCTION SUMMARY AND GROUNDWATER ELEVATION DATA



Hilmar, California

Date Monitored

Measured

Depth to Water

(ft below TOC)

Groundwater

Elevation

(ft msl)

Total Depth

(ft bgs)

Well Diameter

(inches)

Top of Screen

(ft bgs)

Bottom of

Screen

(ft bgs)

Groundwater Elevation Data Well Construction Summary

Location

Identification

Water Bearing

Zone

Reference

Elevation [TOC]

(ft msl)

7/18/2016 7.23 82.60

10/12/2016 9.42 80.41

7/18/2016 Dry Dry

10/12/2016 Dry Dry

7/18/2016 13.15 84.24

10/12/2016 14.25 83.14

7/18/2016 65.15 32.09

10/12/2016 57.68 39.56

MW‐25 UA Supply 91.85 10/12/2016 10.30 81.55 112 4 90 110

Notes:

bgs = below ground surface

ft = foot

LA = Lower Aquifer

msl = mean sea level

TOC = top of casing

UA = Upper Aquifer

MW‐19 UA Supply 89.83 62 2 50 60

MW‐21 UA Shallow 96.45 18 4 8 18

127 4 115 125

197 4 185 195

MW‐22 UA Supply 97.39

MW‐23 LA C‐Zone 97.24

Page 2 of 2

TABLE 2

VERTICAL GRADIENT SUMMARY



Hilmar, California

Well PairsWater Bearing

ZoneDate

Vertical Distance

Between Center of

Screened Intervals

(ft)

TOC

(ft msl)

DTW

(ft below TOC)

Groundwater

Elevation

(ft msl)

Hydraulic

Head

Difference

(ft)

Vertical

Gradient

(ft/ft)a

Vertical

Gradient

Direction

MW‐06 UA Shallow Zone 94.28 8.94 85.34

MW‐22 UA Supply Zone 97.39 13.15 84.24

MW‐06 UA Shallow Zone 94.28 10.47 83.81

MW‐22 UA Supply Zone 97.39 14.25 83.14

MW‐22 UA Supply Zone 97.39 13.15 84.24

MW‐23 LA C‐Zone 97.24 65.15 32.09

MW‐22 UA Supply Zone 97.39 14.25 83.14

MW‐23 LA C‐Zone 97.24 57.68 39.56

Notes:a Vertical gradient measurement based on mid‐point of well screens.

DTW = depth to water

ft = foot

ft/ft = feet per foot

msl = mean sea level

LA = Lower Aquifer

TOC = top of casing

UA = Upper Aquifer

Vertical Gradient = hydraulic head difference/vertical distance between center of screened intervals

downward

7/18/2016 70.0 52.15 0.745 downward

Upper Aquifer Vertical Gradient

downward

95.0 0.67 0.007 downward

Upper Aquifer to Lower Aquifer Vertical Gradient (Across Corcoran Clay)

10/12/2016

10/12/2016 70.0 43.58 0.623

7/18/2016 95.0 1.10 0.012

Page 1 of 1

TABLE 3

SUMMARY OF ANALYTICAL RESULTS FOR GROUNDWATER



Hilmar, California

Sample Location Sample Date Alkalinity, Bicarbonate as

CaC

O3 (m

g/L)

Alkalinity, Carbonate as

CaC

O3 (m

g/L)

Alkalinity, Total as CaC

O3

(mg/L)

Chloride (mg/L)

Dissolved

Calcium (mg/L)

Dissolved

Iron (mg/L)

Dissolved

Magnesium

(mg/L)

Dissolved

Manganese

(mg/L)

Dissolved

Potassium (mg/L)

Dissolved

Sodium (mg/L)

Nitrate‐Nitrogen (mg/L)

Nitrogen, Total Kjeldahl

(mg/L)

Specific Conductivity

(µmhos/cm

)

Sulfate (mg/L)

Total D

issolved

Solids

(mg/L)

Upper Aquifer Shallow Zone Monitoring Wells

RAOs for Upper Aquifer Shallow Zone ‐‐ ‐‐ ‐‐ 239 ‐‐ 0.3 ‐‐ 0.34 ‐‐ 346 52 ‐‐ ‐‐ 250 912

MW‐01 10/12/2016 173 <5.0 175 34 37.6 <0.3 15.6 0.131 76.9 J 70.3 29 <0.53 R 738 28 498

MW‐03 10/12/2016 192 <5.0 193 190 37.7 6.73 9.2 2.78 16.5 J 170 <0.1 2.7 J‐ 1030 48 612

MW‐04 07/18/2016 180 <4.1 180 62 27 <0.05 6.9 0.7 24 85 11 5.1 697 25 460

MW‐04 10/12/2016 140 <4.1 140 51 22 <0.05 5.7 0.6 27 81 9.1 1.5 594 28 400

MW‐05 10/12/2016 173 <5.0 174 110 40.9 3.83 16.2 2.81 135 89.5 19 <0.53 R 1120 110 728

MW‐06 07/18/2016 490 <8.2 490 110 34 <0.05 9.6 0.7 9.6 320 0.53 2.9 1470 110 940

MW‐06 10/12/2016 480 <8.2 480 110 36 <0.05 Jo 9.1 0.7 11 320 0.64 2.5 1450 120 950

MW‐07 10/12/2016 358 <5.0 361 200 75 7.12 18 3.66 37.6 J 278 0.11 4.7 J‐ 1650 230 1050

MW‐08 07/18/2016 150 <4.1 150 43 23 <0.05 10 0.12 48 66 23 0.86 678 14 490

MW‐08 10/12/2016 110 <4.1 110 130 43 <0.05 18 0.74 77 92 24 0.53 987 29 620

MW‐09 07/18/2016 400 <8.2 400 190 96 <0.05 23 0.11 62 240 47 0.73 1910 69 1300

MW‐09 10/12/2016 440 <8.2 440 140 72 <0.05 15 0.057 53 280 35 0.75 1680 79 1100

MW‐11 07/18/2016 100 <4.1 100 45 38 <0.05 13 0.068 6.7 87 36 0.68 713 21 520

MW‐11 10/12/2016 55 <4.1 55 26 53 <0.05 19 0.18 8.2 100 73 0.56 908 30 670

MW‐12 07/18/2016 360 <8.2 360 150 150 <0.05 52 0.071 6.2 110 31 0.66 1500 90 1000

MW‐12 10/12/2016 320 <8.2 320 140 150 <0.05 48 0.023 6.2 120 43 0.46 1500 92 980

MW‐13 10/12/2016 285 <5.0 288 120 42.2 <0.3 15.6 <0.015 154 J 134 43 <0.53 R 1270 37 853

MW‐15 10/12/2016 771 19.5 791 45 36.3 1.18 10.1 0.0643 857 J 114 100 25.0 J‐ 2890 92 2890

MW‐16 07/18/2016 110 <8.2 110 76 90 <0.05 37 0.39 160 80 120 2.8 1680 63 1400

MW‐16 10/12/2016 97 <8.2 97 54 66 <0.05 25 0.16 140 62 78 2.8 1190 46 880

MW‐17 07/18/2016 170 <8.2 170 77 66 <0.05 33 0.22 78 98 70 2.2 1330 27 1000

MW‐17 10/12/2016 250 <8.2 250 49 75 <0.05 33 0.41 99 86 55 3.2 1180 33 860

MW‐21a 07/18/2016 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐

MW‐21a

10/12/2016 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐

Upper Aquifer Supply Zone Monitoring Wells

RAOs for Upper Aquifer Supply Zone ‐‐ ‐‐ ‐‐ 106 ‐‐ 0.3 ‐‐ 0.05 ‐‐ 133 34 ‐‐ ‐‐ 250 713

MW‐18 07/18/2016 170 <4.1 170 52 77 <0.05 23 0.011 2.9 44 27 0.25 822 53 560

MW‐18 10/12/2016 170 <4.1 170 58 85 <0.05 28 0.011 3.0 47 26 0.25 797 61 550

MW‐19 07/18/2016 330 <8.2 330 96 130 <0.05 30 0.031 2.2 50 4.5 0.43 1030 50 680

MW‐19 10/12/2016 330 <8.2 330 97 130 <0.05 32 0.033 2.5 54 4.6 0.44 1020 52 680

MW‐22 07/18/2016 440 <8.2 440 100 73 <0.05 38 0.96 3.1 130 <0.10 <0.20 Jo 1130 13 700

MW‐22 10/12/2016 470 <8.2 470 100 92 <0.05 43 1.0 3.3 130 <0.10 Jo <0.20 1160 12 680

MW‐25 10/12/2016 139 <5.0 141 50 46.9 <0.3 17.9 0.0861 <10 J 57 13 <0.53 R 557 41 396

Lower Aquifer C‐Zone Monitoring Well

MW‐23 07/18/2016 150 <8.2 150 280 34 <0.05 15 0.21 2.8 180 0.35 <0.20 1200 <2.0 Jo 720

MW‐23 10/12/2016 150 <8.2 150 290 38 <0.05 17 0.2 3.4 200 <0.20 <0.20 1200 <2.0 Jo 720

Notes:a Monitoring well MW‐21 was dry and therefore, not sampled. CaCO3 = calcium carbonate

mg/L = milligram per liter

μmhos/cm = micromhos per centimeter

< = less than

‐ = the result is biased low

‐‐ = not applicable

Detections are bolded.

J = The analyte was positively identified but the associated numerical value may not represent the actual concentration of the analyte in the sample due to an analytical bias in

precision or accuracy, or because the resulting concentration has been reported at a confidence level of less than 99 percent.

Jo = The analyte was positively identified but the associated estimated numerical value reported by the laboratory was less than the sample‐specific reporting limit for this analyte.

Consequently, there is a lower confidence in the accuracy of the result.

R = The sample results are rejected due to serious deficiencies in the ability to analyze the sample and meet quality control criteria. The presence or absence of the analyte cannot be

verified and data are not usable.

Page 1 of 1

TABLE 4

WATER QUALITY DATA FOR POTENTIAL IRRIGATION SOURCES TO S‐63, S‐64, S‐65, AND S‐67a



Hilmar, California

Chloride (mg/L) Sodium (mg/L)

Reusec TIDd Dairye Reusec Reusec

Apr 2011 403 140 4,600 65.5 140.0

May 2011 324 150 4,300 62.2 105.2

Jul 2011 358 43 6,200 45.5 110.0

Aug 2011 448 67 6,600 74.8 147.5

Sep 2011 333 79 7,700 64.0 125.0

Jan 2012 334 190 7,200 65.6 136.8

Mar 2012 320 19 7,600 66.0 105.8

May 2012 352 180 4,900 77.2 132.0

Jun 2012 338 150 4,100 68.8 111.3

Jul 2012 266 73 5,700 53.8 93.0

Aug 2012 243 75 1,200 48.0 80.0

Sep 2012 278 280 650 53.5 94.0

Oct 2012 208 120 2,500 46.0 74.0

Jan 2013 226 ‐‐ 3,800 46.0 72.0

Mar 2013 288 94 4,600 65.0 91.0

Apr 2013 418 120 4,800 84.8 136.0

May 2013 483 120 4,400 83.8 160.0

Jun 2013 373 46 4,900 33.3 99.0

Jul 2013 426 250 5,400 57.6 144.0

Aug 2013 363 890 6,800 71.0 127.5

Sep 2013 353 130 4,600 84.8 130.5

Oct 2013 216 50 1,900 52.0 77.2

Jan 2014 328 ‐‐ 4,600 77.4 112.8

Apr 2014 283 68 3,000 57.5 95.5

Jun 2014 335 47 4,200 62.8 118.8

Jul 2014 362 130 5,300 62.2 151.2

Aug 2014 320 91 5,000 51.8 112.8

Sep 2014 388 54 1,900 54.8 127.5

Oct 2014 284 89 2,800 36.0 93.6

Nov 2014 260 ‐‐ 3,100 38.3 90.0

Dec 2014 310 ‐‐ 3,500 46.0 105.4

Jan 2015 373 ‐‐ 3,700 54.8 117.3

Feb 2015 320 ‐‐ 4,000 46.5 115.0

Mar 2015 355 ‐‐ 1,600 57.0 124.8

Apr 2015 324 59 1,500 63.2 120.0

May 2015 415 260 2,900 79.0 140.0

Jun 2015 343 41 2,500 67.3 125.0

Jul 2015 428 140 1,600 77.8 154.0

Aug 2015 303 240 1,900 50.3 99.3

Sep 2015 265 89 1,800 40.5 89.8

Oct 2015 262 51 2,900 47.4 93.2

Nov 2015 278 ‐‐ 2,500 47.0 94.0

Dec 2015 236 ‐‐ 3,500 36.2 82.4

Jan 2016 215 ‐‐ 1,100 34.3 78.5

Discharge MonthbTDS (mg/L)

Page 1 of 2

TABLE 4

WATER QUALITY DATA FOR POTENTIAL IRRIGATION SOURCES TO S‐63, S‐64, S‐65, AND S‐67a



Hilmar, California

Chloride (mg/L) Sodium (mg/L)

Reusec TIDd Dairye Reusec ReusecDischarge Monthb TDS (mg/L)

Feb 2016 248 ‐‐ 1,500 46.8 99.0

Mar 2016 286 ‐‐ 890 51.0 106.6

Apr 2016 370 130 2,100 72.3 145.0

May 2016 365 87 3,200 68.0 141.0

Jun 2016 334 64 4,200 60.4 119.2

Jul 2016 395 94 1,500 65.0 142.5

Aug 2016 398 150 2,800 69.5 141.5

Sep 2016 250 130 3,500 50.0 88.0

Oct 2016 195 39 5,200 36.5 71.3

Nov 2016 348 ‐‐ 2,900 65.3 120.0

Dec 2016 234 ‐‐ 3,700 37.6 84.8

Notes:

HCC = Hilmar Cheese Company


TDS = total dissolved solids

TID = Turlock Irrigation District

WDR = Waste Discharge Requirements

‐‐ = not analyzed

e Dairy wastewater based on data from Table 10 in HCC Quarterly Monitoring Reports.

a S‐63, S‐64, S‐65, and S‐67 are former Primary Lands now designated as Reuse Areas. S‐67 became a reuse area in first quarter

2013. Data provided as reported in the HCC Quarterly Monitoring Report submittals dated July 2011, October 2011, January

2012, April 2012, July 2012, October 2012,

January 2013, April 2013, July 2013, October 2013, January 2014, April 2014, and July 2014; submitted per WDR Order No.R5‐

2010‐0008. TDS is the only parameter reported for all irrigation sources.

b There were no discharges in January through March 2011, June 2011, October through December 2011, February 2012, April

2012, November through December 2012, February 2013, April through May 2013, November through December 2013,

February through March 2014, and May 2014.c Reuse data is a monthly average from Table 2a in HCC Quarterly Monitoring Reports.d TID water quality based on data from Table 8 in HCC Quarterly Monitoring Reports.

Page 2 of 2

TABLE 5

REMEDIAL ACTION OBJECTIVES



Hilmar, California

Upper Aquifer

Shallow Zone

Upper Aquifer

Supply Zone

Chloride 239 106

Iron 0.3 0.3

Manganese 0.34 0.05

Nitrate as Nitrogen 52 34

Sodium 346 133

Sulfate 250 250

Total Dissolved Solids (TDS) 912 713

Notes:

Source:

a All units in milligrams per liter.

Remedial Action Objective (RAO)a,b,c

Constituent

b RAOs are provided for Constituents of Concern (COCs) that have Maximum Contaminant Levels

(MCLs), with the exception of: (1) electrical conductivity, as TDS is a representative indicator, and

(2) sodium, which does not have a MCL but was requested as a key indicator constituent by the

Central Valley Regional Water Quality Control Board for the Upper Aquifer groundwater modeling

of remedial alternatives. The COCs without MCLs will be represented by the TDS RAO. c The RAOs reflect the lower of the MCL or agricultural use level, unless lower than the ambient

screening threshold, in which case the ambient screening threshold was selected as the RAO, as

described in the Upper Aquifer Remedial Action Plan (Jacobson James & Associates [JJ&A], 2013).

JJ&A, 2013. Upper Aquifer Remedial Action Plan, Hilmar Cheese Company, Hilmar, California .

Revised February 28.

Page 1 of 1

TABLE 6

MONITORING WELLS SELECTED FOR MOVING AVERAGE GRAPHICAL ANALYSIS



Hilmar, California

Cl Fe Mn Na NO3‐N SO4 TDS

MW‐01 No No Yes No Yes No Yes

MW‐03 No Yes Yes No No No No

MW‐04 No No Yes No No No No

MW‐05 No Yes Yes No No No No

MW‐06 No No Yes Yes No Yes Yes

MW‐07 Yes Yes Yes Yes No Yes Yes


MW‐09 No No Yes Yes No No Yes

MW‐11 No No Yes No Yes No No

MW‐12 No No No No No No Yes

MW‐13 No No No Yes Yes No Yes

MW‐15 No Yes No No Yes No Yes



MW‐21 No No No No Yes No No

MW‐18 No No No No No No No

MW‐19 No No No No No No No


MW‐25 Yes No Yes No No No No

Notes:

Cl = chloride

Fe = iron

Mn = manganese

Na = sodium

NO3‐N = nitrate as nitrogen

SO4 = sulfate

TDS = total dissolved solids

UA = Upper Aquifer

No = all detections from 4Q2014 through 4Q2016 below RAO; data not included in the moving average charts

(Attachment 8).

Zone Well IdentificationConstituents of Concern

UA Shallow

UA Supply

Yes = at least one detection above Remedial Action Objective (RAO) from 4Q2014 through 4Q2016; data included

in the moving average charts (Attachment 8).

Page 1 of 1

TABLE 7

QC ANALYTICAL SUMMARY: DUPLICATE SAMPLE EVALUATION



Hilmar, California

Sample Location

Sample ID

Sample Date

MW‐07

W‐MW‐07‐A/AF

10/12/2016

Primary

MW‐07

W‐MW‐07‐B/BF

10/12/2016

Duplicate

RPD

Compound Units

Alkalinity, Bicarbonate as CaCO3 mg/L 358 364 2%

Alkalinity, Carbonate as CaCO3 mg/L <5.0 <5.0 ‐‐

Alkalinity, Total as CaCO3 mg/L 361 366 1%

Chloride mg/L 200 200 0%

Dissolved Calcium mg/L 75 76.6 2%

Dissolved Iron mg/L 7.12 7.22 1%

Dissolved Magnesium mg/L 18 18.5 3%

Dissolved Manganese mg/L 3.66 3.77 3%

Dissolved Potassium mg/L 37.6 J 38.5 J 2%

Dissolved Sodium mg/L 278 285 2%

Nitrate‐Nitrogen mg/L 0.11 <0.1 ‐‐

Nitrogen, Total Kjeldahl mg/L 4.7 J‐ 4.8 J‐ 2%

Solids, total dissolved mg/L 1050 1060 1%

Specific Conductivity µmhos/cm 1650 1680 2%

Sulfate mg/L 230 230 0%

Notes:

CaCO3 = calcium carbonate

ID = identification


QC = quality control

RPD = relative percentage difference


< = less than

‐‐ = not applicable

% = percent


See Attachment 10 for data qualifier definitions.

Sample IDs ending in "A" are primary, non‐field filtered, samples. Sample IDs ending in "AF" are primary, field

filtered, samples. Sample IDs ending in "B" are duplicate, non‐field filtered, samples. Sample IDs ending in "BF" are

duplicate, field filtered, samples.

Page 1 of 1

TABLE 8

QC ANALYTICAL SUMMARY: EQUIPMENT BLANK ANALYTICAL RESULTSa



Hilmar, California

Sample Location

Sample ID

Sample Date

Equipment Blank

EB‐101216‐A/AF

10/12/2016

Equipment Blank

EB‐MW‐25‐A/AF

10/12/2016

Field Blank

FB‐MW‐05‐A

10/12/2016

Compound Units

Alkalinity, Bicarbonate as CaCO3 mg/L <5.0 <5.0 ‐‐

Alkalinity, Carbonate as CaCO3 mg/L <5.0 <5.0 ‐‐

Alkalinity, Total as CaCO3 mg/L <10 <13 ‐‐

Chloride mg/L <0.1 <0.1 <0.1

Dissolved Calcium mg/L <1 <1 ‐‐

Dissolved Iron mg/L <0.3 <0.3 ‐‐

Dissolved Magnesium mg/L <5 <5 ‐‐

Dissolved Manganese mg/L <0.015 <0.015 ‐‐

Dissolved Potassium mg/L <10 <10 ‐‐

Dissolved Sodium mg/L <10 <10 ‐‐

Nitrate‐Nitrogen mg/L <0.1 <0.1 <0.1

Nitrogen, Total Kjeldahl mg/L <0.53 <0.53 ‐‐

Specific Conductivity µmhos/cm 1.7 1.5 2.2

Solids, total dissolved mg/L <100 <100 <100

Sulfate mg/L <0.1 <0.1 <0.1

Notes:

a Deionized water for equipment blank samples was obtained from the laboratory.


ID = identification


QC = quality control


< = less than



Sample IDs ending in "A" are non‐field filtered samples. Sample IDs ending in "AF" are field filtered, samples.

Page 1 of 1

FIGURES


LIST OF FIGURES

Figure 1 Site Location Map

Figure 2 Site Plan

Figure 3 Upper Aquifer Shallow Zone Potentiometric Surface Map (October 2016)

Figure 4 Upper Aquifer Supply Zone Potentiometric Surface Map (October 12, 2016)

Figure 5‐1 Total Dissolved Solids Detected in Groundwater, Upper Aquifer Shallow Zone (October 2016)

Figure 5‐2 Total Dissolved Solids Detected in Groundwater, Upper Aquifer Supply Zone (October 2016)

Figure 6‐1 Sodium Detected in Groundwater, Upper Aquifer Shallow Zone (October 2016)

Figure 6‐2 Sodium Detected in Groundwater, Upper Aquifer Supply Zone (October 2016)

Figure 7‐1 Chloride Detected in Groundwater, Upper Aquifer Shallow Zone (October 2016)

Figure 7‐2 Chloride Detected in Groundwater, Upper Aquifer Supply Zone (October 2016)

Figure 8 Former Primary Land Reuse Area Application Timeline, 2016

Figure 9 Site Plan with TDS 2‐Year Moving Average Trend Graphs, January 2011 – October 2016, Upper Aquifer Shallow Zone

© OpenStreetMap (and) contributors, CC-BY-SA

HILMAR CHEESE COMPANYHILMAR, CALIFORNIA

9/21/13 TJDPGDATE DRAWN BY APPR. BY

LOCATION

Path: J:\GIS\Hilmar\Reports\Adhoc\Figure 1 Hilmar Site Location Map_2015.mxd SOURCE:NATIONAL GEOGRAPHIC CALIFORNIA TOPO VERSION 4.2

SITE LOCATION

0 1.5

Miles

FIGURE 1

SITE LOCATION MAP

"m

"

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"

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m

m

m

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&

&

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&

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LATERAL NO. 6

LATE

RAL N

o. 7

MW-37

MW-36

MW-35

MW-34

MW-25

MW-23MW-22

MW-21

MW-19

MW-18

MW-16 MW-15

MW-13

MW-12

MW-11MW-09

MW-08

MW-07

MW-05

MW-04

MW-03

MW-01

MW-17

MW-06

AUGUST AVENUE

JOHNSON AVENUE

AMERICAN AVENUE

LAND

ER AV

ENUE

TEGN

ER AV

ENUE

COLU

MBUS

AVEN

UE

OSLO ROAD

OSLO

STRE

ET

S-52

S-46

S-63S-44

S-08

S-13

S-11

S-30

S-53

S-29

S-58

S-51

S-06

S-31S-33

S-45

S-54

S-47

S-64

S-25

S-07

S-56

S-22

S-21

S-26

S-24

S-40

S-50

S-43

S-34

S-09

S-67

S-28

S-57

S-48

S-61

S-65

S-55

S-60

S-23

S-41

S-62

Pa

th:

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ite P

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APPR. BYDRAWN BYDPGDATE12/16/15PROJECT No.01.HCC.2014

FIGURE 2

SITE PLANTJ

HILMAR CHEESE COMPANYHILMAR, CALIFORNIA£0 1,000

SCALE IN FEET

LEGEND

S-63

&<

©̈©

©

"

m

HCC FACILITY

EXTENT OF HCC FACILITY AND HISTORICAL PRIMARY LANDS

CURRENT REUSE LAND AREA; FORMER PRIMARY LAND (NOTE: S-67 HAS NOT BEEN USED TO DATE)

UPPER AQUIFER SHALLOW ZONE MONITORING WELL

LOWER AQUIFER MONITORING WELLUPPER AQUIFER SUPPLY ZONE MONITORING WELL

CURRENT REUSE AREA

TURLOCK IRRIGATION DISTRICT LATERAL CANAL

Path: J:\GIS\Hilmar\Reports\2016\SemiAnnual2\Figure 3 POT 4Q2016 UAShallow.mxd

SOURCE: HILMAR CHEESE COMPANY QUARTERLY MONITORING REPORT

0 1,600

SCALE IN FEET

£TJ

DATE DRAWN BY APPR. BYPROJECT NO.


HCC.2016 1/2/17 DPG

FIGURE 3UPPER AQUIFER SHALLOW ZONEPOTENTIOMETRIC SURFACE MAP

(OCTOBER 2016)

Path: J:\GIS\Hilmar\Reports\2016\SemiAnnual2\Figure 4 POT 4Q2016 UASupply.mxd

"

m

"

m

"

m

"

m

AMERICAN AVENUE

OSLO ROAD

AUGUST AVENUE

LAND

ER AV

ENUE

OSLO

STRE

ET

COLU

MBUS

AVEN

UE

8283

81

MW-2581.55

MW-2283.14

MW-1980.41

MW-1883.76

£0 1,200

SCALE IN FEET

LEGEND

TJDATE DRAWN BY APPR. BYPROJECT NO.


HCC.2016 1/12/17 ML

FIGURE 4UPPER AQUIFER SUPPLY ZONE

POTENTIOMETRIC SURFACE MAP(OCTOBER 12, 2016)

UPPER AQUIFER SUPPLY ZONE MONITORING WELL"

m

83.14 POTENTIOMETRIC SURFACE ELEVATION (ft-msl)

POTENTIOMETRIC SURFACE CONTOUR(DASHED WHERE INFERRED)

GROUNDWATER FLOW DIRECTION



0.0008 ft/ft APPROXIMATE HORIZONTAL GROUNDWATER GRADIENT

ft/ft FEET PER FOOT

ft-msl FEET ABOVE MEAN SEA LEVEL

0.00

08 ft

/ft

Path: J:\GIS\Hilmar\Reports\2016\SemiAnnual2\Figure 5-1 TDS 4Q2016 UAShallow.mxd

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AMERICAN AVENUE

OSLO ROAD

AUGUST AVENUE

LAND

ER AV

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OSLO

STRE

ET

COLU

MBUS

AVEN

UE

1000

MW-17860

MW-16880

MW-13853

MW-12980

MW-11670

MW-08620

MW-06950

MW-05728

MW-04400

MW-03612

MW-01498

MW-152890

MW-091100

MW-071050

£0 1,200

SCALE IN FEET

LEGEND



HCC.2016 1/27/17 DPG

FIGURE 5-1TOTAL DISSOLVED SOLIDS DETECTED IN

GROUNDWATER, UPPER AQUIFERSHALLOW ZONE (OCTOBER 12, 2016)

UPPER AQUIFER SHALLOW ZONE MONITORING WELL&<

400 TOTAL DISSOLVED SOLIDS (mg/L)



UPPER AQUIFER SHALLOW ZONE MONITORING WELL REPORTEDCONSTITUENT ABOVE RAO OF 912 mg/L&<(

mg/L MILLIGRAM PER LITER

RAO REMEDIAL ACTION OBJECTIVETOTAL DISSOLVED SOLIDS CONCENTRATION CONTOUR (mg/L)(DASHED WHERE INFERRED)

Path: J:\GIS\Hilmar\Reports\2016\SemiAnnual2\Figure 5-2 TDS 4Q2016 UASupply.mxd

"

m

"

m

"

m

"

m

LAND

ER AV

ENUE

AMERICAN AVENUE

OSLO ROAD

AUGUST AVENUE

OSLO

STRE

ET

COLU

MBUS

AVEN

UE

MW-25396

MW-22680

MW-19680

MW-18550

£0 1,200

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HCC.2016 12/12/16 DPG

FIGURE 5-2TOTAL DISSOLVED SOLIDS DETECTED IN

GROUNDWATER, UPPER AQUIFER SUPPLY ZONE (OCTOBER 2016)

LEGEND

UPPER AQUIFER SUPPLY ZONE MONITORING WELL

620 TOTAL DISSOLVED SOLIDS (mg/L)



"

m


RAO REMEDIAL ACTION OBJECTIVE

RAO = 713 mg/L

Path: J:\GIS\Hilmar\Reports\2016\SemiAnnual2\Figure 6-1 Na 4Q2016 UAShallow.mxd

&<

&<

&<

&<

&< &<

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&< &<

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&<&<

&<

AMERICAN AVENUE

OSLO ROAD

AUGUST AVENUE

LAND

ER AV

ENUE

OSLO

STRE

ET

COLU

MBUS

AVEN

UE

MW-1786

MW-1662 MW-15

114

MW-13134

MW-0892

MW-07278

MW-0481

MW-03170

MW-12120

MW-11100

MW-09280

MW-06320

MW-0589.5

MW-0170.3

£0 1,200

SCALE IN FEET



HCC.2016 DPG

FIGURE 6-1SODIUM DETECTED IN GROUNDWATER,

UPPER AQUIFER SHALLOW ZONE (OCTOBER 2016)

LEGEND


RAO = 346 mg/L



1/11/17


RAO REMEDIAL ACTION OBJECTIVENA NOT ANALYZED

114 SODIUM (mg/L)

Path: J:\GIS\Hilmar\Reports\2016\SemiAnnual2\Figure 6-2 Na 4Q2016 UASupply.mxd

"

m

"

m

"

m

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m

AMERICAN AVENUE

OSLO ROAD

AUGUST AVENUE

LAND

ER AV

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OSLO

STRE

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COLU

MBUS

AVEN

UE

MW-2557

MW-1954

MW-1847

MW-22130

£0 1,200

SCALE IN FEET



HCC.2016 12/12/16 DPG

FIGURE 6-2SODIUM DETECTED IN GROUNDWATER,

UPPER AQUIFER SUPPLY ZONE (OCTOBER 2016)

LEGEND


m

57 SODIUM (mg/L)



RAO = 133 mg/Lmg/L MILLIGRAM PER LITER

RAO REMEDIAL ACTION OBJECTIVESEE ATTACHMENT 10 FOR DATA QUALIFIERS

Path: J:\GIS\Hilmar\Reports\2016\SemiAnnual2\Figure 7-1 CL 4Q2016 UAShallow.mxd

&<

&<

&<

&<

&< &<

&<

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AMERICAN AVENUE

OSLO ROAD

AUGUST AVENUE

LAND

ER AV

ENUE

OSLO

STRE

ET

COLU

MBUS

AVEN

UE

MW-1749

MW-1654 MW-15

45

MW-1126

MW-0451

MW-0134

MW-13120

MW-12140

MW-09140

MW-08130

MW-07200

MW-06110

MW-05110

MW-03190

200

£0 1,200

SCALE IN FEET



HCC.2016 1/27/17 DPG

FIGURE 7-1CHLORIDE DETECTED IN GROUNDWATER,

UPPER AQUIFER SHALLOW ZONE (OCTOBER 2016)

LEGEND


150 CHLORIDE (mg/L)




CHLORIDE CONCENTRATION CONTOUR (mg/L)(DASHED WHERE INFERRED)


RAO = 239 mg/L

Path: J:\GIS\Hilmar\Reports\2016\SemiAnnual2\Figure 7-2 CL 4Q2016 UASupply.mxd

"

m

"

m

"

m

"

m

AMERICAN AVENUE

OSLO ROAD

AUGUST AVENUE

LAND

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MBUS

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MW-2550

MW-1997

MW-1858

MW-22100

£0 1,200

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HCC.2016 12/12/16 DPG

FIGURE 7-2CHLORIDE DETECTED IN GROUNDWATER,

UPPER AQUIFER SUPPLY ZONE (OCTOBER 2016)

LEGEND


m

97 CHLORIDE (mg/L)





RAO = 106 mg/L

HCC.2016 DPG1/27/17 TJ

HILMAR CHEESE COMPANYHILMAR, CALIFORNIA FORMER PRIMARY LAND REUSE AREA

APPLICATION TIMELINE, 2016

FIGURE 8

TOTAL DISSOLVED

SOLIDS (TDS)MONTHLY AVERAGES

CHLORIDE AND SODIUM

MONTHLY AVERAGES FOR HCC

REUSE WATER

REUSE AREA APPLICATION

HISTORY

Flow

for T

ID F

resh

wat

er a

nd T

otal

Ap

plic

atio

n (m

g/d)

Chl

orid

e (m

g/L)

TDS

for H

CC

Reu

se W

ater

and

TI

D F

resh

wat

er (m

g/L)

TID Freshwater Application AreaHCC Reuse Water and Dairy Wastewater Application AreaAPPLICATION

COLOR CODES

Flow

for D

airy

Was

tew

ater

(mg/

d)

and

HC

C R

euse

Wat

erTD

S fo

r Dai

ry W

aste

wat

er (m

g/L)

NOTES

HCC Reuse Water, TID Freshwater and Dairy Wastewater Application Area

mg/L =mg/d =

milligrams per litermillion gallons per day

2,3,4

1

HCC Reuse Water

Jan 2016 Feb 2016 Apr 2016 May 2016 June 2016Mar 2016

Hilmar Cheese Company (HCC) Reuse Water and Turlock Irrigation District (TID) Freshwater Application Area

1. Chloride and Sodium concentrations are not reported for TID water or Dairy Wastewater.

2. Application data and history for Reuse Areas within the extent of the former Primary Lands; data not available for former Primary lands not owned by HCC or not receiving HCC Reuse water.

3. Source: Hilmar Cheese Company Quarterly Monitoring Report dated April 14, July 19, October 18, 2016 and January 27, 2017.

4. TID water may have been applied to the former Primary Lands identified as S-63, S-64 and S-65 prior to April 2011; however, HCC was not required to report for this period.

Sodi

um (m

g/L)

Jan 2016 Feb 2016 Mar 2016 Apr 2016 May 2016 Jun 2016

July 2016 Aug 2016 Sep 2016 Oct 2016 Nov 2016 Dec 2016

0.137

0.063 0.070 0.051 0.032

0.137

Jul 2016 Aug 2016 Sep 2016 Oct 2016 Nov 2016 Dec 2016

&<

&<

&<

&<

&< &<

&<

&< &<

&<

&<

&<&<

&<

&<S-67

77

LATERAL NO. 6

MW-21

MW-17

MW-16

MW-15

MW-13

MW-12

MW-11MW-09

MW-08

MW-07MW-06

MW-05

MW-04

MW-03

MW-01

AUGUST AVENUE

LAND

ER

AVE

NUECO

LUMB

US AV

ENUE

OSLO ROAD

OSLO

STRE

ET

S-63

S-08

S-29

S-06

S-64

S-25

S-07

S-26

S-40

S-65

82

8180 83

84

828180 83

Pa

th:

J:\G

IS\H

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6\S

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\Fig

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OC

4Q

20

16 U

AS

hallo

w 2

yr.m

xd

S-63

DRAWN BY FIGURE1/3/17

DATEAPPROVED BYDPG LG

0 400

SCALE IN FEET

£PROJECT No.

HCC.2016

SITE PLAN WITH TDS 2-YEAR MOVING AVERAGETREND GRAPHS JANUARY 2011 - OCTOBER 2016,

UPPER AQUIFER SHALLOW ZONEHILMAR CHEESE COMPANY

HILMAR, CALIFORNIA

9

mg/L - MILLIGRAM PER LITERRAO - REMEDIAL ACTION OBJECTIVETDS - TOTAL DISSOLVED SOLIDS

LEGEND

CURRENT REUSE AREA

HCC FACILITY AND FORMER PRIMARY LANDS


HCC FACILITY

&< UPPER AQUIFER SHALLOW ZONE MONITORING WELL

GROUNDWATER FLOW DIRECTION

POTENTIOMETRIC SURFACE CONTOUR (OCTOBER 2015)

ATTACHMENT 1

MONITORING AND SAMPLING FORMS

(ELECTRONIC FORMAT)

9001 NORTH LANDER AVENUE

HILMAR, CA

October 12, 2016

10624 OLIVE AVENUE, OAKDALE, CALIF. 95361 * OFFICE (209) 847-8757 * FAX (209) 847-7744

4Q2016

GROUNDWATER

FIELD MONITORING

SUMMARY REPORT

SITE:

HILMAR CHEESE COMPANY

JACOBSON JAMES & ASSOCIATES

SAMPLE LOCATION / MW - 1 DATE: 10/12/2016

PROJECT NAME: ANALYSIS PERFORMED: SEE CHAIN OF CUSTODYADDRESS: SAMPLE TIME: 12:05CITY, STATE: SAMPLE CONTAINERS: SEE CHAIN OF CUSTODYSITE CONTACT: PRESERVATIVES: SEE CHAIN OF CUSTODYCONSULTANT: LAB. ANALYSIS BY: ACCUTEST LABS

PROJECT MANAGER: MONUMENT: FLUSHSAMPLER: WELL CASING MATERIAL : PVCSIGNED: WELL CASING DIA. : 2" / 0.1632SAMPLE MEDIA: P.I.D. READING / ODOR: N/A NONETOP OF CASING ELEVATION: 93.72' MSL COLOR: CLEARDEPTH TO WATER: (feet.100th's) 9.80 FEET CALC. PURGE VOL.: 1.72 GAL.DEPTH OF WELL: (feet.100th's) 20.34 FEET TOTAL VOLUME PURGED: 6.00 GAL.STANDING WATER COLUMN: 10.54 FEET DEPTH OF PUMP: ~ 19 FEET

TIME CALCULATED ACTUAL DRAW PUMPING pH E. C. TEMP. O.R.P. DISSOLVED TURBIDITYCASING VOLUME VOLUME DOWN RATE OXYGEN

PER PURGE PURGED (D.T.W.) ( GPM ) (units) (uS/cm) (Celsius) (Mvolts) (PPM) (N.T.U.)

11:40 0 0 10.03 0.25 7.41 806 24.0 71 2211:48 1.72 2.0 10.05 " 7.33 807 24.1 7211:56 3.44 2.0 9.99 " 7.20 808 24.3 7512:04 5.16 2.0 9.94 " 7.18 808 24.3 77 1412:05 SAMPLED

PURGE METHOD: CENTRIFUGAL PUMP & WATERRA

SAMPLE METHOD: CENTRIFUGAL PUMP & WATERRA

D. T. W. AFTER PURGE: D. T. W. AT SAMPLE TIME: 9.94'WELL INTEGRITY: CAP & SEAL ARE SECURE.

WELL LOCATION: SEE SITE MAP.

REMARKS:

WEATHER: CLEAR / COOL WIND: LIGHT BREEZE

QUALITY CONTROL: ALL PURGING AND MONITORING EQUIPMENT WAS CLEANED AS NECESSARY.

DEDICATED PURGE TUBING IS INSTALLED IN EACH WELL. NEW NITRILE GLOVES.

CONTAINMENT: NO CONTAINMENT / PURGE WATER TO THE GROUND

INSTRUMENTATION: MYRON 6P MULTI PROBE METER Y.S.I. DISSOLVED OXYGEN METER

HERON D.T.W. METER OAKTON TURBIDITY METER

HOWARD REAL

DEL-TECH GEOTECHNICAL SUPPORT SERVICES, INC.

MONITORING WELL FIELD LOG 2016

HILMAR CHEESE COMPANY9001 N. LANDER AVENUE

HILMAR, CA.

JACOBSON | JAMES

TONY MIKACICHDEL-TECH / DON LIGHT

GROUNDWATER

FIELD PARAMETERS



PROJECT MANAGER: MONUMENT: FLUSH

SAMPLER: WELL CASING MATERIAL : PVCSIGNED: WELL CASING DIA. : 2" / 0.1632SAMPLE MEDIA: P.I.D. READING / ODOR: N/A MUSTYTOP OF CASING ELEVATION: 92.89' MSL COLOR: BROWN TO CLEARDEPTH TO WATER: (feet.100th's) 8.69 FEET CALC. PURGE VOL.: 2.62 GAL.DEPTH OF WELL: (feet.100th's) 24.77 FEET TOTAL VOLUME PURGED: 9.00 GAL.STANDING WATER COLUMN: 16.08 FEET DEPTH OF PUMP: ~ 23 FEET



11:10 0 0 8.70 0.5 7.30 1060 27.1 45 5811:16 2.62 3.0 8.70 " 7.03 1110 28.2 -411:22 5.25 3.0 8.73 " 6.98 1127 28.1 -411:28 7.87 3.0 8.73 " 6.96 1132 28.2 -2 511:30 SAMPLED





REMARKS:







9001 N. LANDER AVENUE



HILMAR CHEESE COMPANY

HILMAR, CA.HOWARD REAL

JACOBSON | JAMES

TONY MIKACICH

DEL-TECH / DON LIGHT

GROUNDWATER

FIELD PARAMETERS



PROJECT MANAGER: MONUMENT: POSTSAMPLER: WELL CASING MATERIAL : PVCSIGNED: WELL CASING DIA. : 2" / 0.1632SAMPLE MEDIA: P.I.D. READING / ODOR: N/A NONETOP OF CASING ELEVATION: 92.05' MSL COLOR: LIGHT BROWN TO CLEARDEPTH TO WATER: (feet.100th's) 8.20 FEET CALC. PURGE VOL.: 2.55 GAL.DEPTH OF WELL: (feet.100th's) 23.80 FEET TOTAL VOLUME PURGED: 7.50 GAL.STANDING WATER COLUMN: 15.60 FEET DEPTH OF PUMP: ~ 22 FEET



13:50 0 0 8.29 0.5 7.14 1532 23.3 140 3013:55 2.55 2.5 8.40 " 7.02 1235 21.9 11814:00 5.09 2.5 8.48 " 6.98 1197 21.8 11014:05 7.64 2.5 8.57 " 6.97 1184 21.8 102 814:05 SAMPLED





REMARKS:











JACOBSON | JAMES


GROUNDWATER

FIELD PARAMETERS



PROJECT MANAGER: MONUMENT: FLUSHSAMPLER: WELL CASING MATERIAL : PVCSIGNED: WELL CASING DIA. : 2" / 0.1632SAMPLE MEDIA: P.I.D. READING / ODOR: N/A MUSTYTOP OF CASING ELEVATION: 95.98' MSL COLOR: LIGHT BROWN TO CLEARDEPTH TO WATER: (feet.100th's) 10.02 FEET CALC. PURGE VOL.: 2.24 GAL.DEPTH OF WELL: (feet.100th's) 23.76 FEET TOTAL VOLUME PURGED: 7.50 GAL.STANDING WATER COLUMN: 13.74 FEET DEPTH OF PUMP: ~ 22 FEET



10:45 0 0 10.04 0.5 7.04 1952 22.7 150 7210:50 2.24 2.5 10.07 " 6.80 1776 23.1 5310:55 4.48 2.5 10.10 " 6.77 1778 23.1 1211:00 6.73 2.5 10.13 " 6.74 1780 23.1 8 211:00 SAMPLED





REMARKS:







GROUNDWATER





JACOBSON | JAMES


FIELD PARAMETERS

DUPLICATE TAKEN HERE.



PROJECT MANAGER: MONUMENT: POSTSAMPLER: WELL CASING MATERIAL : PVCSIGNED: WELL CASING DIA. : 2" / 0.1632SAMPLE MEDIA: P.I.D. READING / ODOR: N/A NONETOP OF CASING ELEVATION: 97.34' MSL COLOR: CLEARDEPTH TO WATER: (feet.100th's) 15.64 FEET CALC. PURGE VOL.: 1.18 GAL.DEPTH OF WELL: (feet.100th's) 22.90 FEET TOTAL VOLUME PURGED: 4.50 GAL.STANDING WATER COLUMN: 7.26 FEET DEPTH OF PUMP: ~ 21 FEET



12:30 0 0 15.65 0.25 7.38 1257 22.3 116 1412:36 1.18 1.5 15.66 " 7.27 1335 22.3 10512:42 2.37 1.5 15.66 " 7.24 1360 22.3 10112:48 3.55 1.5 15.67 " 7.23 1363 22.4 107 812:48 SAMPLED





REMARKS:







TONY MIKACICH





JACOBSON | JAMES

DEL-TECH / DON LIGHT

GROUNDWATER

FIELD PARAMETERS



PROJECT MANAGER: MONUMENT: POSTSAMPLER: WELL CASING MATERIAL : PVCSIGNED: WELL CASING DIA. : 2" / 0.1632SAMPLE MEDIA: P.I.D. READING / ODOR: N/A MUSTYTOP OF CASING ELEVATION: 96.50' MSL COLOR: BROWNDEPTH TO WATER: (feet.100th's) 12.93 FEET CALC. PURGE VOL.: 1.63 GAL.DEPTH OF WELL: (feet.100th's) 22.89 FEET TOTAL VOLUME PURGED: 6.00 GAL.STANDING WATER COLUMN: 9.96 FEET DEPTH OF PUMP: ~ 21 FEET



13:00 0 0 12.95 0.25 8.04 2981 24.6 133 2213:08 1.63 2.0 12.97 " 7.72 3095 23.6 13813:16 3.25 2.0 12.99 " 7.70 3072 24.0 13713:24 4.88 2.0 13.00 " 7.65 3069 24.1 135 1513:24 SAMPLED





REMARKS:







HOWARD REAL




HILMAR, CA.

JACOBSON | JAMES


GROUNDWATER

FIELD PARAMETERS



PROJECT MANAGER: MONUMENT: FLUSHSAMPLER: WELL CASING MATERIAL : PVCSIGNED: WELL CASING DIA. : 4" / 0.6528SAMPLE MEDIA: P.I.D. READING / ODOR: N/A NONETOP OF CASING ELEVATION: MSL COLOR: CLEARDEPTH TO WATER: (feet.100th's) 10.30 FEET CALC. PURGE VOL.: 65.80 GAL.DEPTH OF WELL: (feet.100th's) 111.10 FEET TOTAL VOLUME PURGED: 198.00 GAL.STANDING WATER COLUMN: 100.80 FEET DEPTH OF PUMP: ~ 105 FEET



14:30 0 0 10.30 2.0 8.20 584 21.4 93 515:03 65.80 66.0 10.32 " 7.90 599 21.1 10115:36 131.60 66.0 10.31 " 7.85 606 21.0 10216:09 197.41 66.0 10.30 " 7.83 610 21.0 107 416:10 SAMPLED

PURGE METHOD: 3" GRUNDFOS STAINLESS STEEL SUBMERSIBLE PUMP.

SAMPLE METHOD: 3" GRUNDFOS STAINLESS STEEL SUBMERSIBLE PUMP.



REMARKS:







HILMAR, CA.




FIELD PARAMETERS

HOWARD REALJACOBSON | JAMES


GROUNDWATER

QTR. 1 QTR. 2 QTR. 3 QTR. 4 TOTAL

DATE MONUMENT 4/14/16 10/12/16 DEPTH

LOCATION

MW - 1 FLUSH 10.62 9.80 20.34'

MW - 3 FLUSH 9.59 8.69 24.77'

MW - 4 POST 9.94 9.18 26.04'

MW - 5 POST 8.94 8.20 23.80'

MW - 6 FLUSH 11.13 10.47 26.80'

MW - 7 FLUSH 10.72 10.02 23.60'

MW - 8 POST 12.10 11.40 21.55'

MW - 9 POST 12.60 12.24 26.20'

MW - 11 FLUSH 9.74 9.10 19.74'

MW - 12 FLUSH 9.19 8.03 18.60'

MW - 13 POST 16.76 15.64 22.90'

MW - 15 POST 13.91 12.93 22.89'

MW - 16 POST 11.92 11.43 23.10'

MW - 17 POST 12.22 12.56 23.40'

MW - 18 FLUSH 9.54 8.84 61.15'

MW - 19 FLUSH 10.69 9.42 58.45'

MW - 21 FLUSH 14.79 DRY 15.85'

MW - 22 POST 14.82 14.25 130.30'

MW - 23 POST 44.45 57.68 207.40'

MW - 25 FLUSH 10.40 10.30 111.10'

WELLS SAMPLED

NOTE :

ALL MEASUREMENTS ARE MADE FROM THE NORTH SIDE AND TOP EDGE OF THE WELL

CASING. THE TOP OF CASING WITH A NOTCH OR PERMENANT MARKINGS, WHICH EVER ONE

CONDITION IS APPROPRIATE.

DEL-TECH GEOTECHNICAL SUPPORT, INC.(209) 847-8757 (OFFICE) * (209) 847-7744 (FAX) * [email protected] (Email)

HILMAR CHEESE COMPANY9001 N. LANDER, HILMAR, CA

J & J - MONITORING WELL FIELD SUMMARY LOG 2016

DEPTH TO WATER MEASUREMENTS

PROJECT NAME: PROJECT MANAGER:

ADDRESS: SAMPLER:

CITY, STATE: SIGNED:

SITE CONTACT: SAMPLE MEDIA:

CONSULTANT: MONTH :

SERIAL Ph Ph Ph COND. TURBIDITY TURBIDITY INST.

# 4 7 10 1413 MHOS 20 100 CONDITION

READING READING READING (Celsius) (N.T.U.) (N.T.U.)

DATE

TIME10/12/16 6207003 GOOD

7:02 PRE-CAL. 4.06 7.17 9.97 1423 20.0 100.1

7:05 CALIBRATION 4.00 7.00 10.00 1413 20 100

CAL. SUCCESSFUL ( Y/N ) Y Y Y Y Y Y

SATIFIES PROTOCOL ? Y Y Y Y Y Y

CAL. BY :

DATE

TIME

PRE-CAL.

CALIBRATION

CAL. SUCCESSFUL ( Y/N )

SATIFIES PROTOCOL ?

CAL. BY :

DATE

TIME

PRE-CAL.

CALIBRATION


SATIFIES PROTOCOL ?

CAL. BY :

DATE

TIME

PRE-CAL.

CALIBRATION


SATIFIES PROTOCOL ?

CAL. BY :

DATE

TIME

PRE-CAL.

CALIBRATION


SATIFIES PROTOCOL ?

CAL. BY :

** DISSOLVED OXYGEN CALIBRATION IS PERFORMED BY THE PERCENT SATURATION AND BARAMETRIC PRESSURE METHOD.

DEL-TECH GEOTECHNICAL SUPPORT SERVICES(209) 847-8757 (OFFICE) * (209) 847-7744 (FAX) * [email protected] (Email)

INSTRUMENT CALIBRATION LOG 2016

HILMAR CHEESE J & J REGINA SEVERDIA-METZGER

9001 N. LANDER DEL TECH / DEL

HILMAR CHEESE

HOWARD REAL GROUNDWATER

JACOBSON JAMES & ASSOCIATES OCTOBER

CALIBRATION RECORDINGSCALIBRATION STANDARDS *

INSTRUMENT METER

CALIBRATION

INSTRUMENT TO THE CALIBRATION STANDARD SOLUTION THAT IS BEING USED AT THAT TIME AND AT THE

CURRENT AMBIENT TEMPERATURE.

2228752

* NOTE: UPON COMPLETING THE INITIAL READINGS OF THE INSTRUMENT , WE WILL ALWAYS ADJUST TO THE

ATTACHMENT 2

HYDROGRAPHS

ATTACHMENT 2

GROUNDWATER ELEVATION DATA UPPER AQUIFER SHALLOW ZONE



Hilmar, California

Notes: Dry monitoring wells plotted as total depth of well and shown with an open symbol.

70

75

80

85

90

95

100

Groundwater Elevation (feet ab

ove

mean

sea level)

MW‐01 MW‐03 MW‐04 MW‐05 MW‐06 MW‐07 MW‐08 MW‐09

MW‐11 MW‐12 MW‐13 MW‐15 MW‐16 MW‐17 MW‐21

ATTACHMENT 2

GROUNDWATER ELEVATION DATA UPPER AQUIFER SUPPLY ZONE



Hilmar, California

70

75

80

85

90

95

100


ove

mean

sea level)

MW‐18 MW‐19 MW‐22 MW‐25

ATTACHMENT 3

WELL CLUSTER WATER LEVEL DATA FOR VERTICAL DATA EVALUATIONS

ATTACHMENT 3

WELL CLUSTER WATER LEVEL DATA FOR VERTICAL DATA EVALUATIONS



Hilmar, California

20

30

40

50

60

70

80

90

100


ove

mean

sea level)

MW‐06 (Upper Aquifer Shallow Zone) MW‐22 (Upper Aquifer Supply Zone) MW‐23 (C‐Zone)

ATTACHMENT 4

LABORATORY ANALYTICAL RESULTS AND CHAIN‐OF‐CUSTODY DOCUMENTATION

(ELECTRONIC FORMAT)

12/19/16

Technical Report for

Jacobson James and Associates, Inc.

SL0604737007-Hilmar Cheese Co; 9001 N Lander Ave, Hilmar, CA

HCC-007-03/WA2016_006_HCC

SGS Accutest Job Number: FA37765

Sampling Date: 10/12/16

Report to:

Jacobson James & Associates, Inc9083 Foothills Blvd Suite 370Roseville, CA [email protected]; [email protected];[email protected]; [email protected]: Leon Gearhart

Total number of pages in report:

Certifications: FL(E83510), LA(03051), KS(E-10327), IL(200063), NC(573), NJ(FL002), NY(12022), SC(96038001)

DoD ELAP(L-A-B L2229), AZ(AZ0806), CA(2937), TX(T104704404), PA(68-03573), VA(460177),

AK, AR, GA, IA, KY, MA, NV, OK, OR, UT, WA

This report shall not be reproduced, except in its entirety, without the written approval of SGS Accutest.

Test results relate only to samples analyzed.

Southeast • 4405 Vineland Road • Suite C-15 • Orlando, FL 32811 • tel: 407-425-6700 • fax: 407-425-0707 • http://www.accutest.com

Test results contained within this data package meet the requirements

of the National Environmental Laboratory Accreditation Program

and/or state specific certification programs as applicable.

Client Service contact: Nutan Kabir 407-425-6700

Norm FarmerTechnical Director

Southeast 12/19/16Reissue #2

e-Hardcopy 2.0Automated Report

72

SGS Accutest is the sole authority for authorizing edits or modifications to this document.Unauthorized modification of this report is strictly prohibited.

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FA37765

Florida ♦ 4405 Vineland Road ♦ Suite C-15 ♦ Orlando, FL 32811 ♦ tel: 407 425-6700 ♦ fax: 407 425-0707 ♦ http://www.sgs.com

December 2, 2016 Mr. Bill Kay Jacobson & James Associates Inc, 9083 Foothills Blvd, Suite 370 Roseville, CA 95747 RE: SGS Accutest job FA37765 Reissue Dear Mr. Kay, The final report for job number FA37765 has been edited to reflect requested corrections. These edits have been incorporated into the revised report. Chloride and Sulfate results in the report deleted. SGS Accutest apologies for any inconvenience this may have caused. Please feel free to contact us if we can be of further assistance. Sincerely, SGS Accutest Orlando

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Florida 4405 Vineland Road Suite C-15 Orlando, FL 32811 tel: 407 425-6700 fax: 407 425-0707 htpp://www.sgs.com

December 7, 2016 Mr. Bill Kay Jacobson & James Associates Inc, 9083 Foothills Blvd Suite 370 Roseville, CA 95747 RE: SGS Accutest job FA37765 Reissue Dear Mr. Kay, The final report for job number FA37765 has been edited to reflect requested corrections. These edits have been incorporated into the revised report. Chloride and Sulfate results in the report deleted. Metals QC calculations error fixed. ALSE is a CA certified lab but pending certification for TDS. SGS Accutest apologies for any inconvenience this may have caused. Please feel free to contact us if we can be of further assistance. Sincerely, SGS Accutest - Orlando

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Table of Contents-1-

Sections:

Section 1: Sample Summary ................................................................................................... 5Section 2: Summary of Hits .................................................................................................... 7Section 3: Sample Results ........................................................................................................ 11

3.1: FA37765-1: W-MW-13-A ............................................................................................. 123.2: FA37765-2F: W-MW-13-AF ........................................................................................ 133.3: FA37765-3: W-MW-15-A ............................................................................................. 143.4: FA37765-4F: W-MW-15-AF ........................................................................................ 153.5: FA37765-5: W-MW-05-A ............................................................................................. 163.6: FA37765-6F: W-MW-05-AF ........................................................................................ 173.7: FA37765-7: FB-MW-05-A ........................................................................................... 183.8: FA37765-9: W-MW-25-A ............................................................................................. 193.9: FA37765-10F: W-MW-25-AF ...................................................................................... 203.10: FA37765-11: EB-101216-A ........................................................................................ 213.11: FA37765-12F: EB-101216-AF ................................................................................... 223.12: FA37765-13: W-MW-07-A ......................................................................................... 233.13: FA37765-14F: W-MW-07-AF .................................................................................... 243.14: FA37765-15: W-MW-07-B ......................................................................................... 253.15: FA37765-16F: W-MW-07-BF .................................................................................... 263.16: FA37765-17: W-MW-03-A ......................................................................................... 273.17: FA37765-18F: W-MW-03-AF .................................................................................... 283.18: FA37765-19: W-MW-01-A ......................................................................................... 293.19: FA37765-20F: W-MW-01-AF .................................................................................... 303.20: FA37765-21: EB-MW-25-A ....................................................................................... 313.21: FA37765-22F: EB-MW-25-AF ................................................................................... 32

Section 4: Subcontract Lab Data ............................................................................................ 33Section 5: Misc. Forms ............................................................................................................ 47

5.1: Chain of Custody ........................................................................................................... 48Section 6: Metals Analysis - QC Data Summaries ................................................................ 55

6.1: Prep QC MP30988: Ca,Fe,Mg,Mn,K,Na ...................................................................... 566.2: Prep QC MP31008: Ca,Fe,Mg,Mn,K,Na ...................................................................... 62

Section 7: General Chemistry - QC Data Summaries .......................................................... 687.1: Method Blank and Spike Results Summary .................................................................. 697.2: Duplicate Results Summary .......................................................................................... 707.3: Matrix Spike Results Summary ..................................................................................... 717.4: Matrix Spike Duplicate Results Summary .................................................................... 72

12

34

56

7

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Sample Summary

Jacobson James and Associates, Inc.Job No: FA37765

SL0604737007-Hilmar Cheese Co; 9001 N Lander Ave, Hilmar, CAProject No: HCC-007-03/WA2016_006_HCC

Sample Collected Matrix Client Number Date Time By Received Code Type Sample ID

FA37765-1 10/12/16 12:48 DL 10/14/16 AQ Ground Water W-MW-13-A

FA37765-2F 10/12/16 12:48 DL 10/14/16 AQ Groundwater Filtered W-MW-13-AF


FA37765-3D 10/12/16 13:24 DL 10/14/16 AQ Water Dup/MSD W-MW-15-A

FA37765-3S 10/12/16 13:24 DL 10/14/16 AQ Water Matrix Spike W-MW-15-A


FA37765-4FD10/12/16 13:24 DL 10/14/16 AQ Water Dup/MSD W-MW-15-AF

FA37765-4FS 10/12/16 13:24 DL 10/14/16 AQ Water Matrix Spike W-MW-15-AF





FA37765-11 10/12/16 10:40 DL 10/14/16 AQ Ground Water EB-101216-A

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Sample Summary(continued)

Jacobson James and Associates, Inc.Job No: FA37765

SL0604737007-Hilmar Cheese Co; 9001 N Lander Ave, Hilmar, CAProject No: HCC-007-03/WA2016_006_HCC

Sample Collected Matrix Client Number Date Time By Received Code Type Sample ID

FA37765-12F 10/12/16 10:40 DL 10/14/16 AQ Groundwater Filtered EB-101216-AF



FA37765-15 10/12/16 11:02 DL 10/14/16 AQ Ground Water W-MW-07-B

FA37765-16F 10/12/16 11:02 DL 10/14/16 AQ Groundwater Filtered W-MW-07-BF





FA37765-21 10/12/16 16:30 DL 10/14/16 AQ Equipment Blank EB-MW-25-A

FA37765-22F 10/12/16 16:30 DL 10/14/16 AQ Equip Blank Filtered EB-MW-25-AF

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Summary of Hits Page 1 of 4 Job Number: FA37765Account: Jacobson James and Associates, Inc.Project: SL0604737007-Hilmar Cheese Co; 9001 N Lander Ave, Hilmar, CACollected: 10/12/16

Lab Sample ID Client Sample ID Result/Analyte Qual RL MDL Units Method

FA37765-1 W-MW-13-A

Alkalinity, Bicarbonate as CaCO3 285 5.0 mg/l SM2320 B-11Alkalinity, Total as CaCO3 288 10 mg/l SM2320 B-11Solids, Total Dissolved 853 100 mg/l SM2540 C-11Specific Conductivity 1270 1.0 umhos/cm EPA 120.1

FA37765-2F W-MW-13-AF

Calcium 42200 1000 ug/l EPA 200.7Magnesium 15600 5000 ug/l EPA 200.7Potassium 154000 20000 ug/l EPA 200.7Sodium 134000 20000 ug/l EPA 200.7

FA37765-3 W-MW-15-A

Alkalinity, Bicarbonate as CaCO3 771 5.0 mg/l SM2320 B-11Alkalinity, Carbonate 19.5 5.0 mg/l SM2320 B-11Alkalinity, Total as CaCO3 791 25 mg/l SM2320 B-11Nitrogen, Total Kjeldahl 25.0 2.6 mg/l EPA 351.2Solids, Total Dissolved 2890 200 mg/l SM2540 C-11Specific Conductivity 2890 1.0 umhos/cm EPA 120.1

FA37765-4F W-MW-15-AF

Calcium 36300 1000 ug/l EPA 200.7Iron 1180 300 ug/l EPA 200.7Magnesium 10100 5000 ug/l EPA 200.7Manganese 64.3 15 ug/l EPA 200.7Potassium a 857000 100000 ug/l EPA 200.7Sodium 114000 20000 ug/l EPA 200.7

FA37765-5 W-MW-05-A


FA37765-6F W-MW-05-AF

Calcium 40900 1000 ug/l EPA 200.7Iron 3830 300 ug/l EPA 200.7Magnesium 16200 5000 ug/l EPA 200.7Manganese 2810 15 ug/l EPA 200.7

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2



Potassium 135000 20000 ug/l EPA 200.7Sodium 89500 20000 ug/l EPA 200.7

FA37765-7 FB-MW-05-A

Specific Conductivity 2.2 1.0 umhos/cm EPA 120.1

FA37765-9 W-MW-25-A


FA37765-10F W-MW-25-AF

Calcium 46900 1000 ug/l EPA 200.7Magnesium 17900 5000 ug/l EPA 200.7Manganese 86.1 15 ug/l EPA 200.7Sodium 57000 10000 ug/l EPA 200.7

FA37765-11 EB-101216-A


FA37765-12F EB-101216-AF

No hits reported in this sample.

FA37765-13 W-MW-07-A

Alkalinity, Bicarbonate as CaCO3 358 5.0 mg/l SM2320 B-11Alkalinity, Total as CaCO3 361 5.0 mg/l SM2320 B-11Nitrogen, Total Kjeldahl 4.7 0.53 mg/l EPA 351.2Solids, Total Dissolved 1050 100 mg/l SM2540 C-11Specific Conductivity 1650 1.0 umhos/cm EPA 120.1

FA37765-14F W-MW-07-AF

Calcium 75000 1000 ug/l EPA 200.7Iron 7120 300 ug/l EPA 200.7Magnesium 18000 5000 ug/l EPA 200.7Manganese 3660 15 ug/l EPA 200.7Potassium 37600 10000 ug/l EPA 200.7Sodium 278000 50000 ug/l EPA 200.7

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FA37765-15 W-MW-07-B

Alkalinity, Bicarbonate as CaCO3 364 5.0 mg/l SM2320 B-11Alkalinity, Total as CaCO3 366 10 mg/l SM2320 B-11Nitrogen, Total Kjeldahl 4.8 0.53 mg/l EPA 351.2Solids, Total Dissolved 1060 100 mg/l SM2540 C-11Specific Conductivity 1680 1.0 umhos/cm EPA 120.1

FA37765-16F W-MW-07-BF


FA37765-17 W-MW-03-A

Alkalinity, Bicarbonate as CaCO3 192 5.0 mg/l SM2320 B-11Alkalinity, Total as CaCO3 193 10 mg/l SM2320 B-11Nitrogen, Total Kjeldahl 2.7 0.53 mg/l EPA 351.2Solids, Total Dissolved 612 100 mg/l SM2540 C-11Specific Conductivity 1030 1.0 umhos/cm EPA 120.1

FA37765-18F W-MW-03-AF


FA37765-19 W-MW-01-A


FA37765-20F W-MW-01-AF

Calcium 37600 1000 ug/l EPA 200.7

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2



Magnesium 15600 5000 ug/l EPA 200.7Manganese 131 15 ug/l EPA 200.7Potassium 76900 10000 ug/l EPA 200.7Sodium 70300 10000 ug/l EPA 200.7

FA37765-21 EB-MW-25-A


FA37765-22F EB-MW-25-AF

No hits reported in this sample.

(a) Above high standard.

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SGS Accutest

Sample Results

Report of Analysis

SoutheastSection 3

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Report of Analysis Page 1 of 1

Client Sample ID: W-MW-13-A Lab Sample ID: FA37765-1 Date Sampled: 10/12/16 Matrix: AQ - Ground Water Date Received: 10/14/16

Percent Solids: n/a Project: SL0604737007-Hilmar Cheese Co; 9001 N Lander Ave, Hilmar, CA

General Chemistry

Analyte Result RL Units DF Analyzed By Method

Alkalinity, Bicarbonate as CaC 285 5.0 mg/l 1 10/21/16 19:30 ZC SM2320 B-11

Alkalinity, Carbonate <5.0 5.0 mg/l 1 10/21/16 17:30 ZC SM2320 B-11

Alkalinity, Total as CaCO3 288 10 mg/l 1 10/21/16 12:00 ZC SM2320 B-11

Nitrogen, Total Kjeldahl <0.53 0.53 mg/l 1 10/20/16 15:49 KH EPA 351.2

Solids, Total Dissolved 853 100 mg/l 1 10/17/16 19:45 LJ SM2540 C-11

Specific Conductivity 1270 1.0 umhos/cm 1 10/14/16 19:15 ZC EPA 120.1

RL = Reporting Limit

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33.1

SGS Accutest


Client Sample ID: W-MW-13-AF Lab Sample ID: FA37765-2F Date Sampled: 10/12/16 Matrix: AQ - Groundwater Filtered Date Received: 10/14/16


Dissolved Metals Analysis

Analyte Result RL Units DF Prep Analyzed By Method Prep Method

Calcium 42200 1000 ug/l 1 10/17/16 10/17/16 LM EPA 200.7 1 EPA 200.7 3

Iron <300 300 ug/l 1 10/17/16 10/17/16 LM EPA 200.7 1 EPA 200.7 3

Magnesium 15600 5000 ug/l 1 10/17/16 10/17/16 LM EPA 200.7 1 EPA 200.7 3

Manganese <15 15 ug/l 1 10/17/16 10/17/16 LM EPA 200.7 1 EPA 200.7 3

Potassium 154000 20000 ug/l 2 10/17/16 10/18/16 LM EPA 200.7 2 EPA 200.7 3

Sodium 134000 20000 ug/l 2 10/17/16 10/18/16 LM EPA 200.7 2 EPA 200.7 3

(1) Instrument QC Batch: MA13489(2) Instrument QC Batch: MA13491(3) Prep QC Batch: MP30988


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33.2

SGS Accutest




General Chemistry



Alkalinity, Carbonate 19.5 5.0 mg/l 1 10/21/16 17:30 ZC SM2320 B-11


Nitrogen, Total Kjeldahl 25.0 2.6 mg/l 5 10/20/16 16:08 KH EPA 351.2




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33.3

SGS Accutest







Iron 1180 300 ug/l 1 10/17/16 10/17/16 LM EPA 200.7 1 EPA 200.7 3


Manganese 64.3 15 ug/l 1 10/17/16 10/17/16 LM EPA 200.7 1 EPA 200.7 3

Potassium a 857000 100000 ug/l 10 10/17/16 10/18/16 LM EPA 200.7 2 EPA 200.7 3



(a) Above high standard.


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33.4

SGS Accutest




General Chemistry









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33.5

SGS Accutest









Manganese 2810 15 ug/l 1 10/19/16 10/20/16 LM EPA 200.7 1 EPA 200.7 2



(1) Instrument QC Batch: MA13502(2) Prep QC Batch: MP31008


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33.6

SGS Accutest


Client Sample ID: FB-MW-05-A Lab Sample ID: FA37765-7 Date Sampled: 10/12/16 Matrix: AQ - Ground Water Date Received: 10/14/16


General Chemistry


Solids, Total Dissolved <100 100 mg/l 1 10/17/16 18:35 LJ SM2540 C-11

Specific Conductivity 2.2 1.0 umhos/cm 1 10/14/16 19:15 ZC EPA 120.1


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33.7

SGS Accutest




General Chemistry









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33.8

SGS Accutest









Manganese 86.1 15 ug/l 1 10/17/16 10/17/16 LM EPA 200.7 1 EPA 200.7 2

Potassium <10000 10000 ug/l 1 10/17/16 10/17/16 LM EPA 200.7 1 EPA 200.7 2




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33.9

SGS Accutest


Client Sample ID: EB-101216-A Lab Sample ID: FA37765-11 Date Sampled: 10/12/16 Matrix: AQ - Ground Water Date Received: 10/14/16


General Chemistry


Alkalinity, Bicarbonate as CaC <5.0 5.0 mg/l 1 10/21/16 19:30 ZC SM2320 B-11


Alkalinity, Total as CaCO3 <10 10 mg/l 1 10/21/16 16:00 ZC SM2320 B-11





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33.10

SGS Accutest


Client Sample ID: EB-101216-AF Lab Sample ID: FA37765-12F Date Sampled: 10/12/16 Matrix: AQ - Groundwater Filtered Date Received: 10/14/16




Calcium <1000 1000 ug/l 1 10/17/16 10/17/16 LM EPA 200.7 1 EPA 200.7 2


Magnesium <5000 5000 ug/l 1 10/17/16 10/17/16 LM EPA 200.7 1 EPA 200.7 2



Sodium <10000 10000 ug/l 1 10/17/16 10/17/16 LM EPA 200.7 1 EPA 200.7 2



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33.11

SGS Accutest




General Chemistry




Alkalinity, Total as CaCO3 361 5.0 mg/l 1 10/21/16 12:00 ZC SM2320 B-11





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33.12

SGS Accutest














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33.13

SGS Accutest


Client Sample ID: W-MW-07-B Lab Sample ID: FA37765-15 Date Sampled: 10/12/16 Matrix: AQ - Ground Water Date Received: 10/14/16


General Chemistry









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33.14

SGS Accutest


Client Sample ID: W-MW-07-BF Lab Sample ID: FA37765-16F Date Sampled: 10/12/16 Matrix: AQ - Groundwater Filtered Date Received: 10/14/16












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33.15

SGS Accutest




General Chemistry









27 of 72

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33.16

SGS Accutest














28 of 72

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33.17

SGS Accutest




General Chemistry









29 of 72

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33.18

SGS Accutest














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33.19

SGS Accutest


Client Sample ID: EB-MW-25-A Lab Sample ID: FA37765-21 Date Sampled: 10/12/16 Matrix: AQ - Equipment Blank Date Received: 10/14/16


General Chemistry


Alkalinity, Bicarbonate as CaC <5.0 5.0 mg/l 1 10/21/16 19:30 ZC SM2320 B-11


Alkalinity, Total as CaCO3 <13 13 mg/l 1 10/21/16 16:00 ZC SM2320 B-11





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33.20

SGS Accutest


Client Sample ID: EB-MW-25-AF Lab Sample ID: FA37765-22F Date Sampled: 10/12/16 Matrix: AQ - Equip Blank Filtered Date Received: 10/14/16




Calcium <1000 1000 ug/l 1 10/17/16 10/17/16 LM EPA 200.7 1 EPA 200.7 2


Magnesium <5000 5000 ug/l 1 10/17/16 10/17/16 LM EPA 200.7 1 EPA 200.7 2



Sodium <10000 10000 ug/l 1 10/17/16 10/17/16 LM EPA 200.7 1 EPA 200.7 2



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33.21

SGS Accutest

Subcontract Lab Data

Report of Analysis

SoutheastSection 4

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4

WorkOrder:

Report Created for: SGS Accutest Orlando

4405 Vineland Rd. Suite C-15Orlando, FL 32811

Project Contact: Caitlin Brice

Project Name: FA37765XProject P.O.:

Project Received: 10/13/2016

Analytical Report reviewed & approved for release on 10/21/2016 by:

Angela Rydelius,Laboratory Manager

1610504

The report shall not be reproduced except in full, without the written

approval of the laboratory. The analytical results relate only to the

items tested. Results reported conform to the most current NELAP

standards, where applicable, unless otherwise stated in the case

narrative.

Amended: 12/06/2016

Analytical Report

1534 Willow Pass Rd. Pittsburg, CA 94565 ♦ TEL: (877) 252-9262 ♦ FAX: (925) 252-9269 ♦ www.mccampbell.comCA ELAP 1644 ♦ NELAP 4033ORELAP

McCampbell Analytical, Inc."When Quality Counts"

Page 1 of 13

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4

Glossary of Terms & Qualifier Definitions

Client: SGS Accutest OrlandoProject: FA37765XWorkOrder: 1610504

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

Glossary Abbreviation

%D Serial Dilution Percent Difference

95% Interval 95% Confident Interval

DF Dilution Factor

DI WET (DISTLC) Waste Extraction Test using DI water

DISS Dissolved (direct analysis of 0.45 µm filtered and acidified water sample)

DLT Dilution Test (Serial Dilution)

DUP Duplicate

EDL Estimated Detection Limit

ITEF International Toxicity Equivalence Factor

LCS Laboratory Control Sample

MB Method Blank

MB % Rec % Recovery of Surrogate in Method Blank, if applicable

MDL Method Detection Limit

ML Minimum Level of Quantitation

MS Matrix Spike

MSD Matrix Spike Duplicate

N/A Not Applicable

ND Not detected at or above the indicated MDL or RL

NR Data Not Reported due to matrix interference or insufficient sample amount.

PDS Post Digestion Spike

PDSD Post Digestion Spike Duplicate

PF Prep Factor

RD Relative Difference

RL Reporting Limit (The RL is the lowest calibration standard in a multipoint calibration.)

RPD Relative Percent Deviation

RRT Relative Retention Time

SPK Val Spike Value

SPKRef Val Spike Reference Value

SPLP Synthetic Precipitation Leachate Procedure

ST Sorbent Tube

TCLP Toxicity Characteristic Leachate Procedure

TEQ Toxicity Equivalents

WET (STLC) Waste Extraction Test (Soluble Threshold Limit Concentration)

Page 2 of 13

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4

Glossary of Terms & Qualifier Definitions

Client: SGS Accutest OrlandoProject: FA37765XWorkOrder: 1610504



Analytical Qualifiers

S Surrogate spike recovery outside accepted recovery limits

a14 reporting limit raised due to the physical nature of the sample

c1 surrogate recovery outside of the control limits due to the dilution of the sample.

Page 3 of 13

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4

Analytical Report



Client: SGS Accutest Orlando

Project: FA37765X

Date Received: 10/13/16 10:15Date Prepared: 10/13/16-10/18/16

WorkOrder: 1610504Extraction Method: E300.1Analytical Method: E300.1Unit: mg/L

Inorganic Anions by IC

W-MW-13-A 1610504-001A Water 10/12/2016 12:48 IC3 128090

Analytes Result DF Date AnalyzedRL

Client ID Lab ID Matrix Date Collected Instrument Batch ID

Chloride 120 10 100 10/17/2016 19:28Nitrate as N 43 1.0 10 10/14/2016 05:47Sulfate 37 10 100 10/17/2016 19:28

Surrogates REC (%) Limits

Analyst(s): AO

Formate 111 85-115 10/13/2016 16:47

W-MW-15-A 1610504-002A Water 10/12/2016 13:24 IC3 128090



Chloride 45 10 100 10/14/2016 06:24Nitrate as N 100 10 100 10/14/2016 06:24Sulfate 92 10 100 10/14/2016 06:24

Surrogates REC (%) LimitsQualifiers

Analytical Comments: a14,c1Analyst(s): AO, GM

Formate 0 85-115S 10/14/2016 06:24

W-MW-5-A 1610504-003A Water 10/12/2016 14:05 IC3 128090



Chloride 110 10 100 10/17/2016 20:05Nitrate as N 19 1.0 10 10/13/2016 18:01Sulfate 110 10 100 10/17/2016 20:05


Analytical Comments: a14Analyst(s): AO

Formate 107 85-115 10/13/2016 18:01

Angela Rydelius, Lab ManagerCDPH ELAP 1644 • NELAP 4033ORELAP(Cont.)

Page 4 of 13

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4

Analytical Report




Project: FA37765X




FB-MW-5-A 1610504-004A Water 10/12/2016 14:15 IC3 128090



Chloride ND 0.10 1 10/14/2016 07:01Nitrate as N ND 0.10 1 10/14/2016 07:01Sulfate ND 0.10 1 10/14/2016 07:01


Analyst(s): AO

Formate 109 85-115 10/14/2016 07:01

W-MW-25-A 1610504-005A Water 10/12/2016 16:10 IC3 128090



Chloride 50 1.0 10 10/13/2016 19:15Nitrate as N 13 1.0 10 10/13/2016 19:15Sulfate 41 1.0 10 10/13/2016 19:15


Analytical Comments: a14Analyst(s): AO

Formate 92 85-115 10/13/2016 19:15

EB-101216-A 1610504-006A Water 10/12/2016 10:40 IC3 128090





Analyst(s): AO

Formate 112 85-115 10/14/2016 07:38


Page 5 of 13

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4

Analytical Report




Project: FA37765X




W-MW-07-A 1610504-007A Water 10/12/2016 11:00 IC3 128090



Chloride 200 10 100 10/17/2016 20:42Nitrate as N 0.11 0.10 1 10/14/2016 08:16Sulfate 230 10 100 10/17/2016 20:42


Analyst(s): AO

Formate 107 85-115 10/14/2016 08:16

W-MW-07-B 1610504-008A Water 10/12/2016 11:02 IC3 128090



Chloride 200 10 100 10/17/2016 21:19Nitrate as N ND 0.10 1 10/14/2016 08:43Sulfate 230 10 100 10/17/2016 21:19


Analyst(s): AO

Formate 108 85-115 10/14/2016 08:43

W-MW-03-A 1610504-009A Water 10/12/2016 11:30 IC3 128090



Chloride 190 10 100 10/18/2016 01:39Nitrate as N ND 0.10 1 10/14/2016 09:20Sulfate 48 10 100 10/18/2016 01:39


Analyst(s): AO

Formate 107 85-115 10/14/2016 09:20


Page 6 of 13

39 of 72

FA37765

4

Analytical Report




Project: FA37765X




W-MW-01-A 1610504-010A Water 10/12/2016 12:05 IC3 128090



Chloride 34 1.0 10 10/13/2016 23:36Nitrate as N 29 1.0 10 10/13/2016 23:36Sulfate 28 1.0 10 10/13/2016 23:36


Analytical Comments: a14,c1Analyst(s): AO

Formate 93 85-115 10/13/2016 23:36

EB-MW-25-A 1610504-011A Water 10/12/2016 16:30 IC3 128090





Analyst(s): AO

Formate 109 85-115 10/14/2016 09:57

Angela Rydelius, Lab ManagerCDPH ELAP 1644 • NELAP 4033ORELAP

Page 7 of 13

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4

Quality Control Report




Project: FA37765X

Date Analyzed: 10/13/16 - 10/17/16Date Prepared: 10/13/16 - 10/17/16

WorkOrder: 1610504BatchID: 128090

Analytical Method: E300.1Unit: mg/LSample ID: MB/LCS-128090

1610504-002AMS/MSD

Instrument: IC3Matrix: Water

Extraction Method: E300.1

QC Summary Report for E300.1

Analyte MB Result

LCS Result

RL SPK Val

MB SS %REC

LCS %REC

LCS Limits

Chloride ND 0.954 0.10 1 - 95 85-115Nitrate as N ND 0.960 0.10 1 - 96 85-115Nitrate as NO3¯ ND 4.25 0.45 4.4 - 97 85-115Nitrite as N ND 1.00 0.10 1 - 100 85-115Nitrite as NO2¯ ND 3.30 0.33 3.3 - 100 85-115Sulfate ND 0.972 0.10 1 - 97 85-115

Surrogate Recovery

Formate 0.109 0.106 0.10 109 106 85-115

Analyte MS Result

MSD Result

SPK Val

SPKRef Val

MS %REC

MSD %REC

MS/MSD Limits

RPD RPDLimit

Chloride 141 140 100 44.88 96 95 85-115 0.585 15Nitrate as N 208 207 100 100.7 108 107 85-115 0.552 15Nitrate as NO3¯ 924 918 440 446.1 109 107 85-115 0.552 15Nitrite as N 101 101 100 ND<10 101 101 85-115 0 15Nitrite as NO2¯ 333 331 330 ND<33 101 100 85-115 0.544 15Sulfate 198 198 100 91.70 106 107 85-115 0.0117 15

Surrogate Recovery

Formate 10.8 10.8 10 108 108 85-115 0 10

QA/QC OfficerCDPH ELAP 1644 • NELAP 4033ORELAPPage 8 of 13

41 of 72

FA37765

4

McCampbell Analytical, Inc.1534 Willow Pass RdPittsburg, CA 94565-1701(925) 252-9262

CHAIN-OF-CUSTODY RECORD Page

Lab ID Matrix Collection Date Hold

Requested Tests (See legend below)

Report to:

Caitlin Brice

4405 Vineland Rd. Suite C-15Orlando, FL 32811(407) 425-6700 FAX:

PO:

10/13/2016

Client ID

ProjectNo: FA37765X

WorkOrder: 1610504

1 of 1

Date Logged:

Date Received: 10/13/2016

1 2 3 4 5 6 7 8 9 10 11 12

SGS Accutest Orlando

Bill to:

Jean Dent-SmithSGS Accutest Orlando4405 Vineland Rd. Suite C-15Orlando, FL 32811

Requested TAT: 5 days;

ClientCode: SGSAF

Email: [email protected]

EDF EQuIS Email HardCopy ThirdPartyExcel J-flagWriteOn

cc/3rd Party:

WaterTrax

A1610504-001 Water 10/12/2016 12:48W-MW-13-AA1610504-002 Water 10/12/2016 13:24W-MW-15-A AA1610504-003 Water 10/12/2016 14:05W-MW-5-AA1610504-004 Water 10/12/2016 14:15FB-MW-5-AA1610504-005 Water 10/12/2016 16:10W-MW-25-AA1610504-006 Water 10/12/2016 10:40EB-101216-AA1610504-007 Water 10/12/2016 11:00W-MW-07-AA1610504-008 Water 10/12/2016 11:02W-MW-07-BA1610504-009 Water 10/12/2016 11:30W-MW-03-AA1610504-010 Water 10/12/2016 12:05W-MW-01-AA1610504-011 Water 10/12/2016 16:30EB-MW-25-A

Prepared by: Maria Venegas

NOTE: Soil samples are discarded 60 days after results are reported unless other arrangements are made (Water samples are 30 days). Hazardous samples will be returned to client or disposed of at client expense.

Comments:

300_1_W PRQC300_11 2 3 4

5 6 7 8

9 10

Test Legend:

11 12

Page 9 of 1342 of 72

FA37765

4

Lab ID Client ID Collection Date

& Time

Date Logged:

TATMatrix Test Name Containers

/Composites

WORK ORDER SUMMARY

Work Order: 1610504

Comments:

Client Name: SGS ACCUTEST ORLANDO Project: FA37765XQC Level: LEVEL 2

HoldDe-

chlorinated

SubOutBottle & Preservative

10/13/2016

Sediment

Content

EDF Fax Email HardCopy ThirdPartyExcel J-flagWriteOn

Caitlin BriceClient Contact:

[email protected]'s Email:

WaterTrax



1610504-001A W-MW-13-A 10/12/2016 12:48 5 daysWater E300.1 (Inorganic Anions) <Chloride, Nitrate & Nitrite as N, Nitrate as N, Nitrate as NO3¯, Nitrite as N, Nitrite as NO2¯, Sulfate>

1 250mL HDPE, unprsv. None


1 250mL HDPE, unprsv. Present




1610504-004A FB-MW-5-A 10/12/2016 14:15 5 daysWater E300.1 (Inorganic Anions) <Chloride, Nitrate & Nitrite as N, Nitrate as N, Nitrate as NO3¯, Nitrite as N, Nitrite as NO2¯, Sulfate>




1610504-006A EB-101216-A 10/12/2016 10:40 5 daysWater E300.1 (Inorganic Anions) <Chloride, Nitrate & Nitrite as N, Nitrate as N, Nitrate as NO3¯, Nitrite as N, Nitrite as NO2¯, Sulfate>


1 of 2Page

- STLC and TCLP extractions require 2 days to complete; therefore, all TATs begin after the extraction is completed (i.e., One-day TAT yields results in 3 days from sample submission).

NOTES:

- MAI assumes that all material present in the provided sampling container is considered part of the sample - MAI does not exclude any material from the sample prior to sample preparation unless requested in writing by the client.

Page 10 of 1343 of 72

FA37765

4

Lab ID Client ID Collection Date

& Time

Date Logged:

TATMatrix Test Name Containers

/Composites

WORK ORDER SUMMARY

Work Order: 1610504

Comments:

Client Name: SGS ACCUTEST ORLANDO Project: FA37765XQC Level: LEVEL 2

HoldDe-

chlorinated

SubOutBottle & Preservative

10/13/2016

Sediment

Content

EDF Fax Email HardCopy ThirdPartyExcel J-flagWriteOn

Caitlin BriceClient Contact:

[email protected]'s Email:

WaterTrax





1610504-008A W-MW-07-B 10/12/2016 11:02 5 daysWater E300.1 (Inorganic Anions) <Chloride, Nitrate & Nitrite as N, Nitrate as N, Nitrate as NO3¯, Nitrite as N, Nitrite as NO2¯, Sulfate>



1 250mL HDPE, unprsv. Trace



1610504-011A EB-MW-25-A 10/12/2016 16:30 5 daysWater E300.1 (Inorganic Anions) <Chloride, Nitrate & Nitrite as N, Nitrate as N, Nitrate as NO3¯, Nitrite as N, Nitrite as NO2¯, Sulfate>


2 of 2Page

- STLC and TCLP extractions require 2 days to complete; therefore, all TATs begin after the extraction is completed (i.e., One-day TAT yields results in 3 days from sample submission).

NOTES:

- MAI assumes that all material present in the provided sampling container is considered part of the sample - MAI does not exclude any material from the sample prior to sample preparation unless requested in writing by the client.

Page 11 of 1344 of 72

FA37765

4

Page 12 of 1345 of 72

FA37765

4

Sample Receipt Checklist



Client Name: SGS Accutest Orlando

WorkOrder №: 1610504

Date Logged: 10/13/2016

Logged by: Maria VenegasMatrix: WaterCarrier: Client Drop-In

Shipping container/cooler in good condition? Yes No

Custody seals intact on shipping container/cooler? Yes No NA

Samples Received on Ice? Yes No

Chain of custody present? Yes No

Chain of custody signed when relinquished and received? Yes No

Chain of custody agrees with sample labels? Yes No

Samples in proper containers/bottles? Yes No

Sample containers intact? Yes No

Sufficient sample volume for indicated test? Yes No

All samples received within holding time? Yes No

NASample/Temp Blank temperature

Yes No NAWater - VOA vials have zero headspace / no bubbles?

pH acceptable upon receipt (Metal: <2; 522: <4; 218.7: >8)? Yes No NA

Temp: 5°C

Chain of Custody (COC) Information

Yes NoSample IDs noted by Client on COC?

Yes NoDate and Time of collection noted by Client on COC?

Yes NoSampler's name noted on COC?

Sample Receipt Information

Sample Preservation and Hold Time (HT) Information

Sample labels checked for correct preservation? Yes No

Project Name: FA37765X

(Ice Type: WET ICE )

Comments: Method E300.1 (Inorganic Anions) was received passed its 2-day holding time.

Total Chlorine tested and acceptable upon receipt for EPA 522? Yes No NAUCMR3 Samples:

Free Chlorine tested and acceptable upon receipt for EPA 218.7, 300.1, 537, 539?

Yes No NA

Date and Time Received 10/13/2016 10:15

Received by: Maria Venegas

Page 13 of 13

46 of 72

FA37765

4

SGS Accutest

Misc. Forms

Custody Documents and Other Forms

Includes the following where applicable:

• Chain of Custody

SoutheastSection 5

47 of 72

FA37765

5

FA37765: Chain of CustodyPage 1 of 7

48 of 72

FA37765

55.1


49 of 72

FA37765

55.1


50 of 72

FA37765

55.1


51 of 72

FA37765

55.1


52 of 72

FA37765

55.1


53 of 72

FA37765

55.1


54 of 72

FA37765

55.1

SGS Accutest

Metals Analysis

QC Data Summaries


• Method Blank Summaries• Matrix Spike and Duplicate Summaries• Blank Spike and Lab Control Sample Summaries• Serial Dilution Summaries

SoutheastSection 6

55 of 72

FA37765

6

BLANK RESULTS SUMMARY Part 2 - Method Blanks

Login Number: FA37765 Account: JJAAICAR - Jacobson James and Associates, Inc.

Project: SL0604737007-Hilmar Cheese Co; 9001 N Lander Ave, Hilmar, CA

QC Batch ID: MP30988 Methods: EPA 200.7 Matrix Type: AQUEOUS Units: ug/l

Prep Date: 10/17/16

MB Metal RL IDL MDL raw final

Aluminum 200 14 14

Antimony 6.0 1 1

Arsenic 10 1.3 1.3

Barium 200 1 1

Beryllium 4.0 .2 .2

Cadmium 5.0 .2 .2

Calcium 1000 50 50 9.1 <1000

Chromium 10 1 1

Cobalt 50 .2 .2

Copper 25 1 1

Iron 300 17 17 0.80 <300

Lead 5.0 1 1.1

Magnesium 5000 35 35 19.2 <5000

Manganese 15 .5 1 0.10 <15

Molybdenum 50 .3 .3

Nickel 40 .4 .4

Potassium 10000 200 200 -2.9 <10000

Selenium 10 2.4 2.9

Silver 10 .7 .7

Sodium 10000 500 500 -150 <10000

Strontium 10 .5 .5

Thallium 10 1.1 1.4

Tin 50 .9 1

Titanium 10 .5 1

Vanadium 50 .5 .6

Zinc 20 3 4.4

Associated samples MP30988: FA37765-2F, FA37765-4F, FA37765-10F, FA37765-12F, FA37765-14F, FA37765-16F,FA37765-18F, FA37765-20F, FA37765-22F

Results < IDL are shown as zero for calculation purposes(*) Outside of QC limits(anr) Analyte not requested

_________________________________________________________________________________________________________

Page 1

56 of 72

FA37765

66.1.1

MATRIX SPIKE AND DUPLICATE RESULTS SUMMARY




Prep Date: 10/17/16 10/17/16

FA37765-4F QC FA37765-4F Spikelot QC Metal Original DUP RPD Limits Original MS MPFLICP2 % Rec Limits

Aluminum

Antimony

Arsenic

Barium

Beryllium

Cadmium

Calcium 36300 37600 3.5 0-20 36300 62800 25000 106.0 70-130

Chromium

Cobalt

Copper

Iron 1180 1210 2.5 0-20 1180 28000 26000 103.2 70-130

Lead

Magnesium 9760 10400 2.9 0-20 9760 36900 25000 107.2 70-130

Manganese 62.8 66.2 2.9 0-20 62.8 572 500 101.5 70-130

Molybdenum

Nickel

Potassium 857000 1070000a 22.1*(b) 0-20 857000 1030000a 25000 692.0(c) 70-130

Selenium

Silver

Sodium 114000 122000 6.8 0-20 114000 140000 25000 104.0 70-130

Strontium

Thallium

Tin

Titanium

Vanadium

Zinc


Results < IDL are shown as zero for calculation purposes(*) Outside of QC limits(N) Matrix Spike Rec. outside of QC limits(anr) Analyte not requested(a) Above high standard.(b) High RPD indicates possible matrix interference.(c) Spike amount low relative to the sample amount. Refer to lab control or spike blank for recovery

information.

_________________________________________________________________________________________________________

Page 1

57 of 72

FA37765

66.1.2





Prep Date: 10/17/16

FA37765-4F Spikelot MSD QC Metal Original MSD MPFLICP2 % Rec RPD Limit

Aluminum

Antimony

Arsenic

Barium

Beryllium

Cadmium

Calcium 36300 63100 25000 107.2 0.5 20

Chromium

Cobalt

Copper

Iron 1180 27800 26000 102.4 0.7 20

Lead

Magnesium 9760 36800 25000 106.8 0.3 20

Manganese 62.8 570 500 101.1 0.4 20

Molybdenum

Nickel

Potassium 857000 1050000a 25000 772.0(b) 1.9 20

Selenium

Silver

Sodium 114000 146000 25000 128.0 4.2 20

Strontium

Thallium

Tin

Titanium

Vanadium

Zinc


Results < IDL are shown as zero for calculation purposes(*) Outside of QC limits(N) Matrix Spike Rec. outside of QC limits(anr) Analyte not requested(a) Above high standard.(b) Spike amount low relative to the sample amount. Refer to lab control or spike blank for recovery

information.

_________________________________________________________________________________________________________

Page 2

58 of 72

FA37765

66.1.2

SPIKE BLANK AND LAB CONTROL SAMPLE SUMMARY




Prep Date: 10/17/16

BSP Spikelot QC Metal Result MPFLICP2 % Rec Limits

Aluminum

Antimony

Arsenic

Barium

Beryllium

Cadmium

Calcium 28000 25000 112.0 85-115

Chromium

Cobalt

Copper

Iron 27800 26000 106.9 85-115

Lead

Magnesium 28400 25000 113.6 85-115

Manganese 524 500 104.8 85-115

Molybdenum

Nickel

Potassium 26000 25000 104.0 85-115

Selenium

Silver

Sodium 28900 25000 115.6 85-115

Strontium

Thallium

Tin

Titanium

Vanadium

Zinc



_________________________________________________________________________________________________________

Page 1

59 of 72

FA37765

66.1.3

SERIAL DILUTION RESULTS SUMMARY




Prep Date: 10/17/16

FA37765-4F QC Metal Original SDL 1:5 %DIF Limits

Aluminum

Antimony

Arsenic

Barium

Beryllium

Cadmium

Calcium 36300 35500 2.3 0-10

Chromium

Cobalt

Copper

Iron 1180 1140 3.4 0-10

Lead

Magnesium 9760 9920 1.4 0-10

Manganese 62.8 61.9 3.7 0-10

Molybdenum

Nickel

Potassium 857000 964000 12.5*(a) 0-10

Selenium

Silver

Sodium 114000 125000 9.7 0-10

Strontium

Thallium

Tin

Titanium

Vanadium

Zinc


Results < IDL are shown as zero for calculation purposes(*) Outside of QC limits(anr) Analyte not requested(a) Serial dilution indicates possible matrix interference.

_________________________________________________________________________________________________________

Page 1

60 of 72

FA37765

66.1.4

POST DIGESTATE SPIKE SUMMARY




Prep Date: 10/17/16

Sample Final FA37765-4F PS Spike Spike Spike QC Metal ml ml Raw Corr.** ug/l ml ug/ml ug/l % Rec Limits

Aluminum

Antimony

Arsenic

Barium

Beryllium

Cadmium

Calcium 9.8 10 36310 35583.8 41330 0.2 250 5000 114.9 85-115

Chromium

Cobalt

Copper

Iron 9.8 10 1175 1151.5 4538 0.2 150 3000 112.9 85-115

Lead

Magnesium 9.8 10 9764 9858.8 15750 0.2 250 5000 117.8*(a 85-115

Manganese 9.8 10 62.8 63.014 120 0.2 2.5 50 114.0 85-115

Molybdenum

Nickel

Potassium 9.8 10 857000 839860 1031000 0.2 500 10000 1911.4*a 85-115

Selenium

Silver

Sodium 9.8 10 114000 111720 127900 0.2 500 10000 161.8*(a 85-115

Strontium

Thallium

Tin

Titanium

Vanadium

Zinc


Results < IDL are shown as zero for calculation purposes(*) Outside of QC limits(**) Corr. sample result = Raw * (sample volume / final volume)(anr) Analyte not requested(a) Spike recovery indicates matrix interference and/or outside control limits due to high level in

sample relative to spike amount.

_________________________________________________________________________________________________________

Page 1

61 of 72

FA37765

66.1.5

BLANK RESULTS SUMMARY Part 2 - Method Blanks




Prep Date: 10/19/16

MB Metal RL IDL MDL raw final

Aluminum 200 14 14

Antimony 6.0 1 1

Arsenic 10 1.3 1.3

Barium 200 1 1

Beryllium 4.0 .2 .2

Cadmium 5.0 .2 .2

Calcium 1000 50 50 12.7 <1000

Chromium 10 1 1

Cobalt 50 .2 .2

Copper 25 1 1

Iron 300 17 17 6.3 <300

Lead 5.0 1 1.1

Magnesium 5000 35 35 -12 <5000

Manganese 15 .5 1 0.10 <15

Molybdenum 50 .3 .3

Nickel 40 .4 .4

Potassium 10000 200 200 27.1 <10000

Selenium 10 2.4 2.9

Silver 10 .7 .7

Sodium 10000 500 500 41.9 <10000

Strontium 10 .5 .5

Thallium 10 1.1 1.4

Tin 50 .9 1

Titanium 10 .5 1

Vanadium 50 .5 .6

Zinc 20 3 4.4

Associated samples MP31008: FA37765-6F


_________________________________________________________________________________________________________

Page 1

62 of 72

FA37765

66.2.1





Prep Date: 10/19/16 10/19/16

FA37843-1 QC FA37843-1 Spikelot QC Metal Original DUP RPD Limits Original MS MPFLICP2 % Rec Limits

Aluminum

Antimony

Arsenic

Barium

Beryllium

Cadmium

Calcium 250000 256000 2.4 0-20 250000 273000 25000 92.0 70-130

Chromium

Cobalt

Copper

Iron 2680 2710 1.1 0-20 2680 28900 26000 100.8 70-130

Lead

Magnesium 60400 61100 1.2 0-20 60400 84100 25000 94.8 70-130

Manganese 3510 3590 2.3 0-20 3510 3940 500 86.0 70-130

Molybdenum

Nickel

Potassium 5680 5790 1.9 0-20 5680 31400 25000 102.9 70-130

Selenium

Silver

Sodium 240000 245000 2.1 0-20 240000 258000 25000 72.0 70-130

Strontium

Thallium

Tin

Titanium

Vanadium

Zinc


Results < IDL are shown as zero for calculation purposes(*) Outside of QC limits(N) Matrix Spike Rec. outside of QC limits(anr) Analyte not requested

_________________________________________________________________________________________________________

Page 1

63 of 72

FA37765

66.2.2





Prep Date: 10/19/16

FA37843-1 Spikelot MSD QC Metal Original MSD MPFLICP2 % Rec RPD Limit

Aluminum

Antimony

Arsenic

Barium

Beryllium

Cadmium

Calcium 250000 278000 25000 112.0 1.8 20

Chromium

Cobalt

Copper

Iron 2680 29200 26000 102.0 1.0 20

Lead

Magnesium 60400 84800 25000 97.6 0.8 20

Manganese 3510 4020 500 102.0 2.0 20

Molybdenum

Nickel

Potassium 5680 31400 25000 102.9 0.0 20

Selenium

Silver

Sodium 240000 265000 25000 100.0 2.7 20

Strontium

Thallium

Tin

Titanium

Vanadium

Zinc


Results < IDL are shown as zero for calculation purposes(*) Outside of QC limits(N) Matrix Spike Rec. outside of QC limits(anr) Analyte not requested

_________________________________________________________________________________________________________

Page 2

64 of 72

FA37765

66.2.2

SPIKE BLANK AND LAB CONTROL SAMPLE SUMMARY




Prep Date: 10/19/16

BSP Spikelot QC Metal Result MPFLICP2 % Rec Limits

Aluminum

Antimony

Arsenic

Barium

Beryllium

Cadmium

Calcium 25800 25000 103.2 85-115

Chromium

Cobalt

Copper

Iron 27100 26000 104.2 85-115

Lead

Magnesium 25200 25000 100.8 85-115

Manganese 505 500 101.0 85-115

Molybdenum

Nickel

Potassium 25700 25000 102.8 85-115

Selenium

Silver

Sodium 25300 25000 101.2 85-115

Strontium

Thallium

Tin

Titanium

Vanadium

Zinc



_________________________________________________________________________________________________________

Page 1

65 of 72

FA37765

66.2.3

SERIAL DILUTION RESULTS SUMMARY




Prep Date: 10/19/16

FA37843-1 QC Metal Original SDL 1:5 %DIF Limits

Aluminum

Antimony

Arsenic

Barium

Beryllium

Cadmium

Calcium 250000 258000 3.2 0-10

Chromium

Cobalt

Copper

Iron 2680 2720 1.5 0-10

Lead

Magnesium 60400 61800 2.4 0-10

Manganese 3510 3630 3.2 0-10

Molybdenum

Nickel

Potassium 5680 5770 1.7 0-10

Selenium

Silver

Sodium 240000 254000 5.6 0-10

Strontium

Thallium

Tin

Titanium

Vanadium

Zinc



_________________________________________________________________________________________________________

Page 1

66 of 72

FA37765

66.2.4

POST DIGESTATE SPIKE SUMMARY




Prep Date: 10/19/16

Sample Final FA37843-1 PS Spike Spike Spike QC Metal ml ml Raw Corr.** ug/l ml ug/ml ug/l % Rec Limits

Aluminum

Antimony

Arsenic

Barium

Beryllium

Cadmium

Calcium 9.8 10 249700 244706 251800 0.2 250 5000 141.9*(a 85-115

Chromium

Cobalt

Copper

Iron 9.8 10 2680 2626.4 5855 0.2 150 3000 107.6 85-115

Lead

Magnesium 9.8 10 60370 59162.6 64210 0.2 250 5000 100.9 85-115

Manganese 9.8 10 3514 3443.72 3484 0.2 2.5 50 80.6*(a) 85-115

Molybdenum

Nickel

Potassium 9.8 10 5677 5563.46 16170 0.2 500 10000 106.1 85-115

Selenium

Silver

Sodium 9.8 10 240200 235396 243000 0.2 500 10000 76.0*(a) 85-115

Strontium

Thallium

Tin

Titanium

Vanadium

Zinc


Results < IDL are shown as zero for calculation purposes(*) Outside of QC limits(**) Corr. sample result = Raw * (sample volume / final volume)(anr) Analyte not requested(a) Spike recovery indicates matrix interference and/or outside control limits due to high level in

sample relative to spike amount.

_________________________________________________________________________________________________________

Page 1

67 of 72

FA37765

66.2.5

SGS Accutest

General Chemistry

QC Data Summaries


• Method Blank and Blank Spike Summaries• Duplicate Summaries• Matrix Spike Summaries

SoutheastSection 7

68 of 72

FA37765

7

METHOD BLANK AND SPIKE RESULTS SUMMARY GENERAL CHEMISTRY



MB Spike BSP BSP QC Analyte Batch ID RL Result Units Amount Result %Recov Limits

Alkalinity, Total as CaCO3 GN72790 5.0 0.0 mg/l 250 254 101.4 90-113% Alkalinity, Total as CaCO3 GN72792 5.0 0.0 mg/l 10 10.1 101.0 90-113% Alkalinity, Total as CaCO3 GN72793 25 0.0 mg/l 250 256 102.0 90-113% Nitrogen, Total Kjeldahl GP28674/GN72779 0.53 0.0 mg/l 2.63 2.64 100.6 90-110% Solids, Total Dissolved GN72702 100 14.0 mg/l Solids, Total Dissolved GN72727 100 0.0 mg/l Specific Conductivity GN72698 1.0 0.0 umhos/cm

Associated Samples: Batch GN72698: FA37765-1, FA37765-3, FA37765-5, FA37765-7, FA37765-9, FA37765-11, FA37765-13, FA37765-15, FA37765-17,FA37765-19, FA37765-21Batch GN72702: FA37765-1Batch GN72727: FA37765-3, FA37765-5, FA37765-7, FA37765-9, FA37765-11, FA37765-13, FA37765-15, FA37765-17, FA37765-19,FA37765-21Batch GN72790: FA37765-1, FA37765-5, FA37765-9, FA37765-13, FA37765-15, FA37765-17, FA37765-19Batch GN72792: FA37765-11, FA37765-21Batch GN72793: FA37765-3Batch GP28674: FA37765-1, FA37765-3, FA37765-5, FA37765-9, FA37765-11, FA37765-13, FA37765-15, FA37765-17, FA37765-19,FA37765-21(*) Outside of QC limits

__________________________________________________________________________________________________________________________

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FA37765

77.1

DUPLICATE RESULTS SUMMARY GENERAL CHEMISTRY



QC Original DUP QC Analyte Batch ID Sample Units Result Result RPD Limits

Alkalinity, Total as CaCO3 GN72790 FA37838-1 mg/l 161 161 0.6 0-20% Alkalinity, Total as CaCO3 GN72793 FA37765-3 mg/l 791 789 0.2 0-20% Solids, Total Dissolved GN72702 FA37623-4 mg/l 1140 1140 0.0 0-5% Solids, Total Dissolved GN72727 FA37765-3 mg/l 2890 2880 0.3 0-5% Specific Conductivity GN72698 FA37765-19 umhos/cm 738 769 4.1 0-10% Specific Conductivity GN72698 FA37765-21 umhos/cm 1.5 1.4 6.2 0-10%

Associated Samples: Batch GN72698: FA37765-1, FA37765-3, FA37765-5, FA37765-7, FA37765-9, FA37765-11, FA37765-13, FA37765-15, FA37765-17,FA37765-19, FA37765-21Batch GN72702: FA37765-1Batch GN72727: FA37765-3, FA37765-5, FA37765-7, FA37765-9, FA37765-11, FA37765-13, FA37765-15, FA37765-17, FA37765-19,FA37765-21Batch GN72790: FA37765-1, FA37765-5, FA37765-9, FA37765-13, FA37765-15, FA37765-17, FA37765-19Batch GN72793: FA37765-3(*) Outside of QC limits

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FA37765

77.2

MATRIX SPIKE RESULTS SUMMARY GENERAL CHEMISTRY



QC Original Spike MS QC Analyte Batch ID Sample Units Result Amount Result %Rec Limits

Nitrogen, Total Kjeldahl GP28674/GN72779 FA37765-19 mg/l 0.0 2.63 0.0 0.0N(a) 90-110% Nitrogen, Total Kjeldahl GP28674/GN72779 FA37765-3 mg/l 25.0 2.63 31.3 240.0(b) 90-110%

Associated Samples: Batch GP28674: FA37765-1, FA37765-3, FA37765-5, FA37765-9, FA37765-11, FA37765-13, FA37765-15, FA37765-17, FA37765-19,FA37765-21(*) Outside of QC limits(N) Matrix Spike Rec. outside of QC limits(a) Spike recovery indicates possible matrix interference.(b) Spike amount low relative to the sample amount. Refer to lab control or spike blank for recovery information.

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FA37765

77.3

MATRIX SPIKE DUPLICATE RESULTS SUMMARY GENERAL CHEMISTRY



QC Original Spike MSD QC Analyte Batch ID Sample Units Result Amount Result RPD Limit

Nitrogen, Total Kjeldahl GP28674/GN72779 FA37765-19 mg/l 0.0 2.63 0.0 0.0 20% Nitrogen, Total Kjeldahl GP28674/GN72779 FA37765-3 mg/l 25.0 2.63 29.1 7.3 20%

Associated Samples: Batch GP28674: FA37765-1, FA37765-3, FA37765-5, FA37765-9, FA37765-11, FA37765-13, FA37765-15, FA37765-17, FA37765-19,FA37765-21(*) Outside of QC limits(N) Matrix Spike Rec. outside of QC limits

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FA37765

77.4

ATTACHMENT 5

HISTORICAL ANALYTICAL RESULTS FOR GROUNDWATER

(ELECTRONIC FORMAT)

ATTACHMENT 5




Hilmar, California

Sample

Location Sample Date Alkalinity, Bicarbonate

as CaC

O3 (mg/L)

Alkalinity, Carbonate

as CaC

O3 (mg/L)

Alkalinity, Hydroxide

as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)

Nitrogen, Total Kjeldah

l

(mg/L)

Solids, total dissolved

(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐01 07/27/1989 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 23.2 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.2 ‐‐ ‐‐ 150 ‐‐

MW‐01 10/16/1989 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.2 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.2 ‐‐ ‐‐ 700 ‐‐

MW‐01 01/15/1990 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 430 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 14 ‐‐ ‐‐ 232 ‐‐

MW‐01 04/10/1990 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.5 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 25 ‐‐ ‐‐ 345 ‐‐

MW‐01 10/29/1990 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 83.2 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 21 ‐‐ ‐‐ 440 ‐‐

MW‐01 01/08/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 48.9 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.23 ‐‐ ‐‐ 460 ‐‐

MW‐01 04/18/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 410 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 ‐‐ ‐‐ 1600 ‐‐

MW‐01 07/26/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 362 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5 ‐‐ ‐‐ 2020 ‐‐

MW‐01 10/23/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.6 ‐‐ ‐‐ 260 ‐‐

MW‐01 01/24/1992 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 249 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 ‐‐ ‐‐ 1610 ‐‐

MW‐01 04/02/1992 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ ‐‐ 2690 ‐‐

MW‐01 06/19/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 35 2200 2800 ‐‐

MW‐01 07/11/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 27 1300 2300 18

MW‐01 08/15/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 22 1100 1900 ‐‐

MW‐01 11/14/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 24 1100 1600 ‐‐

MW‐01 02/14/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 310 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 32 1400 2400 ‐‐

MW‐01 05/21/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 40 1300 2500 ‐‐

MW‐01 08/20/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 320 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 74 1600 3000 ‐‐

MW‐01 11/19/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 24 1100 1900 ‐‐

MW‐01 02/18/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 53 1500 2600 ‐‐

MW‐01 05/20/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 66 1300 2600 ‐‐

MW‐01 08/25/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 39 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 11 490 900 ‐‐

MW‐01 11/20/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 21 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8.2 360 540 ‐‐

MW‐01 02/26/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 100 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 24 780 1400 ‐‐

MW‐01 05/19/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 100 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 7.7 1100 1700 ‐‐

MW‐01 08/20/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 98 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9.7 1100 1400 ‐‐

MW‐01 11/24/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 10 1300 2200 ‐‐

MW‐01 02/15/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 110 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 4.1 850 1300 ‐‐

MW‐01 05/24/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 7.9 1400 2200 ‐‐

MW‐01 08/20/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8.6 1400 2100 ‐‐

MW‐01 02/11/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11 15 860 1400 ‐‐

MW‐01 05/02/2000 360 <1 <1 360 ‐‐ 110 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 10 960 1500 59

MW‐01 11/21/2000 880 <1 <1 880 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 43 1200 2300 ‐‐

MW‐01 12/14/2000 1200 <1 <1 1200 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 36 1800 2900 ‐‐

MW‐01 01/07/2001 1100 <1 <1 1100 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 29 1600 2500 ‐‐

Page 1 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐01 02/02/2001 1100 <1 <1 1100 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ 1700 2600 <0.5

MW‐01 03/27/2001 150 <1 <1 150 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 14 610 1100 0.7

MW‐01 04/18/2001 260 <1 <1 260 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 15 700 1300 <0.5

MW‐01 05/21/2001 210 <1 <1 210 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 11 530 1000 <0.5

MW‐01 06/19/2001 200 <1 <1 200 ‐‐ 310 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 12 770 1400 <0.5

MW‐01 07/17/2001 200 <1 <1 200 ‐‐ 350 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 16 800 1500 <0.5

MW‐01 08/02/2001 200 <1 <1 200 ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 15 820 1300 <0.5

MW‐01 09/05/2001 410 <1 <1 410 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 17 750 1200 <0.5

MW‐01 10/02/2001 580 <1 <1 580 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.4 990 1600 1.5

MW‐01 11/06/2001 500 <1 <1 500 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 22 850 1500 <0.5

MW‐01 12/05/2001 300 <1 <1 300 ‐‐ 750 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 19 1600 3000 3

MW‐01 01/04/2002 330 <1 <1 330 ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 19 900 1600 <0.5

MW‐01 02/05/2002 940 <1 <1 940 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 23 1300 2400 <0.5

MW‐01 03/04/2002 450 <1 <1 450 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 43 660 1300 <0.5

MW‐01 04/02/2002 270 <1 <1 270 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 26 640 1300 <0.5

MW‐01 05/07/2002 300 <1 <1 300 ‐‐ 410 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 27 910 1800 <0.5

MW‐01 06/04/2002 270 <1 <1 270 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 23 930 1700 <0.5

MW‐01 07/02/2002 300 <1 <1 300 ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 20 720 1500 <0.5

MW‐01 08/08/2002 370 <1 <1 370 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 24 680 1300 3.6

MW‐01 09/05/2002 130 <1 <1 130 ‐‐ 80 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 11 580 860 150

MW‐01 10/08/2002 160 <1 <1 160 ‐‐ 76 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9.7 430 680 57

MW‐01 11/05/2002 410 <1 <1 410 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 12 750 1300 24

MW‐01 12/06/2002 1000 <1 <1 1000 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 14 1600 2400 <0.5

MW‐01 01/07/2003 920 <1 <1 920 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 10 1500 2200 <0.5

MW‐01 02/05/2003 890 <1 <1 890 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8.2 1500 2300 <0.5

MW‐01 03/04/2003 830 <1 <1 830 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 10 1300 2100 <0.5

MW‐01 04/03/2003 940 <1 <1 940 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 14 1600 2300 <0.5

MW‐01 05/02/2003 930 <1 <1 930 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 13 1500 2400 <0.5

MW‐01 06/06/2003 920 <1 <1 920 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 15 1500 2400 <0.5

MW‐01 07/03/2003 1200 <1 <1 1200 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 17 1800 2800 <0.5

MW‐01 08/07/2003 1300 <1 <1 1300 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 35 1700 2900 <0.5

MW‐01 09/06/2003 1100 <1 <1 1100 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 52 1400 2600 2

MW‐01 10/03/2003 950 <1 <1 950 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 44 1400 2400 2.2

MW‐01 11/05/2003 800 <1 <1 800 ‐‐ 130 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 31 1200 1900 7

MW‐01 12/03/2003 860 <1 <1 860 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.3 38 1400 2100 62

Page 2 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐01 01/15/2004 740 <1 <1 740 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 25 1400 2200 140

MW‐01 02/06/2004 1100 <1 <1 1100 ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 21 1700 2700 8.9

MW‐01 03/03/2004 1300 <1 <1 1300 ‐‐ 330 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 22 2100 3300 2.1

MW‐01 04/07/2004 790 <1 <1 790 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 30 1800 2500 3.3

MW‐01 05/13/2004 450 <1 <1 450 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 19 880 1600 <0.5

MW‐01 06/05/2004 380 <1 <1 380 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 20 700 1300 0.6

MW‐01 07/09/2004 330 <1 <1 330 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 18 690 1200 0.8

MW‐01 08/07/2004 730 <1 <1 730 ‐‐ 370 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 31 1400 2500 0.5

MW‐01 09/07/2004 1100 <1 <1 1100 ‐‐ 450 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 43 1900 3200 <0.5

MW‐01 10/05/2004 830 <1 <1 830 ‐‐ 460 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 51 2000 3500 <0.5

MW‐01 11/02/2004 1300 <1 <1 1300 ‐‐ 600 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 59 2400 4100 <0.5

MW‐01 12/02/2004 1000 <1 <1 1000 ‐‐ 520 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 52 2000 3500 44

MW‐01 01/14/2005 1100 <1 <1 1100 ‐‐ 490 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 48 2100 3700 76

MW‐01 02/02/2005 1000 <1 <1 1000 ‐‐ 540 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 43 2300 3700 77

MW‐01 03/09/2005 1100 <1 <1 1100 ‐‐ 590 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 39 2400 4000 100

MW‐01 04/06/2005 1200 <1 <1 1200 ‐‐ 580 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 32 2400 4000 110

MW‐01 05/10/2005 1000 <1 <1 1000 ‐‐ 430 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 28 2100 3400 96

MW‐01 06/06/2005 910 <1 <1 910 ‐‐ 400 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.4 26 1900 3100 95

MW‐01 07/22/2005 1000 <1 <1 1000 ‐‐ 330 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 19 1900 2900 37

MW‐01 08/02/2005 1100 <1 <1 1100 ‐‐ 350 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 15 2000 3100 47

MW‐01 09/09/2005 980 <1 <1 980 ‐‐ 440 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 11 2200 3200 140

MW‐01 10/07/2005 870 <1 <1 870 ‐‐ 500 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9 2300 3300 140

MW‐01 11/11/2005 1000 <1 <1 1000 ‐‐ 540 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8 2300 3700 160

MW‐01 12/08/2005 1000 <1 <1 1000 ‐‐ 560 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 3.9 2700 4100 310

MW‐01 01/05/2006 1100 <1 <1 1100 ‐‐ 620 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 3 2800 4200 310

MW‐01 02/08/2006 1100 <1 <1 1100 ‐‐ 590 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.3 4.2 2600 3900 260

MW‐01 03/13/2006 1000 <1 <1 1000 ‐‐ 630 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 5.2 2700 4100 320

MW‐01 08/03/2006 730 <10 <10 730 ‐‐ 460 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.5 2000 3120 260

MW‐01 09/05/2006 670 <10 <10 670 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.7 1500 2250 160

MW‐01 10/09/2006 760 <10 <10 760 ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.3 1600 2540 200

MW‐01 11/06/2006 770 <10 <10 770 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.0 1600 2410 180

MW‐01 12/11/2006 790 <10 <10 790 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.7 1600 2610 130

MW‐01 01/03/2007 730 <10 <10 730 ‐‐ 330 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.7 1900 2940 160

MW‐01 02/05/2007 880 <20 <20 880 ‐‐ 310 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.4 2100 3060 120

MW‐01 03/05/2007 860 <10 <10 860 ‐‐ 320 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.2 2200 3120 84

Page 3 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐01 04/05/2007 1100 <10 <10 1100 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.8 2400 3470 67

MW‐01 05/03/2007 830 <10 <10 830 ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.6 2600 3760 110

MW‐01 06/07/2007 770 <10 <10 770 ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.6 2600 3780 110

MW‐01 07/02/2007 820 <10 <10 820 ‐‐ 320 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.6 2500 3610 120

MW‐01 08/02/2007 990 <10 <10 990 ‐‐ 390 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.9 3000 4160 150

MW‐01 09/10/2007 1100 <10 <10 1100 ‐‐ 430 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.7 2900 4360 180

MW‐01 10/08/2007 1100 <20 <20 1100 ‐‐ 430 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 2600 3960 190

MW‐01 11/07/2007 980 <20 <20 980 ‐‐ 370 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.6 2600 3740 140

MW‐01 12/06/2007 810 <10 <10 810 ‐‐ 370 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.9 2600 3700 120

MW‐01 01/14/2008 650 <10 <10 650 ‐‐ 380 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.8 2600 3560 110

MW‐01 02/07/2008 680 <10 <10 680 ‐‐ 380 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 2500 3730 89

MW‐01 03/04/2008 720 <10 <10 720 ‐‐ 360 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.1 2200 3310 68

MW‐01 04/10/2008 900 <10 <10 900 ‐‐ 310 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.8 2000 2980 54

MW‐01 05/05/2008 960 <10 <10 960 ‐‐ 290 27 0.85 14 0.66 140 520 ‐‐ ‐‐ ‐‐ 2.6 2000 2980 51

MW‐01 06/03/2008 1200 <20 <20 1200 ‐‐ 320 31 0.92 16 0.69 150 550 ‐‐ ‐‐ ‐‐ 2.9 2100 3130 45

MW‐01 07/01/2008 1300 <20 <20 1300 ‐‐ 350 34 1.0 17 0.79 160 630 ‐‐ ‐‐ ‐‐ 3.3 2200 3340 65

MW‐01 08/05/2008 970 <10 <10 970 ‐‐ 380 65 0.88 27 1.1 220 800 ‐‐ ‐‐ ‐‐ 2.6 3100 4530 270

MW‐01 09/08/2008 480 <5.0 <5.0 480 ‐‐ 230 52 0.25 16 0.65 190 670 ‐‐ ‐‐ ‐‐ 2.9 2800 3900 380

MW‐01 10/09/2008 400 <10 <10 400 ‐‐ 170 31 0.19 9.2 0.58 130 440 ‐‐ ‐‐ ‐‐ 3.3 2200 2850 290

MW‐01 11/04/2008 390 <10 <10 390 ‐‐ 130 28 0.26 8.3 0.65 120 400 ‐‐ ‐‐ ‐‐ 3.1 1800 2470 250

MW‐01 12/03/2008 450 <10 <10 450 ‐‐ 170 28 0.32 8.9 0.64 120 440 ‐‐ ‐‐ ‐‐ 2.5 1900 2600 280

MW‐01 01/13/2009 620 <8.2 <8.2 620 ‐‐ 240 39 0.5 14 0.88 150 580 ‐‐ ‐‐ ‐‐ 1.8 2000 2980 240

MW‐01 02/04/2009 680 <8.2 <8.2 680 ‐‐ 240 34 0.43 14 0.77 140 570 ‐‐ ‐‐ ‐‐ 2.1 2000 2800 220

MW‐01 03/04/2009 610 <8.2 <8.2 610 ‐‐ 250 32 0.34 13 0.74 140 530 ‐‐ ‐‐ ‐‐ 2.2 2000 2830 290

MW‐01 04/14/2009 590 <8.2 <8.2 590 ‐‐ 230 45 0.32 17 0.79 170 580 ‐‐ ‐‐ ‐‐ 1.9 2100 2990 280

MW‐01 05/04/2009 340 <8.2 <8.2 340 ‐‐ 65 12 0.26 4.4 0.19 76 280 ‐‐ ‐‐ ‐‐ 2.6 1000 1450 140

MW‐01 06/09/2009 300 <8.2 <8.2 300 ‐‐ 160 40 0.079 15 0.77 160 270 ‐‐ ‐‐ ‐‐ 2.1 1400 1960 210

MW‐01 07/14/2009 250 <8.2 <8.2 250 ‐‐ 180 58 <0.050 Jo 24 1.0 200 220 ‐‐ ‐‐ ‐‐ 2.2 1500 2020 120

MW‐01 08/04/2009 280 <8.2 <8.2 280 ‐‐ 150 45 <0.05 Jo 18 0.77 160 220 ‐‐ ‐‐ ‐‐ 2 1400 1880 77

MW‐01 09/08/2009 260 <16 <16 260 ‐‐ 190 45 <0.050 Jo 17 0.68 180 250 ‐‐ ‐‐ ‐‐ 1.6 1300 2020 65

MW‐01 10/06/2009 250 <8.2 <8.2 250 ‐‐ 160 43 <0.050 Jo 17 0.83 170 220 ‐‐ ‐‐ ‐‐ 1.9 1300 1810 64

MW‐01 11/10/2009 320 <8.2 <8.2 320 ‐‐ 160 38 0.065 17 0.7 150 240 ‐‐ ‐‐ ‐‐ 1.8 1300 1870 80

MW‐01 12/08/2009 300 <8.2 <8.2 300 ‐‐ 180 40 0.05 17 0.72 150 240 ‐‐ ‐‐ ‐‐ 1.7 1300 1840 74

MW‐01 01/05/2010 340 <4.1 <4.1 340 ‐‐ 160 41 0.065 17 0.73 160 280 ‐‐ ‐‐ ‐‐ 1.7 1400 2020 84

MW‐01 02/10/2010 410 <8.2 <8.2 410 ‐‐ 170 41 0.11 19 0.85 150 310 ‐‐ ‐‐ ‐‐ 1.0 1500 2120 110

Page 4 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐01 03/08/2010 380 <8.2 <8.2 380 ‐‐ 200 47 0.1 21 1.0 180 280 ‐‐ ‐‐ ‐‐ 1.0 1600 2080 130

MW‐01 04/15/2010 290 <8.2 ‐‐ 290 ‐‐ 150 49 0.058 19 1 170 210 ‐‐ ‐‐ ‐‐ 1.4 1300 1790 100

MW‐01 07/08/2010 200 <8.2 ‐‐ 200 ‐‐ 98 31 <0.05 Jo 13 0.68 130 140 ‐‐ ‐‐ ‐‐ 1.6 820 1260 59

MW‐01 10/27/2010 130 <8.2 ‐‐ 130 ‐‐ 120 54 <0.05 Jo 22 1.5 160 91 0.023 ‐‐ ‐‐ 1.4 1000 1350 66

MW‐01 01/19/2011 220 <8.2 ‐‐ 220 ‐‐ 130 46 <0.05 Jo 22 1.4 130 130 ‐‐ ‐‐ ‐‐ 0.89 1100 1470 76

MW‐01 04/04/2011 160 <8.2 ‐‐ 160 ‐‐ 97 55 <0.05 Jo 24 1.7 150 89 ‐‐ ‐‐ ‐‐ 0.91 940 1340 53

MW‐01 07/07/2011 190 <8.2 ‐‐ 190 ‐‐ 65 41 <0.05 18 1.1 120 82 ‐‐ ‐‐ 45 1.6 770 1120 33

MW‐01 11/09/2011 157 <5.0 ‐‐ 157 <2.0 213 84.6 J <0.20 32.1 J 1.99 J 203 74.0 J 0.082 ‐‐ 80.2 J‐ <0.20 1140 1730 30.1

MW‐01 01/19/2012 140 ‐‐ ‐‐ 140 1.6 190 65 <0.050 Jo 26 1.8 160 71 0.068 ‐‐ 57 2.1 1000 1480 36

MW‐01 04/03/2012 176 <5.0 ‐‐ 176 <1.0 188 86.0 <0.20 33.9 2.29 171 77.9 0.086 ‐‐ 62.2 <0.26 1100 1610 <36.5 U

MW‐01 07/23/2012 174 <5.0 ‐‐ 174 <0.20 41.2 27.9 <0.20 11.6 0.634 103 63.3 0.038 ‐‐ 24.4 <0.25 U 470 707 27.0

MW‐01 10/15/2012 <150 U <5.0 ‐‐ <150 U <2.0 <30.6 U 42.1 J 0.266 17.0 J 0.712 J 116 J 54.7 J 0.047 ‐‐ 46.8 0.25 649 901 <29.2 U

MW‐01 01/22/2013 150 <5.0 ‐‐ 150 <0.50 37.2 38.1 <0.20 16.1 0.861 94.2 52.3 0.046 ‐‐ 42.9 <0.20 582 710 30.0

MW‐01 04/16/2013 148 <5.0 ‐‐ 148 <0.50 29.9 31.3 <0.20 12.5 0.797 90.4 52.4 0.045 ‐‐ 37.2 0.32 528 757 31.5

MW‐01 07/17/2013 125 <5.0 ‐‐ 125 <0.50 43.0 27.3 <0.20 11.7 0.573 80.4 J 44.4 0.019 ‐‐ 24.5 <0.36 U 450 763 29.0

MW‐01 10/21/2013 84.0 <5.0 ‐‐ 84.0 ‐‐ 40.4 29.9 J 2.87 13.0 J 0.604 83.3 33.1 J ‐‐ ‐‐ 31.0 0.48 476 750 24.2

MW‐01 01/22/2014 102 <5.0 ‐‐ 102 ‐‐ 50.6 30.4 <0.20 14.0 0.528 80.3 34.8 ‐‐ ‐‐ 29.7 <4.5 U 482 723 27.6

MW‐01 04/22/2014 80.8 <5.0 ‐‐ 80.8 ‐‐ 47.0 42.9 <0.20 18.5 J 0.709 98.2 J 40.2 J ‐‐ ‐‐ 46.1 <0.20 606 920 34.6

MW‐01 10/20/2014 121 <5.0 ‐‐ 121 ‐‐ 60.7 26.3 <0.20 9.83 0.365 75.8 64.9 ‐‐ ‐‐ 23.6 <0.20 482 768 23.0

MW‐01 04/15/2015 218 <5.0 ‐‐ 218 ‐‐ 159 126 J <0.20 46.0 J 1.07 J 123 J 103 J ‐‐ ‐‐ 64.6 0.29 1160 1590 34.3

MW‐01 10/15/2015 177 <5.0 ‐‐ 177 ‐‐ 91.4 53.0 <0.20 21.2 0.308 J 79.6 73.1 ‐‐ ‐‐ 26.2 <0.20 651 1030 38.7

MW‐01 04/14/2016 168 <5.0 ‐‐ 168 ‐‐ 101 68.6 <0.20 28.5 0.315 J 74.5 75.8 J ‐‐ ‐‐ 48.1 <0.20 866 1260 50.3

MW‐01 10/12/2016 173 <5.0 ‐‐ 175 ‐‐ 34 37.6 <0.3 15.6 0.131 76.9 J 70.3 ‐‐ ‐‐ 29 <0.53 R 498 738 28

MW‐02 07/27/1989 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11.4 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 ‐‐ ‐‐ 300 ‐‐

MW‐02 10/16/1989 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12.2 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 ‐‐ ‐‐ 320 ‐‐

MW‐02 01/15/1990 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 20.2 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 ‐‐ ‐‐ 479 ‐‐

MW‐02 04/10/1990 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.8 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 ‐‐ ‐‐ 284 ‐‐

MW‐02 07/30/1990 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 41.9 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 23 ‐‐ ‐‐ 578 ‐‐

MW‐02 10/29/1990 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 18.7 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 ‐‐ ‐‐ 460 ‐‐

MW‐02 01/08/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.1 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 42 ‐‐ ‐‐ 480 ‐‐

MW‐02 04/18/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 39 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 ‐‐ ‐‐ 400 ‐‐

MW‐02 07/26/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 21 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 ‐‐ ‐‐ 570 ‐‐

MW‐02 10/23/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 66 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 ‐‐ ‐‐ 660 ‐‐

MW‐02 01/24/1992 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 186 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 ‐‐ ‐‐ 1160 ‐‐

MW‐02 04/02/1992 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 197 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.4 ‐‐ ‐‐ 1621 ‐‐

Page 5 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐02 07/09/1992 1210 <1 <1 1210 ‐‐ 235 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ 1320.1 3030 13.9

MW‐02 10/06/1992 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 175 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ ‐‐ 1532 ‐‐

MW‐02 01/13/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 89 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.77 ‐‐ ‐‐ 701 ‐‐

MW‐02 04/15/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 223.8 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.5 ‐‐ ‐‐ 1801 ‐‐

MW‐02 07/14/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 93 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ ‐‐ 1495 ‐‐

MW‐02 10/11/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 275 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ ‐‐ 2114 ‐‐

MW‐02 01/18/1994 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 246.5 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ ‐‐ 2030 ‐‐

MW‐02 04/19/1994 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ ‐‐ 2180 ‐‐

MW‐02 07/18/1994 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ ‐‐ 1800 ‐‐

MW‐02 11/14/1994 1089 <1 <1 1089 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ 1372 2340 2.6

MW‐02 02/20/1995 892.5 <1 <1 892.5 ‐‐ 310 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ 1354 2360 20

MW‐02 05/11/1995 1053 <1 <1 1053 ‐‐ 265.6 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ 1478 2600 6

MW‐02 06/19/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 7.9 1700 2400 ‐‐

MW‐02 07/11/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 57 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 6.2 900 1400 18

MW‐02 08/15/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9.2 1100 1800 ‐‐

MW‐02 11/14/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 15 1300 2000 ‐‐

MW‐02 02/14/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 14 1000 1600 ‐‐

MW‐02 05/21/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8.2 1100 2100 ‐‐

MW‐02 08/20/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 31 1200 2100 ‐‐

MW‐02 11/19/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 15 1300 2200 ‐‐

MW‐02 02/18/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 34 1300 2200 ‐‐

MW‐02 05/20/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 38 1100 2100 ‐‐

MW‐02 08/25/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 62 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 29 750 1500 ‐‐

MW‐02 11/20/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 17 500 810 ‐‐

MW‐02 02/26/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 27 1300 2200 ‐‐

MW‐02 05/19/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 100 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 13 1100 1800 ‐‐

MW‐02 08/20/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 87 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 6.4 730 1100 ‐‐

MW‐02 11/24/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.2 520 730 ‐‐

MW‐02 11/22/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 50 1000 2000 ‐‐

MW‐02 02/11/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 22 1500 2600 ‐‐

MW‐02 05/02/2000 1000 <1 <1 1000 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.16 20 1400 2300 <0.5

MW‐02 09/21/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 27 1300 2000 ‐‐

MW‐02 11/30/2000 1100 <1 <1 1100 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 40 1500 2500 ‐‐

MW‐02 12/14/2000 1100 <1 <1 1100 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 41 1500 2500 ‐‐

MW‐02 01/05/2001 1100 <1 <1 1100 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 35 1500 2500 ‐‐

Page 6 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐02 02/02/2001 1100 <1 <1 1100 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ 1800 2700 <0.5

MW‐02 03/18/2001 1200 <1 <1 1200 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 30 1600 2700 <0.5

MW‐02 04/17/2001 1200 <1 <1 1200 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 29 1600 2600 <0.5

MW‐02 05/21/2001 1300 <1 <1 1300 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 60 1800 3000 0.6

MW‐02 06/19/2001 1400 <1 <1 1400 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 51 1800 3000 1.2

MW‐02 07/17/2001 1300 <1 <1 1300 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 48 1900 3100 <0.5

MW‐02 08/02/2001 1300 <1 <1 1300 ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 46 1800 3100 <0.5

MW‐02 09/05/2001 1400 <1 <1 1400 ‐‐ 350 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 51 2100 3300 2.5

MW‐02 10/02/2001 1500 <1 <1 1500 ‐‐ 320 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 53 2100 3200 4.7

MW‐02 11/06/2001 1500 <1 <1 1500 ‐‐ 350 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 51 2100 3400 7.4

MW‐02 12/03/2001 1400 <1 <1 1400 ‐‐ 330 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 59 1900 3300 6.5

MW‐02 01/04/2002 1300 <1 <1 1300 ‐‐ 380 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 60 2000 3500 14

MW‐02 02/05/2002 1400 <1 <1 1400 ‐‐ 440 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.2 61 2100 3800 58

MW‐02 03/04/2002 1300 <1 <1 1300 ‐‐ 330 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 17 2000 3400 20

MW‐02 04/02/2002 1300 <1 <1 1300 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 50 1800 3200 <0.5

MW‐02 05/07/2002 1200 <1 <1 1200 ‐‐ 380 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 50 2000 3400 98

MW‐02 06/04/2002 1200 <1 <1 1200 ‐‐ 400 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 45 2100 3500 97

MW‐02 07/02/2002 1200 <1 <1 1200 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 38 1900 3300 <0.5

MW‐02 08/08/2002 1100 <1 <1 1100 ‐‐ 350 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 47 1800 3100 60

MW‐02 09/03/2002 720 <1 <1 720 ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 31 1300 2300 88

MW‐02 10/08/2002 820 <1 <1 820 ‐‐ 350 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 37 1700 2700 140

MW‐02 11/05/2002 700 <1 <1 700 ‐‐ 310 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 44 1600 2700 180

MW‐02 12/06/2002 460 <1 <1 460 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 25 1100 1800 190

MW‐02 01/06/2003 230 <1 <1 230 ‐‐ 69 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9.4 550 890 81

MW‐02 02/05/2003 1100 <1 <1 1100 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 29 1700 2700 1

MW‐02 03/04/2003 1300 <1 <1 1300 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 47 1900 3100 <0.5

MW‐02 04/03/2003 1200 <1 <1 1200 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 41 1700 2800 <0.5

MW‐02 05/05/2003 1100 <1 <1 1100 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.01 19 1600 2600 0.8

MW‐02 06/06/2003 950 <1 <1 950 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 17 1600 2500 <0.5

MW‐02 07/03/2003 970 <1 <1 970 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 22 1500 2500 <0.5

MW‐02 08/07/2003 480 <1 <1 480 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.4 15 820 1700 17

MW‐02 09/05/2003 690 <1 <1 690 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 22 1100 1900 12

MW‐02 10/03/2003 680 <1 <1 680 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.3 18 1200 2000 61

MW‐02 11/05/2003 670 <1 <1 670 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 15 1200 2000 51

MW‐02 12/04/2003 860 <1 <1 860 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.2 10 1300 1900 45

Page 7 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐02 01/15/2004 900 <1 <1 900 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 19 1600 2400 3.4

MW‐02 02/06/2004 810 <1 <1 810 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 12 1200 1900 7

MW‐02 03/04/2004 960 <1 <1 960 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 17 1400 2300 4.2

MW‐02 04/08/2004 920 <1 <1 920 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 13 1300 2000 25

MW‐02 05/14/2004 610 <1 <1 610 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.2 13 1100 1600 69

MW‐02 06/05/2004 520 <1 <1 520 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 14 990 1600 120

MW‐02 07/09/2004 860 <1 <1 860 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 18 1300 2200 32

MW‐02 08/07/2004 1100 <1 <1 1100 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 16 2000 2800 0.9

MW‐02 09/07/2004 1100 <1 <1 1100 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 31 1500 2500 <0.5

MW‐02 10/05/2004 830 <1 <1 830 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 10 1400 2300 1

MW‐02 11/02/2004 650 <1 <1 650 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 22 1300 2300 19

MW‐02 12/02/2004 870 <1 <1 870 ‐‐ 370 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 22 1700 2700 12

MW‐02 01/14/2005 830 <1 <1 830 ‐‐ 510 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.4 29 1800 3100 15

MW‐02 02/02/2005 970 <1 <1 970 ‐‐ 460 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.5 14 1800 3000 36

MW‐02 03/09/2005 860 <1 <1 860 ‐‐ 430 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.3 27 1700 2900 13

MW‐02 04/06/2005 900 <1 <1 900 ‐‐ 390 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 18 1600 2800 21

MW‐02 05/10/2005 950 <1 <1 950 ‐‐ 430 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2 15 1900 3000 43

MW‐02 06/06/2005 930 <1 <1 930 ‐‐ 420 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1 9.2 1900 3000 50

MW‐02 07/22/2005 870 <1 <1 870 ‐‐ 360 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 10 1900 3000 130

MW‐02 08/02/2005 870 <1 <1 870 ‐‐ 370 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 28 12 1900 3100 130

MW‐02 09/06/2005 880 10 <1 880 ‐‐ 410 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.2 16 1800 3000 100

MW‐02 10/05/2005 980 <1 <1 980 ‐‐ 450 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.1 12 2000 3300 120

MW‐02 11/11/2005 910 <1 <1 910 ‐‐ 450 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.7 18 1900 3300 150

MW‐02 12/08/2005 890 <1 <1 890 ‐‐ 440 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 20 2100 3300 170

MW‐02 01/06/2006 950 <1 <1 950 ‐‐ 500 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.3 18 2100 3300 180

MW‐02 02/08/2006 960 20 <1 960 ‐‐ 510 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2 12 2400 3600 180

MW‐02 03/13/2006 1000 <1 <1 1000 ‐‐ 540 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.2 10 2400 3800 190

MW‐02 08/03/2006 910 <10 <10 910 ‐‐ 460 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 18 2000 3240 190

MW‐02 09/05/2006 920 <10 <10 920 ‐‐ 420 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 2000 3180 180

MW‐02 10/09/2006 970 <10 <10 970 ‐‐ 360 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.1 1900 2920 130

MW‐02 11/06/2006 990 <10 <10 990 ‐‐ 360 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.8 1800 2690 100

MW‐02 12/11/2006 900 <10 <10 900 ‐‐ 350 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.7 1900 2950 140

MW‐02 01/03/2007 920 <10 <10 920 ‐‐ 350 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11 1900 2950 140

MW‐02 02/05/2007 1300 <20 <20 1300 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.2 1900 2920 120

MW‐02 03/05/2007 1400 <20 <20 1400 ‐‐ 330 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.4 2300 3280 59

Page 8 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐02 04/05/2007 1200 <20 <20 1200 ‐‐ 320 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.2 2000 3170 88

MW‐02 05/03/2007 1000 <10 <10 1000 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.7 1900 2960 97

MW‐02 06/07/2007 1000 <10 <10 1000 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 2200 3440 100

MW‐02 07/02/2007 960 <10 <10 960 ‐‐ 320 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.3 2200 3230 100

MW‐02 08/02/2007 1100 <10 <10 1100 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.7 2400 3600 89

MW‐02 09/10/2007 950 <10 <10 950 ‐‐ 330 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.1 2200 3400 100

MW‐02 10/08/2007 910 <20 <20 910 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.4 2100 3250 95

MW‐02 11/07/2007 820 <20 <20 820 ‐‐ 350 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.2 2200 3140 100

MW‐02 12/06/2007 1000 <10 <10 1000 ‐‐ 370 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.1 2400 3460 92

MW‐02 01/14/2008 780 <10 <10 780 ‐‐ 370 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.5 2600 3600 130

MW‐02 02/07/2008 780 <10 <10 780 ‐‐ 350 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 2300 3340 69

MW‐02 03/04/2008 1000 <10 <10 1000 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.1 2000 3040 55

MW‐02 04/10/2008 1300 <20 <20 1300 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.1 2100 3260 50

MW‐02 05/05/2008 1200 <20 <20 1200 ‐‐ 280 39 0.55 11 0.69 140 560 ‐‐ ‐‐ ‐‐ 2 2000 3140 53

MW‐02 06/03/2008 1300 <20 <20 1300 ‐‐ 340 48 0.44 12 0.38 150 630 ‐‐ ‐‐ ‐‐ 1.8 2300 3430 57

MW‐02 07/01/2008 1200 <20 <20 1200 ‐‐ 390 49 0.56 15 0.54 170 700 ‐‐ ‐‐ ‐‐ 2.5 2400 3690 92

MW‐02 08/05/2008 710 <20 <20 710 ‐‐ 270 21 0.28 9.5 0.33 120 490 ‐‐ ‐‐ ‐‐ 2.9 1600 2640 67

MW‐02 09/08/2008 550 <10 <10 550 ‐‐ 150 20 0.62 11 0.4 100 380 ‐‐ ‐‐ ‐‐ 4.3 1500 2010 130

MW‐02 10/09/2008 370 <5.0 <5.0 370 ‐‐ 91 12 1.2 8.1 0.24 84 270 ‐‐ ‐‐ ‐‐ 3.9 1600 1640 230

MW‐02 11/04/2008 390 <10 <10 390 ‐‐ 110 14 0.5 12 0.48 110 350 ‐‐ ‐‐ ‐‐ 2.6 1600 2170 300

MW‐02 12/03/2008 520 <10 <10 520 ‐‐ 210 17 0.64 11 0.51 110 390 ‐‐ ‐‐ ‐‐ 3.2 1600 2300 230

MW‐02 01/13/2009 450 <8.2 <8.2 450 ‐‐ 120 14 1.3 9.1 0.43 96 320 ‐‐ ‐‐ ‐‐ 4.2 1400 1680 120

MW‐02 02/04/2009 530 <8.2 <8.2 530 ‐‐ 180 13 0.51 9.3 0.39 110 380 ‐‐ ‐‐ ‐‐ 2.8 1300 1960 120

MW‐02 03/04/2009 430 <8.2 <8.2 430 ‐‐ 140 10 1.2 7.2 0.33 93 300 ‐‐ ‐‐ ‐‐ 3.5 1300 1620 120

MW‐02 04/14/2009 320 <8.2 <8.2 320 ‐‐ 120 11 0.45 6.5 0.3 83 270 ‐‐ ‐‐ ‐‐ 4.2 1100 1320 140

MW‐02 05/04/2009 470 <8.2 <8.2 470 ‐‐ 170 19 0.72 8.3 0.42 100 280 ‐‐ ‐‐ ‐‐ 4.6 1200 1630 81

MW‐02 06/09/2009 410 <8.2 <8.2 410 ‐‐ 150 32 0.48 11 0.78 150 210 ‐‐ ‐‐ ‐‐ 4 1200 1410 51

MW‐02 07/14/2009 440 <8.2 <8.2 440 ‐‐ 93 44 0.6 14 0.92 140 220 ‐‐ ‐‐ ‐‐ 3.4 1200 1650 42

MW‐02 08/04/2009 370 <8.2 <8.2 370 ‐‐ 170 34 0.35 12 0.73 120 230 ‐‐ ‐‐ ‐‐ 3.2 1100 1650 57

MW‐02 09/08/2009 220 <8.2 <8.2 220 ‐‐ 61 15 1.0 6.0 0.28 89 140 ‐‐ ‐‐ ‐‐ 2.7 880 960 21

MW‐02 10/06/2009 200 <4.1 <4.1 200 ‐‐ 51 11 0.51 5.0 0.23 86 150 ‐‐ ‐‐ ‐‐ 2.1 830 878 17

MW‐02 11/10/2009 260 <8.2 <8.2 260 ‐‐ 88 15 0.55 7.1 0.28 97 160 ‐‐ ‐‐ ‐‐ 2.1 900 1320 30

MW‐02 12/08/2009 380 <8.2 <8.2 380 ‐‐ 150 21 0.36 9.5 0.35 110 240 ‐‐ ‐‐ ‐‐ 2.1 1100 1590 76

MW‐02 01/05/2010 330 <4.1 <4.1 330 ‐‐ 130 17 0.37 8.0 0.32 120 230 ‐‐ ‐‐ ‐‐ 1.8 1000 1490 53

MW‐02 02/10/2010 110 <4.1 <4.1 110 ‐‐ 53 30 0.079 11 0.059 110 83 ‐‐ ‐‐ ‐‐ 0.84 810 974 23

Page 9 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐02 03/08/2010 220 <8.2 <8.2 220 ‐‐ 100 26 0.25 9.9 0.21 100 140 ‐‐ ‐‐ ‐‐ 1.6 820 1150 45

MW‐02 04/15/2010 140 <4.1 ‐‐ 140 ‐‐ 51 29 0.46 9.7 0.12 100 99 ‐‐ ‐‐ ‐‐ 1.3 760 980 26

MW‐02 07/08/2010 150 <4.1 ‐‐ 150 ‐‐ 71 26 0.058 8.5 0.06 80 50 ‐‐ ‐‐ ‐‐ 1.5 520 709 21

MW‐02 10/27/2010 170 <4.1 ‐‐ 170 ‐‐ 66 25 0.28 7.2 0.16 87 70 0.058 ‐‐ ‐‐ 1.9 540 756 21

MW‐02 01/19/2011 120 <4.1 ‐‐ 120 ‐‐ 66 27 0.064 10 0.21 95 62 ‐‐ ‐‐ ‐‐ 0.79 640 825 27

MW‐02 04/04/2011 130 <4.1 ‐‐ 130 ‐‐ 41 23 0.32 8.4 0.11 94 52 ‐‐ ‐‐ ‐‐ 1.0 480 708 22

MW‐02 07/07/2011 110 <4.1 ‐‐ 110 ‐‐ 26 22 0.071 6.8 0.051 61 33 ‐‐ ‐‐ 14 1.4 370 501 13

MW‐02 11/09/2011 186 <5.0 ‐‐ 186 <2.0 101 42.4 J <0.20 22.0 J 1.26 J 208 63.1 J 0.083 ‐‐ 60.3 J‐ <0.20 818 1310 22.7

MW‐02 01/19/2012 160 ‐‐ ‐‐ 160 0.74 86 44 <0.050 Jo 21 0.46 160 68 0.048 ‐‐ 60 1.4 840 1200 23

MW‐02 04/03/2012 <140 U <5.0 ‐‐ <140 U <0.20 72.8 25.2 <0.20 10.9 0.205 96.6 44.4 0.027 J ‐‐ 13.4 2.0 424 667 <19.7 U

MW‐02 07/23/2012 258 <5.0 ‐‐ 258 0.5 137 49.0 <0.20 22.4 0.395 137 88.4 0.085 ‐‐ 9.5 <0.71 U 653 1090 19.3

MW‐02 10/15/2012 <128 U <5.0 ‐‐ <128 U <1.0 <38.7 U 22.6 J <0.20 13.1 J 0.321 J 96.1 J 54.4 J 0.037 ‐‐ 22.9 0.59 461 704 <16.0 U

MW‐02 01/22/2013 <120 U <5.0 ‐‐ <120 U <0.50 46.7 19.5 <0.20 8.77 0.055 65.3 48.1 0.029 ‐‐ 17.1 <0.20 417 502 22.3

MW‐02 04/16/2013 91.4 <5.0 ‐‐ 91.4 <0.50 40.7 23.4 <0.20 8.34 <0.015 66.2 49.3 0.023 ‐‐ 22.5 <0.20 397 533 21.8

MW‐02 07/17/2013 106 <5.0 ‐‐ 106 <0.50 30.2 17.2 <0.20 7.12 0.0779 70.0 J 46.3 0.019 ‐‐ 16.9 <0.20 358 607 24.5

MW‐02 10/21/2013 90.0 <5.0 ‐‐ 90.0 ‐‐ 55.8 18.2 J <0.20 7.88 J 0.11 65.8 45.3 J ‐‐ ‐‐ 19.3 <0.20 423 669 18.9

MW‐02 01/22/2014 94.0 <5.0 ‐‐ 94.0 ‐‐ 54.8 22.3 <0.20 8.6 0.0341 62.1 49.9 ‐‐ ‐‐ 22.3 <0.51 U 452 669 22.7

MW‐02 04/22/2014 80.0 <5.0 ‐‐ 80.0 ‐‐ 52.9 42.5 J <0.20 17.0 J 0.126 90.6 J 56.4 J ‐‐ ‐‐ 49.2 <0.20 649 1480 J 34.4

MW‐03 10/29/1990 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 805 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.47 ‐‐ ‐‐ 4000 ‐‐

MW‐03 01/08/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 148.9 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.23 ‐‐ ‐‐ 4000 ‐‐

MW‐03 04/18/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 700 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.36 ‐‐ ‐‐ 3700 ‐‐

MW‐03 07/26/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 377 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.32 ‐‐ ‐‐ 2400 ‐‐

MW‐03 10/23/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.23 ‐‐ ‐‐ 2000 ‐‐

MW‐03 01/24/1992 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 248 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.23 ‐‐ ‐‐ 1770 ‐‐

MW‐03 04/02/1992 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 185 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ ‐‐ 1492 ‐‐

MW‐03 07/09/1992 220 <1 <1 220 ‐‐ 124 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ 481.9 1020 35.7

MW‐03 10/06/1992 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 203.6 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ ‐‐ 1270 ‐‐

MW‐03 01/13/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 239.8 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.59 ‐‐ ‐‐ 1660 ‐‐

MW‐03 04/15/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 291.8 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.8 ‐‐ ‐‐ 2170 ‐‐

MW‐03 07/14/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 246 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ ‐‐ 2280 ‐‐

MW‐03 10/11/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 307.5 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.68 ‐‐ ‐‐ 2470 ‐‐

MW‐03 01/18/1994 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 299 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ ‐‐ 2570 ‐‐

MW‐03 04/19/1994 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ ‐‐ 2460 ‐‐

MW‐03 07/18/1994 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ ‐‐ 2200 ‐‐

MW‐03 11/14/1994 893 <1 <1 893 ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ 1260 2250 15

Page 10 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐03 02/20/1995 969 <1 <1 969 ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ 1356 2320 9.7

MW‐03 05/11/1995 962 <1 <1 962 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ 1564 2360 6.5

MW‐03 06/19/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.4 1700 2400 ‐‐

MW‐03 07/11/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 1500 2400 ‐‐

MW‐03 08/15/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 1500 2400 ‐‐

MW‐03 11/14/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 3 1700 2500 ‐‐

MW‐03 02/14/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 4.5 1700 2500 ‐‐

MW‐03 05/21/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.4 1700 2600 ‐‐

MW‐03 08/20/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 1700 2600 ‐‐

MW‐03 11/19/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.7 1600 2600 ‐‐

MW‐03 02/18/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 1600 2500 ‐‐

MW‐03 05/20/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 1600 2600 ‐‐

MW‐03 08/25/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.1 1400 2400 ‐‐

MW‐03 11/20/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 3.5 1500 2300 ‐‐

MW‐03 02/26/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.3 1500 2400 ‐‐

MW‐03 05/19/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2 1400 2200 ‐‐

MW‐03 08/20/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.7 1200 1700 ‐‐

MW‐03 11/24/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.2 990 1600 ‐‐

MW‐03 02/15/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 980 1500 ‐‐

MW‐03 05/24/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 320 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.7 1100 1800 ‐‐

MW‐03 02/18/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 370 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.4 1200 2000 ‐‐

MW‐03 05/02/2000 460 <1 <1 460 ‐‐ 370 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.3 1200 2000 14

MW‐03 11/21/2000 600 <1 <1 600 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 4.3 940 1500 ‐‐

MW‐03 12/15/2000 620 <1 <1 620 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 2.5 950 1500 ‐‐

MW‐03 01/07/2001 640 <1 <1 640 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 3.1 1000 1500 ‐‐

MW‐03 02/08/2001 600 <1 <1 600 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ 1100 1600 0.6

MW‐03 03/25/2001 730 <1 <1 730 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 1100 1700 0.7

MW‐03 04/18/2001 760 <1 <1 760 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.5 1100 1800 <0.5

MW‐03 05/24/2001 730 <1 <1 730 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.7 1100 1700 1.1

MW‐03 06/28/2001 660 <1 <1 660 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 1000 1600 14

MW‐03 07/19/2001 580 <1 <1 580 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 3.7 960 1600 21

MW‐03 08/03/2001 740 <1 <1 740 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 940 1500 21

MW‐03 09/06/2001 540 <1 <1 540 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 4.9 930 1400 12

MW‐03 10/03/2001 580 <1 <1 580 ‐‐ 130 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 4.4 950 1400 9.2

MW‐03 11/08/2001 590 <1 <1 590 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 3.9 890 1400 6.4

Page 11 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐03 12/08/2001 710 <1 <1 710 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 4 900 1400 7.7

MW‐03 01/09/2002 590 <1 <1 590 ‐‐ 110 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 4.3 900 1400 5

MW‐03 02/07/2002 600 <1 <1 600 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.2 3.9 930 1500 7.6

MW‐03 03/08/2002 580 <1 <1 580 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.2 3.8 920 1500 7.3

MW‐03 04/03/2002 580 <1 <1 580 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 3.7 980 1500 9.4

MW‐03 05/09/2002 580 <1 <1 580 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 4.5 1000 1600 20

MW‐03 06/06/2002 550 <1 <1 550 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 5.2 1000 1600 22

MW‐03 07/03/2002 450 <1 <1 450 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 5.5 930 1500 38

MW‐03 08/08/2002 450 50 <1 500 ‐‐ 130 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 5.6 930 1400 11

MW‐03 09/06/2002 530 <1 <1 530 ‐‐ 110 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 5.6 850 1300 <0.5

MW‐03 10/10/2002 420 <1 <1 420 ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 6.9 1000 1700 12

MW‐03 11/08/2002 420 <1 <1 420 ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 6.7 990 1600 8.6

MW‐03 12/06/2002 460 <1 <1 460 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 5.5 930 1500 2.5

MW‐03 01/07/2003 490 <1 <1 490 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 5.4 850 1400 <0.5

MW‐03 02/05/2003 580 <1 <1 580 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 6.6 960 1500 0.7

MW‐03 03/06/2003 610 <1 <1 610 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 5.8 1100 1600 <0.5

MW‐03 04/03/2003 740 <1 <1 740 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8.2 1100 1800 <0.5

MW‐03 05/05/2003 800 <1 <1 800 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 10 1300 1900 <0.5

MW‐03 06/06/2003 840 <1 <1 840 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 13 1300 2000 <0.5

MW‐03 07/03/2003 840 <1 <1 840 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 12 1200 2000 <0.5

MW‐03 08/07/2003 790 <1 <1 790 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 12 1200 1900 <0.5

MW‐03 09/06/2003 640 <1 <1 640 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 12 940 1600 0.5

MW‐03 10/03/2003 500 <1 <1 500 ‐‐ 130 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 11 800 1300 8.7

MW‐03 11/05/2003 360 <1 <1 360 ‐‐ 110 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9 710 1100 26

MW‐03 12/04/2003 310 <1 <1 310 ‐‐ 97 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9.1 630 980 37

MW‐03 01/15/2004 350 <1 <1 350 ‐‐ 86 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9.4 740 950 38

MW‐03 02/06/2004 310 <1 <1 310 ‐‐ 94 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8 630 980 36

MW‐03 03/04/2004 400 <1 <1 400 ‐‐ 100 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8 720 1100 22

MW‐03 04/08/2004 520 <1 <1 520 ‐‐ 130 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9 830 1300 12

MW‐03 05/14/2004 650 <1 <1 650 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8 1000 1600 4.8

MW‐03 06/05/2004 700 <1 <1 700 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9 1000 1700 3.3

MW‐03 07/09/2004 780 <1 <1 780 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 15 1100 1800 2

MW‐03 08/07/2004 790 <1 <1 790 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 14 1100 1800 1

MW‐03 09/03/2004 610 <1 <1 610 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.5 12 970 1500 0.6

MW‐03 10/06/2004 510 <1 <1 510 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8 760 1300 5.6

Page 12 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐03 11/04/2004 500 <1 <1 500 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 14 890 1200 3.4

MW‐03 12/02/2004 610 <1 <1 610 ‐‐ 130 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 14 900 1500 0.8

MW‐03 01/14/2005 760 <1 <1 760 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 11 1100 1800 7.8

MW‐03 02/02/2005 770 <1 <1 770 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9 1100 1800 8.8

MW‐03 03/09/2005 830 <1 <1 830 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 7 1300 2000 7.6

MW‐03 04/07/2005 860 <1 <1 860 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 7 1300 2000 9.1

MW‐03 05/10/2005 820 <1 <1 820 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8 1300 2000 13

MW‐03 06/06/2005 790 <1 <1 790 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8.2 1300 2000 21

MW‐03 07/22/2005 750 <1 <1 750 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 12 1300 2000 36

MW‐03 08/04/2005 710 <1 <1 710 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 11 1400 2000 27

MW‐03 09/09/2005 860 <1 <1 860 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 10 1600 2100 15

MW‐03 10/06/2005 860 <1 <1 860 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 10 1300 2100 10

MW‐03 11/10/2005 850 <1 <1 850 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 12 1300 2100 13

MW‐03 12/08/2005 830 <1 <1 830 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 12 1400 2100 27

MW‐03 01/05/2006 820 <1 <1 820 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9 1500 2100 38

MW‐03 02/08/2006 850 <1 <1 850 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.3 75 1400 2100 38

MW‐03 03/15/2006 840 <1 <1 840 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 6.6 1400 2100 34

MW‐03 08/03/2006 550 <20 <20 550 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.6 1000 1600 55

MW‐03 09/05/2006 570 <10 <10 570 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.7 1000 1620 46

MW‐03 10/09/2006 700 <10 <10 700 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 1100 1700 27

MW‐03 11/06/2006 770 <10 <10 770 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 1200 1760 35

MW‐03 12/11/2006 730 <10 <10 730 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 1300 1930 62

MW‐03 01/03/2007 710 <10 <10 710 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.3 1200 1840 59

MW‐03 02/05/2007 690 <10 <10 690 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.8 1200 1770 60

MW‐03 03/05/2007 670 <10 <10 670 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7 1200 1730 62

MW‐03 04/05/2007 660 <10 <10 660 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.9 1100 1840 62

MW‐03 05/03/2007 650 <10 <10 650 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.9 1200 1760 61

MW‐03 06/07/2007 640 <10 <10 640 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 1100 1830 57

MW‐03 07/02/2007 630 <10 <10 630 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 10 1100 1780 57

MW‐03 08/02/2007 670 <10 <10 670 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11 1100 1770 50

MW‐03 09/10/2007 710 <10 <10 710 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 1200 1870 33

MW‐03 10/08/2007 780 <20 <20 780 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 1300 1980 33

MW‐03 11/07/2007 810 <10 <10 810 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 1400 2140 39

MW‐03 12/06/2007 820 <10 <10 820 ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 15 1400 2120 39

MW‐03 01/14/2008 820 <10 <10 820 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11 1400 2100 33

Page 13 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐03 02/07/2008 870 <10 <10 870 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.6 1400 2230 30

MW‐03 03/04/2008 840 <10 <10 840 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9 1400 2230 24

MW‐03 04/10/2008 860 <10 <10 860 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.8 1400 2260 26

MW‐03 05/05/2008 860 <10 <10 860 ‐‐ 270 130 0.74 27 15 29 320 ‐‐ ‐‐ ‐‐ 9.8 1400 2330 28

MW‐03 06/03/2008 900 <10 <10 900 ‐‐ 380 140 0.6 28 12 47 370 ‐‐ ‐‐ ‐‐ 13 1700 2560 33

MW‐03 07/01/2008 910 <10 <10 910 ‐‐ 390 140 0.6 27 13 51 380 ‐‐ ‐‐ ‐‐ 19 1600 2740 33

MW‐03 08/04/2008 920 <20 <20 920 ‐‐ 200 120 0.6 23 10 48 340 ‐‐ ‐‐ ‐‐ 19 1600 2710 14

MW‐03 09/08/2008 640 <10 <10 640 ‐‐ 410 130 0.73 25 12 53 400 ‐‐ ‐‐ ‐‐ 20 1600 2790 7.6

MW‐03 10/09/2008 900 <10 <10 900 ‐‐ 400 120 0.63 22 11 53 380 ‐‐ ‐‐ ‐‐ 21 1600 2780 8.4

MW‐03 11/04/2008 880 <20 <20 880 ‐‐ 400 120 0.66 23 11 55 400 ‐‐ ‐‐ ‐‐ 18 1500 2620 9.0

MW‐03 12/03/2008 870 <10 <10 870 ‐‐ 410 120 0.73 22 11 48 380 ‐‐ ‐‐ ‐‐ 17 1400 2570 12

MW‐03 01/13/2009 860 <8.2 <8.2 860 ‐‐ 410 140 0.74 27 15 44 410 ‐‐ ‐‐ ‐‐ 14 1700 2600 18

MW‐03 02/04/2009 860 <8.2 <8.2 860 ‐‐ 370 130 0.68 26 13 39 420 ‐‐ ‐‐ ‐‐ 12 1600 2560 21

MW‐03 03/04/2009 860 <8.2 <8.2 860 ‐‐ 400 130 0.68 25 13 38 400 ‐‐ ‐‐ ‐‐ 12 1600 2640 32

MW‐03 04/14/2009 840 <8.2 <8.2 840 ‐‐ 350 130 0.67 27 14 35 390 ‐‐ ‐‐ ‐‐ 11 1600 2510 51

MW‐03 05/04/2009 820 <8.2 <8.2 820 ‐‐ 390 130 0.63 26 13 36 400 ‐‐ ‐‐ ‐‐ 12 1500 2550 65

MW‐03 06/08/2009 810 <8.2 <8.2 810 ‐‐ 370 120 0.54 22 10 45 400 ‐‐ ‐‐ ‐‐ 14 1600 2590 93

MW‐03 07/13/2009 780 <8.2 <8.2 780 ‐‐ 350 110 0.54 21 8.5 53 430 ‐‐ ‐‐ ‐‐ 18 1700 2730 160

MW‐03 08/04/2009 790 <8.2 <8.2 790 ‐‐ 370 110 0.55 21 8.3 48 420 ‐‐ ‐‐ ‐‐ 18 1700 2690 160

MW‐03 09/08/2009 810 <16 <16 810 ‐‐ 360 110 0.58 20 8.0 52 420 ‐‐ ‐‐ ‐‐ 15 1500 2030 110

MW‐03 10/06/2009 800 <8.2 <8.2 800 ‐‐ 360 110 0.6 22 8.7 49 430 ‐‐ ‐‐ ‐‐ 14 1600 2580 91

MW‐03 11/10/2009 780 <8.2 <8.2 780 ‐‐ 340 110 0.55 22 11 39 400 ‐‐ ‐‐ ‐‐ 11 1600 2540 150

MW‐03 12/08/2009 780 <8.2 <8.2 780 ‐‐ 340 120 0.54 24 11 37 410 ‐‐ ‐‐ ‐‐ 11 1800 2620 180

MW‐03 01/05/2010 760 <4.1 <4.1 760 ‐‐ 360 130 0.59 26 13 39 440 ‐‐ ‐‐ ‐‐ 9.7 1700 2630 170

MW‐03 02/10/2010 790 <8.2 <8.2 30 ‐‐ 340 130 0.54 26 13 33 410 ‐‐ ‐‐ ‐‐ 10 1800 2590 170

MW‐03 03/08/2010 750 <8.2 <8.2 750 ‐‐ 360 120 0.53 25 13 30 390 ‐‐ ‐‐ ‐‐ 8.2 1600 2520 180

MW‐03 04/15/2010 740 <8.2 ‐‐ 740 ‐‐ 360 130 0.55 26 14 30 430 ‐‐ ‐‐ ‐‐ 7.2 1700 2420 170

MW‐03 07/08/2010 640 <8.2 ‐‐ 640 ‐‐ 320 99 0.47 21 12 24 340 ‐‐ ‐‐ ‐‐ 6.0 1400 2250 160

MW‐03 10/27/2010 500 <8.2 ‐‐ 500 ‐‐ 290 72 0.37 15 6.8 34 320 0.084 ‐‐ ‐‐ 8.1 1400 1980 140

MW‐03 01/19/2011 450 <8.2 ‐‐ 450 ‐‐ 270 74 0.28 16 7.6 24 330 ‐‐ ‐‐ ‐‐ 4.5 1400 1880 140

MW‐03 04/04/2011 460 <8.2 ‐‐ 460 ‐‐ 280 76 0.25 16 8.4 22 330 ‐‐ ‐‐ ‐‐ 4.8 1300 1980 150

MW‐03 07/07/2011 540 <8.2 ‐‐ 540 ‐‐ 310 89 0.26 18 9.1 28 340 ‐‐ ‐‐ <0.10 7.0 1400 2210 140

MW‐03 11/09/2011 452 <5.0 ‐‐ 452 0.54 257 70.2 J 9.27 J 12.4 J 5.04 J 46.8 286 J 0.065 ‐‐ <0.10 8.6 1100 1880 120

MW‐03 01/19/2012 450 ‐‐ ‐‐ 450 2.2 270 73 8.2 15 7.3 26 300 0.055 ‐‐ <0.20 Jo 7.4 1200 1930 120

MW‐03 04/03/2012 538 <5.0 ‐‐ 538 <2.0 261 86.9 8.65 17.1 9.45 26.3 295 0.069 ‐‐ <1.0 6.9 1240 1920 <128 U

Page 14 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐03 07/24/2012 434 <5.0 ‐‐ 434 0.61 202 80.6 9.05 15.3 J+ 7.99 33.9 246 0.056 ‐‐ <0.25 3.8 984 1680 103

MW‐03 10/15/2012 316 <5.0 ‐‐ 316 <0.50 144 46.0 J 6.6 8.55 J 3.45 J 35.5 J 192 J 0.041 ‐‐ <0.25 4.9 731 1260 72.2

MW‐03 01/22/2013 326 <5.0 ‐‐ 326 0.53 166 47.0 6.41 9.25 4.03 25.4 180 0.037 ‐‐ <0.25 4.8 739 1050 89.1

MW‐03 04/16/2013 325 <5.0 ‐‐ 325 0.57 193 53.6 6.1 10.3 5.98 18.8 203 0.055 ‐‐ <0.25 3.1 810 1270 78.9

MW‐03 07/17/2013 292 <5.0 ‐‐ 292 0.85 249 67.4 7.7 13.5 6.22 28.1 J 190 0.12 ‐‐ <0.25 5.4 855 1620 64.5

MW‐03 10/21/2013 270 <5.0 ‐‐ 270 ‐‐ 262 68.5 J 9.96 13.5 J 4.97 39.2 180 J ‐‐ ‐‐ <0.25 5.3 807 1530 53.5

MW‐03 01/22/2014 256 <5.0 ‐‐ 256 ‐‐ 280 67.9 11.2 13.8 4.66 35.8 170 ‐‐ ‐‐ <0.25 11.6 882 1520 59.5

MW‐03 04/22/2014 296 <5.0 ‐‐ 296 ‐‐ 247 81.2 3.83 17.0 J 5.76 38.0 J 218 J ‐‐ ‐‐ <0.25 <13.8 U 813 1490 60.2

MW‐03 10/20/2014 329 <5.0 ‐‐ 329 ‐‐ 231 58.9 8.54 13.9 4.66 25.8 197 ‐‐ ‐‐ <0.10 4.6 J 816 1320 34.7

MW‐03 04/15/2015 440 <5.0 ‐‐ 440 ‐‐ 179 66.8 J 10.7 J 16.0 J 4.97 J 24.0 J 212 J ‐‐ ‐‐ <0.25 4.5 896 1330 37.3

MW‐03 10/15/2015 277 <5.0 ‐‐ 277 ‐‐ 212 47.1 7.61 11.0 4.02 J 19.9 194 ‐‐ ‐‐ <0.10 3.1 794 1350 44.4

MW‐03 04/14/2016 240 <5.0 ‐‐ 240 ‐‐ 168 36.8 6.95 8.7 3.02 J 16.2 160 J ‐‐ ‐‐ <0.10 1.9 J+ 655 1130 44.6

MW‐03 10/12/2016 192 <5.0 ‐‐ 193 ‐‐ 190 37.7 6.73 9.2 2.78 16.5 J 170 ‐‐ ‐‐ <0.1 2.7 J‐ 612 1030 48

MW‐04 10/29/1990 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34.9 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 ‐‐ ‐‐ 600 ‐‐

MW‐04 01/08/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27.8 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 ‐‐ ‐‐ 620 ‐‐

MW‐04 04/18/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 ‐‐ ‐‐ 670 ‐‐

MW‐04 07/26/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 ‐‐ ‐‐ 560 ‐‐

MW‐04 10/23/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 83 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 ‐‐ ‐‐ 540 ‐‐

MW‐04 01/24/1992 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 50 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 ‐‐ ‐‐ 620 ‐‐

MW‐04 04/02/1992 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 18 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 ‐‐ ‐‐ 467 ‐‐

MW‐04 07/09/1992 128.8 <1 <1 128.8 ‐‐ 75 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 18 ‐‐ 181.7 360 19.4

MW‐04 10/06/1992 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 141.1 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.5 ‐‐ ‐‐ 1053 ‐‐

MW‐04 01/13/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 266.8 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 ‐‐ ‐‐ 1859 ‐‐

MW‐04 04/15/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 416.2 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.6 ‐‐ ‐‐ 3080 ‐‐

MW‐04 07/14/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 253 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ ‐‐ 2850 ‐‐

MW‐04 10/11/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 297.3 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ ‐‐ 2270 ‐‐

MW‐04 01/18/1994 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 252 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ ‐‐ 2470 ‐‐

MW‐04 04/19/1994 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ ‐‐ 2350 ‐‐

MW‐04 07/18/1994 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ ‐‐ 2300 ‐‐

MW‐04 11/14/1994 946 <1 <1 946 ‐‐ 310 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ 1466 2430 56

MW‐04 02/20/1995 1147.5 <1 <1 1147.5 ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ 1750 2770 10

MW‐04 05/11/1995 1014 <1 <1 1014 ‐‐ 226.4 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ 1550 2530 277

MW‐04 06/19/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.5 1700 2400 ‐‐

MW‐04 07/11/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 1600 2500 ‐‐

MW‐04 08/15/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.1 1500 2400 ‐‐

Page 15 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐04 11/14/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 1600 2400 ‐‐

MW‐04 02/14/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 5.5 1400 2400 ‐‐

MW‐04 05/21/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 410 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 1500 2400 ‐‐

MW‐04 08/20/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 1500 2400 ‐‐

MW‐04 11/19/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.77 1.7 1100 1800 ‐‐

MW‐04 02/18/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 1500 2300 ‐‐

MW‐04 05/20/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.7 1600 2400 ‐‐

MW‐04 08/25/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.3 1400 2300 ‐‐

MW‐04 11/20/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.8 1300 1900 ‐‐

MW‐04 02/26/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 130 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.6 1100 1500 ‐‐

MW‐04 05/19/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 3.2 1100 1800 ‐‐

MW‐04 08/20/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 31 1100 1800 ‐‐

MW‐04 11/24/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 27 1200 2000 ‐‐

MW‐04 02/15/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 19 1200 1900 ‐‐

MW‐04 05/24/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 22 1100 1800 ‐‐

MW‐04 08/20/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 30 1100 1900 ‐‐

MW‐04 11/22/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.18 24 1100 1800 ‐‐

MW‐04 02/11/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 18 970 1700 ‐‐

MW‐04 05/02/2000 640 <1 <1 640 ‐‐ 110 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 21 870 1500 1.2

MW‐04 08/09/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 21 1000 1800 ‐‐

MW‐04 09/21/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 21 1400 2300 ‐‐

MW‐04 11/28/2000 880 <1 <1 880 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 23 1300 2300 ‐‐

MW‐04 12/15/2000 790 <1 <1 790 ‐‐ 310 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 18 1400 2300 ‐‐

MW‐04 01/05/2001 710 <1 <1 710 ‐‐ 390 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 14 1400 2400 ‐‐

MW‐04 02/02/2001 620 <1 <1 620 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ 1300 1800 24

MW‐04 03/18/2001 530 <1 <1 530 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8.5 990 1500 46

MW‐04 04/17/2001 550 <1 <1 550 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8.8 1000 1700 17

MW‐04 05/22/2001 610 <1 <1 610 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 18 1100 1700 16

MW‐04 06/25/2001 780 <1 <1 780 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 10 1200 2000 6

MW‐04 07/17/2001 790 <1 <1 790 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 13 1200 2000 4.8

MW‐04 08/03/2001 790 <1 <1 790 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 20 1200 2000 4.2

MW‐04 09/06/2001 800 <1 <1 800 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 16 1200 1900 3.6

MW‐04 10/02/2001 810 <1 <1 810 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 16 1100 1800 3.5

MW‐04 11/08/2001 730 <1 <1 730 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 12 1200 1900 4.4

MW‐04 12/03/2001 750 <1 <1 750 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 12 1100 1900 3.3

Page 16 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐04 01/08/2002 740 <1 <1 740 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 16 1100 1800 1.4

MW‐04 02/05/2002 720 <1 <1 720 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 11 1100 1800 1.9

MW‐04 03/04/2002 720 <1 <1 720 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 11 1200 1900 2.1

MW‐04 04/02/2002 740 <1 <1 740 ‐‐ 88 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9.6 1200 2000 1.9

MW‐04 05/07/2002 740 <1 <1 740 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 11 1200 1900 1.5

MW‐04 06/04/2002 750 <1 <1 750 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.5 1900 1900 1.2

MW‐04 07/02/2002 760 <1 <1 760 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8.3 1300 2000 1.7

MW‐04 08/06/2002 750 <1 <1 750 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8.5 1300 2000 6.3

MW‐04 09/03/2002 740 <1 <1 740 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 11 1200 1900 1.8

MW‐04 10/08/2002 740 <1 <1 740 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9.5 1200 1800 <0.5

MW‐04 11/05/2002 730 <1 <1 730 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9 1200 1800 1.2

MW‐04 12/06/2002 750 <1 <1 750 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 11 1200 1800 <0.5

MW‐04 01/06/2003 650 <1 <1 650 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 13 1100 1700 <0.5

MW‐04 02/05/2003 500 <1 <1 500 ‐‐ 130 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8.6 890 1300 9.8

MW‐04 03/04/2003 390 <1 <1 390 ‐‐ 110 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.2 7.3 870 1200 53

MW‐04 04/01/2003 480 <1 <1 480 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 10 1000 1600 21

MW‐04 05/01/2003 310 <1 <1 310 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.2 8.2 810 1300 46

MW‐04 06/03/2003 430 <1 <1 430 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 6.5 920 1400 38

MW‐04 07/01/2003 550 <1 <1 550 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8.9 1000 1400 15

MW‐04 08/05/2003 600 <1 <1 600 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 10 1000 1700 6.2

MW‐04 09/05/2003 610 <1 <1 610 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 11 990 1700 11

MW‐04 10/03/2003 570 <1 <1 570 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9.4 1000 1600 29

MW‐04 11/04/2003 540 <1 <1 540 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 8.8 1100 1600 29

MW‐04 12/03/2003 540 <1 <1 540 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 7.1 1000 1600 30

MW‐04 01/14/2004 560 <1 <1 560 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9.1 950 1700 25

MW‐04 02/05/2004 500 <1 <1 500 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 9 940 1500 36

MW‐04 03/02/2004 600 <1 <1 600 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 10 1000 1700 11

MW‐04 04/07/2004 610 <1 <1 610 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 10 1100 1700 5.7

MW‐04 05/12/2004 200 <1 <1 200 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 11 990 1700 2.7

MW‐04 06/03/2004 620 <1 <1 620 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 12 990 1600 1.7

MW‐04 07/07/2004 620 <1 <1 620 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 11 1000 1600 3.5

MW‐04 09/07/2004 390 <1 <1 390 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 7 810 1200 36

MW‐04 10/06/2004 440 <1 <1 440 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 13 790 1300 16

MW‐04 11/04/2004 600 <1 <1 600 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 12 1000 1500 3

MW‐04 12/02/2004 530 <1 <1 530 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9 870 1300 2.3

Page 17 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐04 01/14/2005 350 <1 <1 350 ‐‐ 98 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 6 680 980 19

MW‐04 02/02/2005 350 <1 <1 350 ‐‐ 110 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 7 710 1100 17

MW‐04 03/09/2005 320 <1 <1 320 ‐‐ 110 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9 730 1000 29

MW‐04 04/07/2005 570 <1 <1 570 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 17 980 1700 6.4

MW‐04 05/10/2005 570 <1 <1 570 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 17 1100 1800 5.4

MW‐04 06/06/2005 600 <1 <1 600 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 17 1000 1700 3.6

MW‐04 07/22/2005 530 <1 <1 530 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 11 930 1500 7.9

MW‐04 08/08/2005 560 <1 <1 560 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 12 990 1500 4.7

MW‐04 09/09/2005 620 <1 <1 620 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 12 1000 1600 4.4

MW‐04 10/05/2005 670 <1 <1 670 ‐‐ 320 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 16 1300 2100 2.9

MW‐04 11/09/2005 640 <1 <1 640 ‐‐ 320 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 17 1400 2200 3.6

MW‐04 12/07/2005 660 <1 <1 660 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 17 1400 2200 2.9

MW‐04 01/06/2006 660 <1 <1 660 ‐‐ 380 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 17 1400 2200 2

MW‐04 02/06/2006 670 <1 <1 670 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.3 17 1300 2200 2.9

MW‐04 03/15/2006 640 <1 <1 640 ‐‐ 330 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 17 1300 2200 3.5

MW‐04 08/03/2006 810 <20 <20 810 ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 1400 2240 1.4

MW‐04 09/05/2006 880 <10 <10 880 ‐‐ 320 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 1500 2410 <1.0 Jo

MW‐04 10/09/2006 930 <10 <10 930 ‐‐ 330 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 1500 2500 1.0

MW‐04 11/06/2006 910 <10 <10 910 ‐‐ 360 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 1500 2380 2.5

MW‐04 12/11/2006 950 <10 <10 950 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 1600 2550 1.0

MW‐04 01/03/2007 950 <10 <10 950 ‐‐ 310 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 20 1500 2410 9.1

MW‐04 02/05/2007 930 <10 <10 930 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 1500 2460 <1

MW‐04 03/05/2007 950 <10 <10 950 ‐‐ 360 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 1600 2550 <1

MW‐04 04/05/2007 920 <10 <10 920 ‐‐ 380 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 50 1300 2650 <1

MW‐04 05/03/2007 960 <10 <10 960 ‐‐ 350 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 18 1600 2590 <1

MW‐04 06/07/2007 930 <10 <10 930 ‐‐ 380 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 1600 2740 <1

MW‐04 07/02/2007 930 <10 <10 930 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 1400 2560 <1

MW‐04 08/02/2007 860 <10 <10 860 ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 1300 2180 8

MW‐04 09/10/2007 750 <10 <10 750 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 15 1100 1920 8.7

MW‐04 10/08/2007 940 <20 <20 940 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 1400 2250 <1

MW‐04 11/07/2007 960 <10 <10 960 ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 1500 2340 <1

MW‐04 12/06/2007 990 <10 <10 990 ‐‐ 320 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 14 1600 2440 <1

MW‐04 01/14/2008 940 <10 <10 940 ‐‐ 440 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 1800 2520 2.4

MW‐04 02/07/2008 890 <10 <10 890 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 41 1600 2570 2.2

MW‐04 03/04/2008 690 <10 <10 690 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 15 1300 2210 19

Page 18 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐04 04/10/2008 610 <10 <10 610 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 15 1100 1930 35

MW‐04 05/05/2008 620 <10 <10 620 ‐‐ 330 100 0.19 22 3.9 51 270 ‐‐ ‐‐ ‐‐ 13 1200 2170 26

MW‐04 06/03/2008 790 <10 <10 790 ‐‐ 400 120 0.52 25 3.9 59 310 ‐‐ ‐‐ ‐‐ 15 1500 2400 7.3

MW‐04 07/01/2008 860 <10 <10 860 ‐‐ 390 130 2.3 28 4.6 60 350 ‐‐ ‐‐ ‐‐ 17 1500 2600 7.8

MW‐04 08/04/2008 890 <10 <10 890 ‐‐ 190 120 0.38 24 3.8 59 320 ‐‐ ‐‐ ‐‐ 17 1600 2600 1.1

MW‐04 09/08/2008 670 <10 <10 670 ‐‐ 280 97 0.26 22 3.2 52 280 ‐‐ ‐‐ ‐‐ 16 1200 2060 31

MW‐04 10/09/2008 790 <10 <10 790 ‐‐ 290 100 0.25 23 3.8 55 300 ‐‐ ‐‐ ‐‐ 16 1300 2250 6.3

MW‐04 11/04/2008 780 <10 <10 780 ‐‐ 240 96 0.21 21 2.6 62 310 ‐‐ ‐‐ ‐‐ 16 1200 2070 6.7

MW‐04 12/03/2008 760 <10 <10 760 ‐‐ 310 97 0.25 24 3.5 52 290 ‐‐ ‐‐ ‐‐ 14 1100 2130 16

MW‐04 01/13/2009 690 <8.2 <8.2 690 ‐‐ 330 110 0.39 26 4.1 55 290 ‐‐ ‐‐ ‐‐ 14 1300 2140 20

MW‐04 02/04/2009 650 <8.2 <8.2 650 ‐‐ 320 100 0.17 23 3.0 65 260 ‐‐ ‐‐ ‐‐ 15 1200 2090 20

MW‐04 03/04/2009 680 <8.2 <8.2 680 ‐‐ 330 110 0.47 27 3.6 66 280 ‐‐ ‐‐ ‐‐ 12 1300 2160 19

MW‐04 04/13/2009 660 <8.2 <8.2 660 ‐‐ 300 110 0.94 25 3.5 77 280 ‐‐ ‐‐ ‐‐ 30 1300 2080 12

MW‐04 05/04/2009 670 <8.2 <8.2 670 ‐‐ 350 120 0.23 27 3.5 73 270 ‐‐ ‐‐ ‐‐ 12 1200 2080 16

MW‐04 06/09/2009 650 <8.2 <8.2 650 ‐‐ 330 110 0.54 26 3 81 250 ‐‐ ‐‐ ‐‐ 10 1200 2060 18

MW‐04 07/13/2009 540 <8.2 <8.2 540 ‐‐ 270 87 0.16 23 2.7 61 240 ‐‐ ‐‐ ‐‐ 8.2 1100 1780 25

MW‐04 08/04/2009 490 <8.2 <8.2 490 ‐‐ 230 79 0.16 22 2.4 41 210 ‐‐ ‐‐ ‐‐ 6.6 960 1590 20

MW‐04 09/08/2009 470 <8.2 <8.2 470 ‐‐ 230 82 0.18 24 2.5 52 220 ‐‐ ‐‐ ‐‐ 5.7 940 1630 25

MW‐04 10/06/2009 420 <8.2 <8.2 420 ‐‐ 210 69 1.8 20 2.1 46 190 ‐‐ ‐‐ ‐‐ 6.3 880 1430 26

MW‐04 11/09/2009 400 <8.2 <8.2 400 ‐‐ 200 64 0.16 19 1.8 46 170 ‐‐ ‐‐ ‐‐ 6.5 950 1360 24

MW‐04 12/08/2009 480 <8.2 <8.2 480 ‐‐ 240 81 0.13 24 2.3 49 200 ‐‐ ‐‐ ‐‐ 7.3 980 1630 25

MW‐04 01/05/2010 440 <4.1 <4.1 440 ‐‐ 230 77 0.13 23 2.2 57 190 ‐‐ ‐‐ ‐‐ 9.3 960 1570 29

MW‐04 02/10/2010 450 <8.2 <8.2 450 ‐‐ 230 74 0.12 22 1.9 57 200 ‐‐ ‐‐ ‐‐ 15 920 1550 29

MW‐04 03/08/2010 440 <8.2 <8.2 440 ‐‐ 240 69 0.12 20 1.8 54 180 ‐‐ ‐‐ ‐‐ 16 920 1610 30

MW‐04 04/15/2010 450 <8.2 ‐‐ 450 ‐‐ 280 77 0.11 20 2 60 200 ‐‐ ‐‐ ‐‐ 27 860 1640 32

MW‐04 07/08/2010 420 <8.2 ‐‐ 420 ‐‐ 260 65 0.11 16 1.8 54 180 ‐‐ ‐‐ ‐‐ 31 880 1630 37

MW‐04 10/27/2010 420 <8.2 ‐‐ 420 ‐‐ 250 58 0.081 15 1.5 43 210 0.19 ‐‐ ‐‐ 37 960 1690 60

MW‐04 01/19/2011 550 <8.2 ‐‐ 550 ‐‐ 280 81 <0.05 Jo 19 2 51 230 ‐‐ ‐‐ ‐‐ 50 1000 1950 35

MW‐04 04/04/2011 460 <8.2 ‐‐ 460 ‐‐ 240 52 0.26 12 1.4 38 210 ‐‐ ‐‐ ‐‐ 50 860 1690 29

MW‐04 07/07/2011 500 <8.2 ‐‐ 500 ‐‐ 240 58 0.56 13 1.7 40 220 ‐‐ ‐‐ <0.10 50 880 1700 12

MW‐04 10/04/2011 340 <8.2 ‐‐ 340 ‐‐ 200 42 0.18 10 1.3 27 180 ‐‐ ‐‐ <0.20 26 760 1380 56

MW‐04 01/18/2012 380 <8.2 ‐‐ 380 ‐‐ 250 58 0.24 15 1.8 33 200 ‐‐ ‐‐ 1.5 32 860 1590 36

MW‐04 04/04/2012 410 <8.2 ‐‐ 410 ‐‐ 250 64 0.15 16 1.8 35 180 ‐‐ ‐‐ <0.20 Jo 26 860 1560 14

MW‐04 07/23/2012 450 <8.2 ‐‐ 450 ‐‐ 240 65 0.17 17 2 33 200 ‐‐ ‐‐ <0.20 Jo 25 890 1650 17

MW‐04 10/15/2012 320 <8.2 ‐‐ 320 ‐‐ 170 43 0.53 11 1.3 26 170 ‐‐ ‐‐ <0.10 23 720 1260 63

Page 19 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐04 01/22/2013 450 <8.2 ‐‐ 450 ‐‐ 290 79 0.21 20 2.8 33 210 ‐‐ ‐‐ <0.20 24 980 1750 27

MW‐04 04/17/2013 470 <8.2 ‐‐ 470 ‐‐ 280 78 0.19 20 3 32 200 ‐‐ ‐‐ <0.20 Jo 31 950 1700 43

MW‐04 07/17/2013 360 <8.2 ‐‐ 360 ‐‐ 200 61 0.11 16 2.2 27 170 ‐‐ ‐‐ 5.8 22 790 1420 32

MW‐04 10/21/2013 340 <8.2 ‐‐ 340 ‐‐ 210 60 0.15 16 2.1 27 150 ‐‐ ‐‐ 3.9 17 760 1360 30

MW‐04 01/22/2014 280 <8.2 ‐‐ 280 ‐‐ 180 57 0.67 15 1.9 25 140 ‐‐ ‐‐ <0.20 Jo 12 690 1150 38

MW‐04 04/22/2014 310 <8.2 ‐‐ 310 ‐‐ 170 74 0.69 20 2.3 29 170 ‐‐ ‐‐ 6.0 11 730 1290 30

MW‐04 07/21/2014 330 <8.2 ‐‐ 330 ‐‐ 180 63 0.068 18 2.1 24 170 ‐‐ ‐‐ 3.0 12 790 1350 30

MW‐04 10/20/2014 270 <8.2 ‐‐ 270 ‐‐ 160 66 <0.05 19 2 25 140 ‐‐ ‐‐ 13 11 620 1220 39

MW‐04 01/21/2015 270 <8.2 ‐‐ 270 ‐‐ 150 56 <0.05 Jo 16 1.6 22 130 ‐‐ ‐‐ 11 8.7 720 1150 37

MW‐04 04/15/2015 260 <8.2 ‐‐ 260 ‐‐ 120 59 0.082 16 1.5 26 140 ‐‐ ‐‐ 12 7.0 660 1030 34

MW‐04 07/22/2015 250 <8.2 ‐‐ 250 ‐‐ 110 45 0.05 13 1.2 23 130 ‐‐ ‐‐ 9.0 6.9 600 1020 34

MW‐04 10/15/2015 200 <4.1 ‐‐ 200 ‐‐ 90 29 <0.05 Jo 8.5 0.82 21 100 ‐‐ ‐‐ 5.4 7.9 600 773 33

MW‐04 01/20/2016 200 <4.1 ‐‐ 200 ‐‐ 84 30 0.1 8.5 0.86 20 99 ‐‐ ‐‐ 6.2 5.5 500 776 30

MW‐04 04/14/2016 200 <4.1 ‐‐ 200 ‐‐ 84 35 <0.05 9.5 0.91 26 110 ‐‐ ‐‐ 6.8 5.3 500 752 33

MW‐04 07/18/2016 180 <4.1 ‐‐ 180 ‐‐ 62 27 <0.05 6.9 0.67 24 85 ‐‐ ‐‐ 11 5.1 460 697 25

MW‐04 10/12/2016 140 <4.1 ‐‐ 140 ‐‐ 51 22 <0.05 5.7 0.55 27 81 ‐‐ ‐‐ 9.1 1.5 400 594 28

MW‐05 10/29/1990 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 74.7 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 ‐‐ ‐‐ 1180 ‐‐

MW‐05 01/08/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 78.8 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 39 ‐‐ ‐‐ 1330 ‐‐

MW‐05 04/18/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 72 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 50 ‐‐ ‐‐ 1200 ‐‐

MW‐05 07/26/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 42 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 49 ‐‐ ‐‐ 990 ‐‐

MW‐05 10/23/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 45 ‐‐ ‐‐ 1320 ‐‐

MW‐05 01/24/1992 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 151 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 41 ‐‐ ‐‐ 1370 ‐‐

MW‐05 04/02/1992 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 181 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 40 ‐‐ ‐‐ 1580 ‐‐

MW‐05 07/09/1992 288 <1 <1 288 ‐‐ 165 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 ‐‐ 726.4 1309 48.3

MW‐05 10/06/1992 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 232.1 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 23 ‐‐ ‐‐ 1631 ‐‐

MW‐05 01/13/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 258.5 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 ‐‐ ‐‐ 2290 ‐‐

MW‐05 04/15/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 321.7 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1 ‐‐ ‐‐ 2790 ‐‐

MW‐05 07/14/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 166.5 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ ‐‐ 1828 ‐‐

MW‐05 10/11/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 250.6 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.56 ‐‐ ‐‐ 2250 ‐‐

MW‐05 01/18/1994 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ ‐‐ 2250 ‐‐

MW‐05 04/19/1994 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.84 ‐‐ ‐‐ 2250 ‐‐

MW‐05 07/18/1994 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.99 ‐‐ ‐‐ 1800 ‐‐

MW‐05 11/14/1994 758 <1 <1 758 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.23 ‐‐ 1220 2040 19

MW‐05 02/20/1995 841.5 <1 <1 841.5 ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.14 ‐‐ 1460 2290 29

MW‐05 05/11/1995 910 <1 <1 910 ‐‐ 247.6 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ 1558 2520 27.5

Page 20 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐05 06/19/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 310 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 1600 2400 ‐‐

MW‐05 07/11/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.7 1500 2200 ‐‐

MW‐05 08/15/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.11 10 1700 2600 ‐‐

MW‐05 11/14/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 3 1700 2500 ‐‐

MW‐05 02/14/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 3.3 1800 2600 ‐‐

MW‐05 05/21/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 1600 2500 ‐‐

MW‐05 08/20/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 3.1 1600 2400 ‐‐

MW‐05 11/19/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 6.3 1500 2400 ‐‐

MW‐05 02/18/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 4.1 1600 2400 ‐‐

MW‐05 05/20/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 7.2 1700 2600 ‐‐

MW‐05 08/25/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 7.7 1400 2300 ‐‐

MW‐05 11/20/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8.6 1400 2300 ‐‐

MW‐05 02/26/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9.4 1300 2000 ‐‐

MW‐05 05/19/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 12 1200 2000 ‐‐

MW‐05 08/20/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 18 1100 1800 ‐‐

MW‐05 11/24/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 19 1100 1900 ‐‐

MW‐05 02/15/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 130 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8.2 1200 1900 ‐‐

MW‐05 05/24/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 12 1300 1900 ‐‐

MW‐05 08/20/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 5.7 1300 2100 ‐‐

MW‐05 11/22/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 20 1200 2000 ‐‐

MW‐05 02/11/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 24 1400 2300 ‐‐

MW‐05 05/02/2000 960 <1 <1 960 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 31 1300 2200 1.6

MW‐05 08/10/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 26 1400 2300 ‐‐

MW‐05 09/21/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 27 1400 2300 ‐‐

MW‐05 11/28/2000 1000 <1 <1 1000 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 22 1400 2300 ‐‐

MW‐05 12/14/2000 1000 <1 <1 1000 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 23 1400 2200 ‐‐

MW‐05 01/05/2001 970 <1 <1 970 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 22 1300 2200 ‐‐

MW‐05 02/01/2001 960 <1 <1 960 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ 1500 2300 <0.5

MW‐05 03/18/2001 1200 <1 <1 1200 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 21 1700 2700 1.3

MW‐05 04/17/2001 1100 <1 <1 1100 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 46 1500 2500 <0.5

MW‐05 05/22/2001 1100 <1 <1 1100 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 26.7 1500 2500 <0.5

MW‐05 06/25/2001 1100 <1 <1 1100 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 18 1100 2400 0.6

MW‐05 07/17/2001 1000 <1 <1 1000 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 20 1400 2400 0.7

MW‐05 08/03/2001 1000 <1 <1 1000 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 15 1400 2300 0.7

MW‐05 09/05/2001 1000 <1 <1 1000 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 22 1500 2300 <0.5

Page 21 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐05 10/02/2001 1000 <1 <1 1000 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 26 1500 2300 <0.5

MW‐05 11/08/2001 1100 <1 <1 1100 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 21 1500 2400 <0.5

MW‐05 12/05/2001 1000 <1 <1 1000 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 28 1500 2500 <0.5

MW‐05 01/04/2002 1100 <1 <1 1100 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 23 1600 2600 0.9

MW‐05 02/07/2002 1100 <1 <1 1100 ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.2 27 1600 2700 <0.5

MW‐05 03/08/2002 1100 <1 <1 1100 ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 30 1700 2800 <0.5

MW‐05 04/03/2002 1100 <1 <1 1100 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 28 1600 2700 <0.5

MW‐05 05/08/2002 1100 <1 <1 1100 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 28 1800 3000 1.1

MW‐05 06/05/2002 1200 <1 <1 1200 ‐‐ 410 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 28 2000 3300 3.7

MW‐05 07/03/2002 1200 <1 <1 1200 ‐‐ 460 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 26 2000 3400 1.5

MW‐05 08/06/2002 1200 <1 <1 1200 ‐‐ 420 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1 33 2100 3600 130

MW‐05 09/05/2002 1200 <1 <1 1200 ‐‐ 410 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 30 2200 3400 110

MW‐05 10/09/2002 980 <1 <1 980 ‐‐ 440 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 31 2400 3700 340

MW‐05 11/06/2002 880 <1 <1 880 ‐‐ 370 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 23 2000 3000 290

MW‐05 12/06/2002 1000 <1 <1 1000 ‐‐ 350 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 19 1800 2800 54

MW‐05 01/07/2003 1100 <1 <1 1100 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 20 1800 2900 35

MW‐05 02/05/2003 1100 <1 <1 1100 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 29 1800 2800 85

MW‐05 03/06/2003 920 <1 <1 920 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 25 1500 2300 48

MW‐05 04/03/2003 1000 <1 <1 1000 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 31 1500 2400 31

MW‐05 05/05/2003 1000 <1 <1 1000 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 43 1400 2400 16

MW‐05 06/05/2003 1000 <1 <1 1000 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 42 1500 2600 18

MW‐05 07/02/2003 1000 <1 <1 1000 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 30 1500 2500 17

MW‐05 08/07/2003 1000 <1 <1 1000 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 26 1500 2500 15

MW‐05 09/05/2003 1000 <1 <1 1000 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 27 1600 2500 14

MW‐05 10/03/2003 1000 <1 <1 1000 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 30 1500 2500 1.8

MW‐05 11/05/2003 1000 <1 <1 1000 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 25 1500 2500 7.1

MW‐05 12/03/2003 1000 <1 <1 1000 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 26 1600 2500 5.2

MW‐05 01/15/2004 1100 <1 <1 1100 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 31 1800 2700 21

MW‐05 02/05/2004 1100 <1 <1 1100 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 28 1600 2700 20

MW‐05 03/03/2004 1200 <1 <1 1200 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 30 1700 2700 17

MW‐05 04/07/2004 1000 <1 <1 1000 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 22 1600 2500 13

MW‐05 05/13/2004 1000 <1 <1 1000 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 22 1500 2500 14

MW‐05 06/05/2004 1000 <1 <1 1000 ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 21 1600 2600 8.1

MW‐05 07/09/2004 1100 <1 <1 1100 ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 22 1700 2700 7.3

MW‐05 08/07/2004 1100 <1 <1 1100 ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 23 1700 2800 5.9

Page 22 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐05 09/07/2004 1100 <1 <1 1100 ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 20 1700 2700 7.2

MW‐05 10/06/2004 1000 <1 <1 1000 ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 27 1600 2700 6.2

MW‐05 11/04/2004 1100 <1 <1 1100 ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 22 1700 2600 5.5

MW‐05 12/02/2004 1100 <1 <1 1100 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 20 1600 2600 4.7

MW‐05 01/14/2005 1000 <1 <1 1000 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 14 1500 2400 4.1

MW‐05 02/02/2005 960 <1 <1 960 ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 12 1600 2500 4.4

MW‐05 03/08/2005 910 <1 <1 910 ‐‐ 370 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 12 1600 2600 3.7

MW‐05 04/06/2005 850 <1 <1 850 ‐‐ 390 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 11 1600 2700 4.9

MW‐05 05/06/2005 710 <1 <1 710 ‐‐ 450 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 10 1600 2700 4.7

MW‐05 06/06/2005 720 <1 <1 720 ‐‐ 480 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 10 1700 2700 2

MW‐05 07/21/2005 820 <1 <1 820 ‐‐ 480 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9 1700 2900 2.4

MW‐05 08/04/2005 790 <1 <1 790 ‐‐ 470 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 12 1800 2900 2.4

MW‐05 09/09/2005 840 <1 <1 840 ‐‐ 470 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8 1800 2700 2.1

MW‐05 10/06/2005 810 <1 <1 810 ‐‐ 370 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8 1600 2600 2

MW‐05 11/09/2005 820 <1 <1 820 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 6 1600 2500 1.9

MW‐05 12/08/2005 840 <1 <1 840 ‐‐ 360 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 6.7 1600 2500 <0.5

MW‐05 01/05/2006 880 <1 <1 880 ‐‐ 380 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8 1700 2600 <0.5

MW‐05 02/08/2006 890 10 <1 890 ‐‐ 400 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.3 8.5 2000 2800 16

MW‐05 03/15/2006 940 <1 <1 940 ‐‐ 440 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 13 2100 3000 30

MW‐05 08/03/2006 1000 <20 <20 1000 ‐‐ 520 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 22 2100 3420 94

MW‐05 09/05/2006 1100 <10 <10 1100 ‐‐ 510 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 18 2200 3430 88

MW‐05 10/09/2006 1100 <20 <20 1100 ‐‐ 560 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 2200 3500 84

MW‐05 11/06/2006 1100 <20 <20 1100 ‐‐ 550 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 2400 3490 87

MW‐05 12/11/2006 1100 <20 <20 1100 ‐‐ 580 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 2300 3720 110

MW‐05 01/03/2007 1100 <10 <10 1100 ‐‐ 530 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 2200 3510 130

MW‐05 02/05/2007 1000 <10 <10 1000 ‐‐ 510 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 14 2200 3340 150

MW‐05 03/05/2007 1000 <10 <10 1000 ‐‐ 510 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 2300 3370 140

MW‐05 04/05/2007 1000 87 <10 1100 ‐‐ 510 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 2000 3470 130

MW‐05 05/03/2007 1000 <10 <10 1000 ‐‐ 500 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11 2200 3350 160

MW‐05 06/07/2007 1000 <10 <10 1000 ‐‐ 410 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 10 2000 3230 150

MW‐05 07/02/2007 990 <10 <10 990 ‐‐ 400 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.8 1900 3060 160

MW‐05 08/02/2007 990 <10 <10 990 ‐‐ 370 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.5 1900 3090 150

MW‐05 09/10/2007 1000 <10 <10 1000 ‐‐ 400 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.2 2000 3140 160

MW‐05 10/08/2007 1100 <20 <20 1100 ‐‐ 380 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.9 2100 3170 160

MW‐05 11/07/2007 1200 <20 <20 1200 ‐‐ 400 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.6 2200 3170 160

Page 23 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐05 12/06/2007 1000 <10 <10 1000 ‐‐ 380 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.5 2200 3080 240

MW‐05 01/14/2008 910 <10 <10 910 ‐‐ 390 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.5 2100 3050 310

MW‐05 02/07/2008 950 <10 <10 950 ‐‐ 400 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.6 2200 3360 340

MW‐05 03/04/2008 970 <10 <10 970 ‐‐ 410 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.8 2400 3500 340

MW‐05 04/10/2008 1100 <10 <10 1100 ‐‐ 460 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.2 2300 3550 250

MW‐05 05/05/2008 1100 <20 <20 1100 ‐‐ 440 91 0.91 23 2.1 140 610 ‐‐ ‐‐ ‐‐ 5.4 2300 3610 210

MW‐05 06/03/2008 1200 <20 <20 1200 ‐‐ 450 91 1.2 24 2.0 140 660 ‐‐ ‐‐ ‐‐ 5.0 2400 3580 190

MW‐05 07/01/2008 1200 <20 <20 1200 ‐‐ 470 88 1.3 23 2.5 130 650 ‐‐ ‐‐ ‐‐ 13 2400 3680 200

MW‐05 08/05/2008 1200 <20 <20 1200 ‐‐ 450 89 1.3 22 2.6 140 660 ‐‐ ‐‐ ‐‐ 4.9 2300 3730 230

MW‐05 09/08/2008 1000 <10 <10 1000 ‐‐ 420 88 0.93 22 2.7 120 600 ‐‐ ‐‐ ‐‐ 4.7 2100 3440 270

MW‐05 10/09/2008 950 <10 <10 950 ‐‐ 400 68 0.71 18 2.1 120 560 ‐‐ ‐‐ ‐‐ 4.0 2200 3300 250

MW‐05 11/04/2008 970 <10 <10 970 ‐‐ 400 68 0.72 18 2.2 130 550 ‐‐ ‐‐ ‐‐ 3.9 2100 3220 250

MW‐05 12/03/2008 990 <10 <10 990 ‐‐ 420 65 0.78 17 1.9 130 570 ‐‐ ‐‐ ‐‐ 3.7 2000 3200 270

MW‐05 01/13/2009 940 <8.2 <8.2 940 ‐‐ 390 73 0.78 19 2.3 130 590 ‐‐ ‐‐ ‐‐ 3.6 2000 3110 240

MW‐05 02/04/2009 950 <8.2 <8.2 950 ‐‐ 360 66 0.78 17 1.9 130 610 ‐‐ ‐‐ ‐‐ 3.6 2000 3070 240

MW‐05 03/04/2009 950 <8.2 <8.2 950 ‐‐ 390 68 0.77 16 1.8 120 570 ‐‐ ‐‐ ‐‐ 3.7 2000 3110 250

MW‐05 04/14/2009 960 <8.2 <8.2 960 ‐‐ 350 73 0.82 19 2.1 130 620 ‐‐ ‐‐ ‐‐ 3.8 2000 3040 220

MW‐05 05/04/2009 970 <8.2 <8.2 970 ‐‐ 390 83 0.74 22 2.4 100 570 ‐‐ ‐‐ ‐‐ 3.9 2000 3080 200

MW‐05 06/09/2009 1000 <8.2 <8.2 1000 ‐‐ 360 71 0.63 19 1.8 110 550 ‐‐ ‐‐ ‐‐ 3.4 2000 2930 200

MW‐05 07/14/2009 1000 <8.2 <8.2 1000 ‐‐ 330 79 0.66 22 2.2 110 580 ‐‐ ‐‐ ‐‐ 2.8 2000 3160 190

MW‐05 08/04/2009 1100 <8.2 <8.2 1100 ‐‐ 350 74 0.63 20 1.9 94 560 ‐‐ ‐‐ ‐‐ 2.7 2000 3130 190

MW‐05 09/08/2009 1100 <16 <16 1100 ‐‐ 330 62 0.6 18 1.5 130 600 ‐‐ ‐‐ ‐‐ 2.3 2000 3160 190

MW‐05 10/07/2009 1000 <8.2 <8.2 1000 ‐‐ 330 57 0.53 16 1.5 110 570 ‐‐ ‐‐ ‐‐ 2.4 2000 2940 210

MW‐05 11/10/2009 1000 <8.2 <8.2 1000 ‐‐ 330 61 0.53 17 1.5 120 550 ‐‐ ‐‐ ‐‐ 2.5 1800 3070 200

MW‐05 12/08/2009 1000 <8.2 <8.2 1000 ‐‐ 330 66 0.52 19 1.6 120 600 ‐‐ ‐‐ ‐‐ 2.3 2100 3110 210

MW‐05 01/05/2010 980 <4.1 <4.1 980 ‐‐ 350 67 0.53 19 1.6 130 590 ‐‐ ‐‐ ‐‐ 2.5 2100 3070 210

MW‐05 02/10/2010 1000 <8.2 <8.2 1000 ‐‐ 330 65 0.49 18 1.5 110 530 ‐‐ ‐‐ ‐‐ 1.8 2100 2890 210

MW‐05 03/08/2010 950 <8.2 <8.2 950 ‐‐ 340 69 0.46 19 1.8 110 490 ‐‐ ‐‐ ‐‐ 1.9 2000 2680 220

MW‐05 04/15/2010 850 <8.2 ‐‐ 850 ‐‐ 320 73 0.44 20 2.1 100 600 ‐‐ ‐‐ ‐‐ 2.1 1900 2830 280

MW‐05 07/08/2010 730 <8.2 ‐‐ 730 ‐‐ 270 60 0.29 18 1.7 65 410 ‐‐ ‐‐ ‐‐ 1.8 1600 2440 230

MW‐05 10/27/2010 520 <8.2 ‐‐ 520 ‐‐ 220 50 0.25 15 1.4 55 360 0.1 ‐‐ ‐‐ 1.6 1400 2020 230

MW‐05 01/19/2011 540 <8.2 ‐‐ 540 ‐‐ 230 46 0.19 14 1.1 55 360 ‐‐ ‐‐ ‐‐ 1.1 1600 2060 240

MW‐05 04/04/2011 470 <8.2 ‐‐ 470 ‐‐ 210 28 0.21 7.2 0.8 74 410 ‐‐ ‐‐ ‐‐ 1.4 1400 2080 280

MW‐05 07/07/2011 470 <8.2 ‐‐ 470 ‐‐ 170 38 0.14 12 1 42 320 ‐‐ ‐‐ <0.10 1.4 1200 1760 180

MW‐05 11/09/2011 356 <5.0 ‐‐ 356 0.22 99.9 16.3 J 1.72 J <5.0 0.367 J 54.9 233 J 0.056 ‐‐ <0.10 1.4 795 1270 125

Page 24 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐05 01/19/2012 340 ‐‐ ‐‐ 340 1.1 120 22 2.2 6.6 0.5 40 250 0.069 ‐‐ <0.10 1.4 890 1320 140

MW‐05 04/03/2012 296 <5.0 ‐‐ 296 <1.0 137 21.9 5.69 5.96 0.455 93.7 207 0.087 ‐‐ <0.50 2.6 888 1370 <160 U

MW‐05 07/24/2012 310 <5.0 ‐‐ 310 <0.50 115 28.7 10.7 7.23 J+ 0.775 147 189 0.17 ‐‐ <0.25 <1.0 U 878 1430 204

MW‐05 10/15/2012 316 <5.0 ‐‐ 316 <0.50 95.0 32.8 J 9.83 9.38 J 1.07 J 126 J 164 J 0.15 ‐‐ <0.25 1.5 800 1260 126

MW‐05 01/22/2013 312 <5.0 ‐‐ 312 <0.50 83.9 28.6 11.3 9.81 1.07 123 111 0.13 ‐‐ <0.25 1.3 660 937 110

MW‐05 04/16/2013 282 <5.0 ‐‐ 282 <1.0 105 28.1 11.0 8.7 0.953 116 135 0.11 ‐‐ <0.50 1.5 731 1100 111

MW‐05 07/17/2013 221 <5.0 ‐‐ 221 <0.50 99.8 26.9 10.4 8.07 0.86 130 J 92.0 0.058 ‐‐ 3.1 <1.9 U 592 1070 91.4

MW‐05 10/21/2013 232 <5.0 ‐‐ 232 ‐‐ 83.2 23.8 J 8.02 7.00 J 0.788 97.7 109 J ‐‐ ‐‐ <0.25 0.81 565 1010 86.5

MW‐05 01/22/2014 190 <5.0 ‐‐ 190 ‐‐ 51.1 18.6 7.67 5.7 0.692 80.9 70.6 ‐‐ ‐‐ 0.69 <3.6 U 461 746 72.9

MW‐05 04/22/2014 163 <5.0 ‐‐ 163 ‐‐ 83.1 33.4 5.46 9.82 J 1.4 96.0 J 74.9 J ‐‐ ‐‐ 6.9 <2.2 U 517 909 85.5

MW‐05 10/20/2014 186 <5.0 ‐‐ 186 ‐‐ 67.6 23.3 5.34 8.55 1.25 103 69.6 ‐‐ ‐‐ 3.8 0.46 504 833 78.8

MW‐05 04/15/2015 200 <5.0 ‐‐ 200 ‐‐ 65.0 28.0 J 9.19 J 9.69 J 1.32 J 110 J 80.1 J ‐‐ ‐‐ <0.10 <0.20 569 892 91.6

MW‐05 10/15/2015 208 <5.0 ‐‐ 208 ‐‐ 128 41.0 7.86 19.7 3.77 J 152 89.2 ‐‐ ‐‐ 19.1 <0.20 805 1280 109

MW‐05 04/14/2016 226 <5.0 ‐‐ 226 ‐‐ 110 38.8 6.19 14.9 2.34 J 127 80.5 J ‐‐ ‐‐ 2.8 0.89 J+ 668 1150 117

MW‐05 10/12/2016 173 <5.0 ‐‐ 174 ‐‐ 110 40.9 3.83 16.2 2.81 135 89.5 ‐‐ ‐‐ 19 <0.53 R 728 1120 110

MW‐06 10/29/1990 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12.2 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.5 ‐‐ ‐‐ 400 ‐‐

MW‐06 01/08/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11.5 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.9 ‐‐ ‐‐ 370 ‐‐

MW‐06 04/18/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 20 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 ‐‐ ‐‐ 450 ‐‐

MW‐06 07/26/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 ‐‐ ‐‐ 480 ‐‐

MW‐06 10/23/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.9 ‐‐ ‐‐ 400 ‐‐

MW‐06 01/24/1992 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 203 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 ‐‐ ‐‐ 1480 ‐‐

MW‐06 04/02/1992 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 216 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 ‐‐ ‐‐ 2250 ‐‐

MW‐06 07/09/1992 261.6 <1 <1 261.6 ‐‐ 49 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 10 ‐‐ 365.1 753 16.3

MW‐06 10/06/1992 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.6 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.8 ‐‐ ‐‐ 192 ‐‐

MW‐06 01/13/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38.8 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 10 ‐‐ ‐‐ 602 ‐‐

MW‐06 04/15/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 236.6 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5 ‐‐ ‐‐ 2310 ‐‐

MW‐06 07/14/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 40.3 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.1 ‐‐ ‐‐ 656 ‐‐

MW‐06 10/11/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 40.2 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6 ‐‐ ‐‐ 583 ‐‐

MW‐06 01/18/1994 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 234.8 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ ‐‐ 2390 ‐‐

MW‐06 04/19/1994 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ ‐‐ 2280 ‐‐

MW‐06 07/18/1994 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.6 ‐‐ ‐‐ 1900 ‐‐

MW‐06 11/14/1994 758 <1 <1 758 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.43 ‐‐ 998 1905 13

MW‐06 02/20/1995 994.5 <1 <1 994.5 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ 1282 2350 9.5

MW‐06 05/11/1995 884 <1 <1 884 ‐‐ 183.6 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.5 ‐‐ 1292 2180 10

MW‐06 06/19/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2 2.3 1200 1700 ‐‐

Page 25 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐06 07/11/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.4 <1.1 460 650 ‐‐

MW‐06 08/15/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.2 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.6 <1.1 140 240 ‐‐

MW‐06 11/14/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 20 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 290 430 ‐‐

MW‐06 02/14/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.1 1200 1800 ‐‐

MW‐06 05/21/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.5 <1.1 240 360 ‐‐

MW‐06 08/20/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.9 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.8 <1.1 170 220 ‐‐

MW‐06 11/19/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.1 1000 1700 ‐‐

MW‐06 02/18/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.27 <1.1 1200 2000 ‐‐

MW‐06 05/20/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 70 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.14 <1.1 770 1200 ‐‐

MW‐06 08/25/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 75 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.4 810 1500 ‐‐

MW‐06 11/20/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.9 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 1100 240 ‐‐

MW‐06 02/26/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 430 610 ‐‐

MW‐06 05/19/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 73 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.1 810 1300 ‐‐

MW‐06 08/20/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 91 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 1100 1600 ‐‐

MW‐06 11/24/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 99 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 1300 2000 ‐‐

MW‐06 02/15/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 1600 2300 ‐‐

MW‐06 05/24/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.9 1400 2200 ‐‐

MW‐06 08/20/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.6 1500 2200 ‐‐

MW‐06 11/22/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.3 1200 1800 ‐‐

MW‐06 02/11/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 1700 2700 ‐‐

MW‐06 05/02/2000 1200 <1 <1 1200 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.1 1300 2600 17

MW‐06 08/10/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 1600 2500 ‐‐

MW‐06 09/21/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.4 1700 2600 ‐‐

MW‐06 11/28/2000 1200 <1 <1 1200 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 6.8 1700 2700 ‐‐

MW‐06 12/14/2000 1200 <1 <1 1200 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 34 1700 2500 ‐‐

MW‐06 01/05/2001 720 <1 <1 720 ‐‐ 380 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.2 1600 2400 ‐‐

MW‐06 02/06/2001 1300 <1 <1 1300 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ 1600 2700 21

MW‐06 03/18/2001 1200 <1 <1 1200 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 3.4 1700 2500 26

MW‐06 04/17/2001 1200 <1 <1 1200 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.1 1600 2500 28

MW‐06 05/22/2001 1300 <1 <1 1300 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.3 1800 2700 4.1

MW‐06 06/22/2001 1200 <1 <1 1200 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 1800 2700 2.3

MW‐06 07/17/2001 1400 <1 <1 1400 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.3 1600 2600 2

MW‐06 08/02/2001 1100 <1 <1 1100 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 3.4 1800 2600 2.4

MW‐06 09/05/2001 1300 <1 <1 1300 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.3 1800 2500 <0.5

MW‐06 10/03/2001 1200 <1 <1 1200 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 4.9 1800 2400 17

Page 26 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐06 11/08/2001 1200 <1 <1 1200 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.2 <1.1 1700 2400 22

MW‐06 12/04/2001 1200 <1 <1 1200 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.1 1700 2600 23

MW‐06 01/08/2002 1200 <1 <1 1200 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 1700 2600 30

MW‐06 02/05/2002 1200 <1 <1 1200 ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.8 1800 2800 4

MW‐06 03/04/2002 1300 <1 <1 1300 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 6 1800 2900 73

MW‐06 04/03/2002 1100 <1 <1 1100 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 5.7 1900 2800 210

MW‐06 05/07/2002 990 <1 <1 990 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 3.9 1900 2700 300

MW‐06 06/04/2002 1100 <1 <1 1100 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 10 1900 2700 210

MW‐06 07/03/2002 860 <1 <1 860 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.9 1800 2500 350

MW‐06 08/08/2002 1100 <1 <1 1100 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2 1700 2600 160

MW‐06 09/05/2002 1100 <1 <1 1100 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.7 1800 2600 130

MW‐06 10/09/2002 1200 <1 <1 1200 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.5 1800 2700 88

MW‐06 11/06/2002 1200 <1 <1 1200 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.8 1800 2600 41

MW‐06 12/05/2002 1300 <1 <1 1300 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.4 1800 2600 28

MW‐06 01/07/2003 1300 <1 <1 1300 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.6 1900 2700 28

MW‐06 02/05/2003 1300 <1 <1 1300 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.3 1900 2700 29

MW‐06 03/06/2003 1200 <1 <1 1200 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.7 1900 2700 39

MW‐06 04/03/2003 1200 <1 <1 1200 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.2 1800 2700 46

MW‐06 05/02/2003 1200 <1 <1 1200 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.1 1800 2700 42

MW‐06 06/05/2003 1200 <1 <1 1200 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.2 1900 2700 39

MW‐06 07/03/2003 1200 <1 <1 1200 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 4 1800 2700 53

MW‐06 08/07/2003 1100 <1 <1 1100 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.9 1700 2700 81

MW‐06 09/05/2003 1100 <1 <1 1100 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 4.5 1800 2600 95

MW‐06 10/03/2003 1100 <1 <1 1100 ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 3.3 1800 2600 120

MW‐06 11/05/2003 1100 <1 <1 1100 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.3 1800 2600 120

MW‐06 12/03/2003 1100 <1 <1 1100 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.9 1800 2600 130

MW‐06 01/14/2004 1100 <1 <1 1100 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2 1800 2500 120

MW‐06 02/05/2004 1000 <1 <1 1000 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2 1700 2500 120

MW‐06 03/03/2004 1000 <1 <1 1000 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2 1800 2500 110

MW‐06 04/08/2004 1100 <1 <1 1100 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2 1700 2500 120

MW‐06 05/13/2004 1000 <1 <1 1000 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2 1600 2500 110

MW‐06 06/05/2004 1000 <1 <1 1000 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 2 1700 2500 110

MW‐06 07/09/2004 1100 <1 <1 1100 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2 1700 2500 88

MW‐06 08/07/2004 1200 <1 <1 1200 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.2 2 1700 2600 92

MW‐06 09/07/2004 1100 <1 <1 1100 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2 1700 2500 75

Page 27 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐06 10/06/2004 1000 <1 <1 1000 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 4 1700 2500 71

MW‐06 11/02/2004 1100 <1 <1 1100 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2 1700 2500 65

MW‐06 12/02/2004 1100 <1 <1 1100 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 3 1700 2600 59

MW‐06 01/14/2005 1100 <1 <1 1100 ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2 1700 2600 56

MW‐06 02/02/2005 1100 <1 <1 1100 ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2 1900 2600 62

MW‐06 03/09/2005 1100 <1 <1 1100 ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2 1800 2600 57

MW‐06 04/06/2005 1100 <1 <1 1100 ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 7 1700 2600 50

MW‐06 05/10/2005 1100 <1 <1 1100 ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1 1800 2700 61

MW‐06 06/03/2005 1000 <1 <1 1000 ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.6 1800 2700 65

MW‐06 07/22/2005 1000 <1 <1 1000 ‐‐ 310 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2 1900 2700 70

MW‐06 08/05/2005 900 <1 <1 900 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 2 1900 2700 72

MW‐06 09/09/2005 1000 <1 <1 1000 ‐‐ 320 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 2 1900 2700 79

MW‐06 10/05/2005 1000 <1 <1 1000 ‐‐ 310 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 3.2 1800 2700 80

MW‐06 11/08/2005 1000 <1 <1 1000 ‐‐ 320 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2 1900 2700 80

MW‐06 12/08/2005 990 <1 <1 990 ‐‐ 330 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.7 1800 2700 86

MW‐06 01/05/2006 1000 <1 <1 1000 ‐‐ 320 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.2 2 1900 2700 92

MW‐06 02/08/2006 950 <1 <1 950 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.3 2 2000 2700 94

MW‐06 03/13/2006 1000 <1 <1 1000 ‐‐ 330 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.5 1900 2700 98

MW‐06 08/03/2006 1000 <20 <20 1000 ‐‐ 350 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.9 1800 2800 97

MW‐06 09/05/2006 1000 <10 <10 1000 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.6 1900 2770 100

MW‐06 10/09/2006 1200 <20 <20 1200 ‐‐ 450 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.8 2000 3100 120

MW‐06 11/06/2006 1400 <20 <20 1400 ‐‐ 460 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.5 2300 3500 140

MW‐06 12/11/2006 1300 <20 <20 1300 ‐‐ 520 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.2 2400 3670 160

MW‐06 01/03/2007 1500 <20 <20 1500 ‐‐ 530 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.4 2500 3740 150

MW‐06 02/05/2007 1600 <20 <20 1600 ‐‐ 530 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.4 2600 3810 150

MW‐06 03/05/2007 1500 <20 <20 1500 ‐‐ 510 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.3 2600 3750 150

MW‐06 04/05/2007 1500 <20 <20 1500 ‐‐ 530 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.3 2000 3670 160

MW‐06 05/03/2007 1500 <20 <20 1500 ‐‐ 510 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.2 2500 3710 170

MW‐06 06/07/2007 1600 <20 <20 1600 ‐‐ 470 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.2 2900 4210 320

MW‐06 07/02/2007 1900 <20 <20 1900 ‐‐ 470 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.7 2900 4450 420

MW‐06 08/02/2007 1900 <20 <20 1900 ‐‐ 480 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.7 2700 4400 400

MW‐06 09/10/2007 1900 <20 <20 1900 ‐‐ 460 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.6 3000 4320 320

MW‐06 10/08/2007 1800 <20 <20 1800 ‐‐ 460 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.5 3100 4180 270

MW‐06 11/07/2007 1800 <20 <20 1800 ‐‐ 470 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.4 3000 4030 250

MW‐06 12/06/2007 1800 <20 <20 1800 ‐‐ 490 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.3 3000 3920 240

Page 28 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐06 01/14/2008 1300 <20 <20 1300 ‐‐ 490 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.1 3100 3800 180

MW‐06 02/07/2008 1800 <20 <20 1800 ‐‐ 500 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.8 3000 4380 200

MW‐06 03/04/2008 1700 <20 <20 1700 ‐‐ 500 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.1 3000 4350 190

MW‐06 04/10/2008 1600 <20 <20 1600 ‐‐ 490 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.9 2700 4250 180

MW‐06 05/05/2008 1800 <20 <20 1800 ‐‐ 470 230 1.2 74 9 6.2 650 ‐‐ ‐‐ ‐‐ 3.4 3000 4360 180

MW‐06 06/03/2008 1800 <20 <20 1800 ‐‐ 520 240 1.4 78 8.4 7.0 710 ‐‐ ‐‐ ‐‐ 3.2 3300 4260 160

MW‐06 07/01/2008 2000 <20 <20 2000 ‐‐ 490 250 1.6 83 8.6 6.6 790 ‐‐ ‐‐ ‐‐ 3.6 3000 4500 140

MW‐06 08/05/2008 2000 <20 <20 2000 ‐‐ 500 270 1.6 88 9.8 6.5 780 ‐‐ ‐‐ ‐‐ 3.3 2800 4630 140

MW‐06 09/08/2008 1800 <20 <20 1800 ‐‐ 530 260 1.5 79 9.7 6.7 730 ‐‐ ‐‐ ‐‐ 3.2 2600 4470 140

MW‐06 10/09/2008 1500 <20 <20 1500 ‐‐ 570 220 0.96 69 8.0 7.1 660 ‐‐ ‐‐ ‐‐ 3.1 2600 4270 160

MW‐06 11/04/2008 1700 <20 <20 1700 ‐‐ 540 240 1.1 75 8.8 6.3 700 ‐‐ ‐‐ ‐‐ 3.0 2900 4160 170

MW‐06 12/03/2008 1800 <20 <20 1800 ‐‐ 540 230 1.5 74 7.9 6.6 720 ‐‐ ‐‐ ‐‐ 3.1 2700 4260 170

MW‐06 01/13/2009 1500 <8.2 <8.2 1500 ‐‐ 420 200 1.4 66 6.9 5.8 660 ‐‐ ‐‐ ‐‐ 2.4 2600 3730 120

MW‐06 02/04/2009 1300 <8.2 <8.2 1300 ‐‐ 350 160 1.0 56 4.7 5.5 600 ‐‐ ‐‐ ‐‐ 2.2 2100 3210 69

MW‐06 03/04/2009 1300 <8.2 <8.2 1300 ‐‐ 350 160 1.0 54 4.3 5.7 530 ‐‐ ‐‐ ‐‐ 2.2 2000 3190 67

MW‐06 04/14/2009 1400 <8.2 <8.2 1400 ‐‐ 390 190 1.2 66 5.7 6.7 640 ‐‐ ‐‐ ‐‐ 2.3 2300 3380 97

MW‐06 05/04/2009 1200 <8.2 <8.2 1200 ‐‐ 370 150 1.1 52 4.2 5.3 560 ‐‐ ‐‐ ‐‐ 2.2 1900 3140 87

MW‐06 06/09/2009 1200 <8.2 <8.2 1200 ‐‐ 340 150 1 49 3.8 4.5 500 ‐‐ ‐‐ ‐‐ 2 2000 2950 99

MW‐06 07/14/2009 1300 <8.2 <8.2 1300 ‐‐ 370 160 1.2 57 4.6 5.7 570 ‐‐ ‐‐ ‐‐ 2.2 2100 3340 98

MW‐06 08/04/2009 1300 <8.2 <8.2 1300 ‐‐ 410 170 1.1 58 4.5 4.9 570 ‐‐ ‐‐ ‐‐ 2.3 2300 3320 120

MW‐06 09/08/2009 1400 <16 <16 1400 ‐‐ 390 160 1.1 58 4.5 6.0 610 ‐‐ ‐‐ ‐‐ 2.1 2200 3170 130

MW‐06 10/07/2009 1200 <8.2 <8.2 1200 ‐‐ 370 160 0.98 58 4.5 5.7 560 ‐‐ ‐‐ ‐‐ 2.0 2000 3150 140

MW‐06 11/10/2009 1200 <8.2 <8.2 1200 ‐‐ 390 160 0.92 60 4.4 5.9 510 ‐‐ ‐‐ ‐‐ 2.1 2100 3200 140

MW‐06 12/08/2009 1200 <8.2 <8.2 1200 ‐‐ 440 180 0.91 63 4.7 5.8 510 ‐‐ ‐‐ ‐‐ 2.2 2400 3410 170

MW‐06 01/05/2010 1200 <4.1 <4.1 1200 ‐‐ 510 210 0.98 77 5.8 7.0 590 ‐‐ ‐‐ ‐‐ 2.2 2400 3570 190

MW‐06 02/10/2010 1200 <8.2 <8.2 1200 ‐‐ 480 190 0.88 70 5.8 6.4 530 ‐‐ ‐‐ ‐‐ 1.8 2600 3580 200

MW‐06 03/08/2010 1200 <8.2 <8.2 1200 ‐‐ 500 190 0.82 66 5.1 5.4 550 ‐‐ ‐‐ ‐‐ 1.5 2400 3570 230

MW‐06 04/15/2010 1200 <8.2 ‐‐ 1200 ‐‐ 520 200 1 68 5.4 5.6 620 ‐‐ ‐‐ ‐‐ 2.1 2400 3470 200

MW‐06 07/08/2010 1200 <8.2 ‐‐ 1200 ‐‐ 480 180 0.84 59 4.8 5.1 510 ‐‐ ‐‐ ‐‐ 2.1 2300 3490 180

MW‐06 10/27/2010 1200 <8.2 ‐‐ 1200 ‐‐ 460 180 0.95 57 4.7 5.5 570 0.097 ‐‐ ‐‐ 1.9 2300 3480 170

MW‐06 01/19/2011 1200 <8.2 ‐‐ 1200 ‐‐ 450 170 0.88 56 4.7 5.3 580 ‐‐ ‐‐ ‐‐ 1.5 2200 3550 160

MW‐06 04/04/2011 1300 <8.2 ‐‐ 1300 ‐‐ 430 180 0.84 55 4.3 5.1 580 ‐‐ ‐‐ ‐‐ 1.7 2300 3560 150

MW‐06 07/07/2011 1200 <8.2 ‐‐ 1200 ‐‐ 370 170 0.92 51 4.2 4.9 580 ‐‐ ‐‐ <0.10 1.8 2200 3260 100

MW‐06 10/04/2011 1100 <8.2 ‐‐ 1100 ‐‐ 410 160 0.7 52 3.9 4.7 550 ‐‐ ‐‐ <0.50 Jo 1.7 2300 3120 140

MW‐06 01/18/2012 1100 <8.2 ‐‐ 1100 ‐‐ 370 150 0.74 51 4.1 4.7 560 ‐‐ ‐‐ <0.20 1.7 2100 3190 150

Page 29 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐06 04/04/2012 980 <8.2 ‐‐ 980 ‐‐ 330 130 0.57 44 3.2 4.0 460 ‐‐ ‐‐ <0.50 1.4 1900 2740 150

MW‐06 07/23/2012 1000 <8.2 ‐‐ 1000 ‐‐ 360 130 0.57 48 3.7 4.2 510 ‐‐ ‐‐ <0.20 1.6 2000 3000 160

MW‐06 10/15/2012 1000 <8.2 ‐‐ 1000 ‐‐ 310 160 0.49 49 3.9 5.0 550 ‐‐ ‐‐ 0.87 1.9 2100 3060 290

MW‐06 01/22/2013 880 <8.2 ‐‐ 880 ‐‐ 270 130 0.3 39 3 5.0 500 ‐‐ ‐‐ 1.6 1.5 1900 2830 320

MW‐06 04/18/2013 910 <8.2 ‐‐ 910 ‐‐ 280 130 0.36 39 2.5 4.9 500 ‐‐ ‐‐ 1.4 1.5 1900 2610 300

MW‐06 07/17/2013 850 <8.2 ‐‐ 850 ‐‐ 250 130 0.25 40 2.9 5.1 480 ‐‐ ‐‐ 2.4 2.1 1900 2680 360

MW‐06 10/21/2013 890 <8.2 ‐‐ 890 ‐‐ 250 120 0.5 36 3 5.1 480 ‐‐ ‐‐ 0.46 2.1 1900 2820 360

MW‐06 01/22/2014 890 <8.2 ‐‐ 890 ‐‐ 220 120 0.73 36 2.7 5.3 510 ‐‐ ‐‐ 0.94 2.1 1900 2640 310

MW‐06 04/22/2014 820 <8.2 ‐‐ 820 ‐‐ 210 110 0.15 34 2.6 5.2 510 ‐‐ ‐‐ 0.28 1.8 1700 2640 280

MW‐06 07/21/2014 760 <8.2 ‐‐ 760 ‐‐ 210 98 0.094 28 2.3 4.5 470 ‐‐ ‐‐ 0.47 1.7 1700 2560 260

MW‐06 10/20/2014 800 <8.2 ‐‐ 800 ‐‐ 230 120 0.35 35 2.8 5.5 480 ‐‐ ‐‐ <0.20 Jo 2.0 1600 2590 290

MW‐06 01/21/2015 740 <8.2 ‐‐ 740 ‐‐ 190 91 0.075 27 1.9 4.5 400 ‐‐ ‐‐ 0.11 1.9 1600 2340 250

MW‐06 04/15/2015 730 <8.2 ‐‐ 730 ‐‐ 200 95 0.14 28 2.3 5.2 420 ‐‐ ‐‐ <0.50 Jo 2.0 1400 2230 210

MW‐06 07/22/2015 620 <8.2 ‐‐ 620 ‐‐ 150 68 0.085 19 1.5 6.0 370 ‐‐ ‐‐ <0.10 Jo 1.9 1200 1920 150

MW‐06 10/15/2015 550 <8.2 ‐‐ 550 ‐‐ 140 47 0.11 13 1 6.9 310 ‐‐ ‐‐ <0.10 2.5 1200 1640 120

MW‐06 01/20/2016 520 <8.2 ‐‐ 520 ‐‐ 130 37 0.1 11 0.88 7.7 290 ‐‐ ‐‐ <0.10 2.5 1000 1550 110

MW‐06 04/14/2016 490 <8.2 ‐‐ 490 ‐‐ 130 43 0.052 11 0.92 11 330 ‐‐ ‐‐ <0.10 Jo 3.1 980 1490 120

MW‐06 07/18/2016 490 <8.2 ‐‐ 490 ‐‐ 110 34 <0.05 9.6 0.72 9.6 320 ‐‐ ‐‐ 0.53 2.9 940 1470 110

MW‐06 10/12/2016 480 <8.2 ‐‐ 480 ‐‐ 110 36 <0.05 Jo 9.1 0.7 11 320 ‐‐ ‐‐ 0.64 2.5 950 1450 120

MW‐07 10/29/1990 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1058 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.63 ‐‐ ‐‐ 4000 ‐‐

MW‐07 01/08/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 629 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.23 ‐‐ ‐‐ 3460 ‐‐

MW‐07 04/18/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 590 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.36 ‐‐ ‐‐ 3300 ‐‐

MW‐07 07/26/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 297 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11 ‐‐ ‐‐ 1520 ‐‐

MW‐07 10/23/1991 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 860 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.23 ‐‐ ‐‐ 1770 ‐‐

MW‐07 01/24/1992 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 299 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.5 ‐‐ ‐‐ 1380 ‐‐

MW‐07 04/02/1992 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 235 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ ‐‐ 2530 ‐‐

MW‐07 07/09/1992 768 <1 <1 768 ‐‐ 244 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.6 ‐‐ 996.6 1975 58.2

MW‐07 10/06/1992 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 321.4 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ ‐‐ 2590 ‐‐

MW‐07 01/13/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 315 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.52 ‐‐ ‐‐ 2830 ‐‐

MW‐07 04/15/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 328.6 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ ‐‐ 2880 ‐‐

MW‐07 07/14/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 190.5 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ ‐‐ 2110 ‐‐

MW‐07 10/11/1993 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 310 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ ‐‐ 2610 ‐‐

MW‐07 01/18/1994 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 286.4 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ ‐‐ 2210 ‐‐

MW‐07 04/19/1994 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ ‐‐ 2180 ‐‐

MW‐07 07/18/1994 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ ‐‐ 2300 ‐‐

Page 30 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐07 11/14/1994 1075 <1 <1 1075 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ 1584 2510 1.1

MW‐07 02/20/1995 1020 <1 <1 1020 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ 1444 2380 <1

MW‐07 05/11/1995 975 <1 <1 975 ‐‐ 186.9 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ 1432 2300 3.5

MW‐07 06/19/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.3 1600 2300 ‐‐

MW‐07 07/11/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.4 1600 2400 ‐‐

MW‐07 08/15/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.3 1800 2700 ‐‐

MW‐07 11/14/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.7 1700 2400 ‐‐

MW‐07 02/14/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.8 1600 2400 ‐‐

MW‐07 05/21/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.1 1500 2400 ‐‐

MW‐07 08/20/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 4 1400 2000 ‐‐

MW‐07 11/19/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 14 1200 2200 ‐‐

MW‐07 02/18/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 22 1200 2200 ‐‐

MW‐07 05/20/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 5.5 920 1400 ‐‐

MW‐07 08/25/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 36 1100 2600 ‐‐

MW‐07 11/20/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 20.4 1100 1900 ‐‐

MW‐07 02/26/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 20 1200 2000 ‐‐

MW‐07 05/19/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 4 960 1700 ‐‐

MW‐07 08/20/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 57 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8.5 500 790 ‐‐

MW‐07 11/24/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 130 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 14 750 1300 ‐‐

MW‐07 02/15/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 18 920 1500 ‐‐

MW‐07 05/24/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.4 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 3.2 230 330 ‐‐

MW‐07 08/20/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.7 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 4.5 180 190 ‐‐

MW‐07 11/22/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.5 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.1 2710 200 ‐‐

MW‐07 02/14/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.5 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 4.1 130 200 ‐‐

MW‐07 05/02/2000 100 <1 <1 100 ‐‐ 17 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.3 190 290 35

MW‐07 11/30/2000 51 <1 <1 51 ‐‐ 7.1 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.8 150 180 ‐‐

MW‐07 12/15/2000 66 <1 <1 66 ‐‐ 9.9 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 2.1 150 190 ‐‐

MW‐07 01/07/2001 100 <1 <1 100 ‐‐ 41 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.4 3.1 270 380 ‐‐

MW‐07 02/08/2001 55 <1 <1 55 ‐‐ 23 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.4 ‐‐ 200 310 17

MW‐07 03/25/2001 160 <1 <1 160 ‐‐ 48 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.3 6.4 380 560 13

MW‐07 04/18/2001 360 <1 <1 360 ‐‐ 73 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 600 880 7.5

MW‐07 05/22/2001 1400 <1 <1 1400 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 2300 2700 <0.5

MW‐07 06/28/2001 1400 <1 <1 1400 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.8 2100 2600 <0.5

MW‐07 07/19/2001 1400 <1 <1 1400 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.5 1800 2600 0.7

MW‐07 08/03/2001 1300 <1 <1 1300 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 1600 2400 <0.5

Page 31 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐07 09/06/2001 1300 <1 <1 1300 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.2 1900 2600 0.5

MW‐07 10/03/2001 1400 <1 <1 1400 ‐‐ 310 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 3.3 1900 2800 <0.5

MW‐07 11/08/2001 1500 <1 <1 1500 ‐‐ 490 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 3.6 2700 3500 <0.5

MW‐07 12/10/2001 1750 <1 <1 1750 ‐‐ 450 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9.1 2700 4000 <0.5

MW‐07 01/09/2002 1000 <1 <1 1000 ‐‐ 420 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 4.3 2500 3800 0.7

MW‐07 02/07/2002 1800 <1 <1 1800 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.5 4 2500 3700 <0.5

MW‐07 03/08/2002 2000 <1 <1 2000 ‐‐ 350 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 6.5 2700 4000 2

MW‐07 04/03/2002 2100 <1 <1 2100 ‐‐ 320 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 8.5 3000 4200 41

MW‐07 05/09/2002 2300 <1 <1 2300 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 11 2900 4200 <0.5

MW‐07 06/06/2002 2100 <1 <1 2100 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 5.2 2800 4000 <0.5

MW‐07 07/03/2002 2100 <1 <1 2100 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 4.7 2700 3800 1.9

MW‐07 08/08/2002 1900 <1 <1 1900 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8.1 2500 3600 18

MW‐07 09/06/2002 1900 <1 <1 1900 ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 5.9 2500 3600 7.6

MW‐07 10/10/2002 1700 <1 <1 1700 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 5.8 2400 3400 11

MW‐07 11/08/2002 1700 <1 <1 1700 ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 6.2 2400 3300 2.7

MW‐07 12/06/2002 1800 <1 <1 1800 ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 13 2600 3600 6.9

MW‐07 01/07/2003 2000 <1 <1 2000 ‐‐ 320 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 25 2800 4000 <0.5

MW‐07 02/05/2003 2000 <1 <1 2000 ‐‐ 330 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 28 2900 4200 <0.5

MW‐07 03/06/2003 1800 <1 <1 1800 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 55 2600 4000 <0.5

MW‐07 04/07/2003 1800 <1 <1 1800 ‐‐ 390 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 32 2500 3900 1.9

MW‐07 05/05/2003 1800 <1 <1 1800 ‐‐ 370 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 22 2700 3800 13

MW‐07 06/06/2003 1600 <1 <1 1600 ‐‐ 360 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 36 2400 3700 10

MW‐07 07/03/2003 1600 <1 <1 1600 ‐‐ 350 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 43 2100 3700 8.4

MW‐07 08/07/2003 1700 <1 <1 1700 ‐‐ 350 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 27 2500 3700 4.1

MW‐07 09/06/2003 1700 <1 <1 1700 ‐‐ 350 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 26 2400 3800 1.6

MW‐07 10/03/2003 1700 <1 <1 1700 ‐‐ 350 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 19 2500 3700 16

MW‐07 11/05/2003 1500 <1 <1 1500 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9.9 2300 3400 9.4

MW‐07 12/04/2003 1400 <1 <1 1400 ‐‐ 310 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8.4 2100 3100 2.7

MW‐07 01/15/2004 1300 <1 <1 1300 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 7.8 2000 3000 <0.5

MW‐07 02/06/2004 1300 <1 <1 1300 ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 21 2000 2900 <0.5

MW‐07 03/04/2004 1400 <1 <1 1400 ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9 2000 3000 1

MW‐07 04/08/2004 1200 <1 <1 1200 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 16 1900 3000 2.6

MW‐07 05/14/2004 1300 <1 <1 1300 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 39 1800 3000 48

MW‐07 06/05/2004 1300 <1 <1 1300 ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 12 2000 3100 190

MW‐07 07/09/2004 1300 <1 <1 1300 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9 2000 2900 130

Page 32 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐07 08/07/2004 1300 <1 <1 1300 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 7 1900 2800 58

MW‐07 09/03/2004 1300 <1 <1 1300 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 7 1900 2800 40

MW‐07 10/06/2004 1200 <1 <1 1200 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 9 1900 2800 64

MW‐07 11/04/2004 1400 <1 <1 1400 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.2 8 2000 2800 59

MW‐07 12/02/2004 1300 <1 <1 1300 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 6 2100 3000 54

MW‐07 01/14/2005 1400 <1 <1 1400 ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 22 2200 3100 220

MW‐07 02/02/2005 1300 <1 <1 1300 ‐‐ 350 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 22 2400 3500 270

MW‐07 03/09/2005 1600 <1 <1 1600 ‐‐ 410 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 88 2400 4000 140

MW‐07 04/07/2005 1500 <1 <1 1500 ‐‐ 450 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 85 2400 4100 81

MW‐07 05/10/2005 1300 <1 <1 1300 ‐‐ 570 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 75 2400 4100 54

MW‐07 06/06/2005 1300 <1 <1 1300 ‐‐ 570 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 70 2400 4100 16

MW‐07 07/21/2005 1300 <1 <1 1300 ‐‐ 620 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 67 2400 4100 22

MW‐07 08/04/2005 1200 <1 <1 1200 ‐‐ 570 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 72 2400 4000 16

MW‐07 09/06/2005 1300 <1 <1 1300 ‐‐ 560 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 60 2300 3900 29

MW‐07 10/06/2005 1300 <1 <1 1300 ‐‐ 530 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 55 2400 4000 30

MW‐07 11/10/2005 1200 <1 <1 1200 ‐‐ 520 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 58 2300 3900 22

MW‐07 12/08/2005 1200 <1 <1 1200 ‐‐ 470 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 43 2300 3600 13

MW‐07 01/05/2006 1200 <1 <1 1200 ‐‐ 410 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 38 2200 3400 62

MW‐07 02/08/2006 980 <1 <1 980 ‐‐ 360 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.3 32 2000 3100 180

MW‐07 03/15/2006 850 <1 <1 850 ‐‐ 380 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 33 1900 3000 200

MW‐07 08/03/2006 1100 <20 <20 1100 ‐‐ 400 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 24 1900 3160 110

MW‐07 09/05/2006 1100 <20 <20 1100 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 23 1900 3110 61

MW‐07 10/09/2006 1100 <20 <20 1100 ‐‐ 410 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 24 1900 3070 130

MW‐07 11/06/2006 1000 <10 <10 1000 ‐‐ 440 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 28 2000 2940 130

MW‐07 12/11/2006 1000 <10 <10 1000 ‐‐ 440 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 37 1900 3430 120

MW‐07 01/03/2007 1100 <20 <20 1100 ‐‐ 420 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 2000 3130 98

MW‐07 02/05/2007 1300 <20 <20 1300 ‐‐ 380 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 25 2000 3100 58

MW‐07 03/05/2007 1200 <20 <20 1200 ‐‐ 390 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 20 2000 3100 63

MW‐07 04/05/2007 1200 <20 <20 1200 ‐‐ 380 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 25 1800 3150 68

MW‐07 05/03/2007 1200 <20 <20 1200 ‐‐ 420 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 1900 3190 71

MW‐07 06/07/2007 1200 <20 <20 1200 ‐‐ 380 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 2000 3350 72

MW‐07 07/02/2007 1200 <20 <20 1200 ‐‐ 410 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 1800 3180 78

MW‐07 08/02/2007 1200 <20 <20 1200 ‐‐ 410 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 1900 3220 95

MW‐07 09/10/2007 1200 <20 <20 1200 ‐‐ 410 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 1900 3180 73

MW‐07 10/08/2007 1100 <20 <20 1100 ‐‐ 380 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 2000 3130 87

Page 33 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐07 11/07/2007 1100 <20 <20 1100 ‐‐ 410 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 3000 3070 100

MW‐07 12/06/2007 1100 <20 <20 1100 ‐‐ 410 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 1900 3050 79

MW‐07 01/14/2008 1200 <20 <20 1200 ‐‐ 410 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 2000 3070 72

MW‐07 02/07/2008 1300 <20 <20 1300 ‐‐ 320 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 25 2000 3240 41

MW‐07 03/04/2008 1200 <20 <20 1200 ‐‐ 320 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 56 2000 3110 32

MW‐07 04/10/2008 1200 <20 <20 1200 ‐‐ 320 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 22 1800 2960 25

MW‐07 05/05/2008 1100 <20 <20 1100 ‐‐ 300 140 0.53 24 8 110 390 ‐‐ ‐‐ ‐‐ 24 1700 2900 21

MW‐07 06/03/2008 1200 <20 <20 1200 ‐‐ 350 130 0.63 22 7.3 120 400 ‐‐ ‐‐ ‐‐ 25 2000 2880 32

MW‐07 07/01/2008 1100 <10 <10 1100 ‐‐ 340 120 0.67 19 7.4 130 410 ‐‐ ‐‐ ‐‐ 68 1700 2930 40

MW‐07 08/04/2008 1100 <20 <20 1100 ‐‐ 180 99 0.59 16 6.1 110 370 ‐‐ ‐‐ ‐‐ 25 1700 2940 22

MW‐07 09/08/2008 1000 <20 <20 1000 ‐‐ 350 110 0.7 18 7.5 120 430 ‐‐ ‐‐ ‐‐ 23 1600 2890 46

MW‐07 10/09/2008 970 <10 <10 970 ‐‐ 320 98 0.57 17 6.7 110 390 ‐‐ ‐‐ ‐‐ 22 1600 2820 54

MW‐07 11/04/2008 1000 <20 <20 1000 ‐‐ 330 110 0.58 19 7.1 120 420 ‐‐ ‐‐ ‐‐ 22 1700 2780 61

MW‐07 12/03/2008 1000 <10 <10 1000 ‐‐ 340 100 0.66 16 6.1 120 380 ‐‐ ‐‐ ‐‐ 23 3100 2680 65

MW‐07 01/13/2009 1100 <8.2 <8.2 1100 ‐‐ 370 140 0.63 22 8.4 130 390 ‐‐ ‐‐ ‐‐ 26 1900 2940 26

MW‐07 02/04/2009 1100 <8.2 <8.2 1100 ‐‐ 180 170 0.62 29 8.3 140 430 ‐‐ ‐‐ ‐‐ 23 1700 2930 11

MW‐07 03/04/2009 1100 <8.2 <8.2 1100 ‐‐ 330 150 0.6 26 6.8 110 380 ‐‐ ‐‐ ‐‐ 32 1700 2880 22

MW‐07 04/14/2009 1000 <8.2 <8.2 1000 ‐‐ 270 120 0.43 21 6.3 96 370 ‐‐ ‐‐ ‐‐ 38 1600 2590 15

MW‐07 05/04/2009 1000 <8.2 <8.2 1000 ‐‐ 310 120 0.42 22 5.8 91 390 ‐‐ ‐‐ ‐‐ 37 1400 2650 19

MW‐07 06/08/2009 1000 <8.2 <8.2 1000 ‐‐ 310 120 0.35 20 5.1 84 380 ‐‐ ‐‐ ‐‐ 35 1500 2660 31

MW‐07 07/13/2009 950 <8.2 <8.2 950 ‐‐ 310 120 0.31 20 5.2 85 380 ‐‐ ‐‐ ‐‐ 41 1700 2620 59

MW‐07 08/04/2009 950 <8.2 <8.2 950 ‐‐ 310 110 0.3 20 5.2 78 360 ‐‐ ‐‐ ‐‐ 42 1500 2650 55

MW‐07 09/08/2009 1000 <16 <16 1000 ‐‐ 300 110 0.31 20 5.0 84 370 ‐‐ ‐‐ ‐‐ 37 1500 2640 51

MW‐07 10/06/2009 850 <8.2 <8.2 850 ‐‐ 290 110 0.32 20 5.3 84 350 ‐‐ ‐‐ ‐‐ 38 1300 2460 71

MW‐07 11/10/2009 850 <8.2 <8.2 850 ‐‐ 270 110 0.37 20 4.9 79 310 ‐‐ ‐‐ ‐‐ 36 1300 2400 52

MW‐07 12/08/2009 840 <8.2 <8.2 840 ‐‐ 260 110 0.4 21 5.0 72 310 ‐‐ ‐‐ ‐‐ 33 1400 2340 48

MW‐07 01/05/2010 830 <4.1 <4.1 830 ‐‐ 270 100 0.44 20 5.2 72 330 ‐‐ ‐‐ ‐‐ 31 1400 2300 24

MW‐07 02/10/2010 870 <8.2 <8.2 30 ‐‐ 270 110 0.53 22 5.0 69 340 ‐‐ ‐‐ ‐‐ 34 1500 2350 27

MW‐07 03/08/2010 780 <8.2 <8.2 780 ‐‐ 230 94 0.4 19 4.7 56 270 ‐‐ ‐‐ ‐‐ 22 1300 1900 36

MW‐07 04/15/2010 740 <8.2 ‐‐ 740 ‐‐ 220 110 0.46 22 5.6 52 310 ‐‐ ‐‐ ‐‐ 20 1200 2030 41

MW‐07 07/08/2010 680 <8.2 ‐‐ 680 ‐‐ 330 110 0.4 26 6.1 48 270 ‐‐ ‐‐ ‐‐ 14 1200 2140 26

MW‐07 10/27/2010 520 <8.2 ‐‐ 520 ‐‐ 310 100 0.27 22 5.8 50 250 0.094 ‐‐ ‐‐ 11 1200 1970 52

MW‐07 01/19/2011 570 <8.2 ‐‐ 570 ‐‐ 330 100 0.33 23 5.6 47 260 ‐‐ ‐‐ ‐‐ 11 1200 2120 43

MW‐07 04/04/2011 630 <8.2 ‐‐ 630 ‐‐ 190 91 0.37 20 4.4 42 260 ‐‐ ‐‐ ‐‐ 9.9 1000 1760 23

MW‐07 07/07/2011 490 <8.2 ‐‐ 490 ‐‐ 180 74 0.18 17 3.7 37 200 ‐‐ ‐‐ 1.5 9.9 940 1470 22

Page 34 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐07 11/09/2011 463 <5.0 ‐‐ 463 0.42 165 61.7 J 4.23 J 12.5 J 3.74 J 41.0 192 J 0.1 ‐‐ 0.12 7.3 772 1420 35.5

MW‐07 01/19/2012 390 ‐‐ ‐‐ 390 1.6 170 64 6.7 13 3.8 42 180 0.1 ‐‐ <0.10 10 800 1380 42

MW‐07 04/03/2012 438 <5.0 ‐‐ 438 <1.0 <198 U 68.4 8.28 13.9 3.97 44.7 198 0.12 ‐‐ <0.50 9.7 863 1480 <20.7 U

MW‐07 07/24/2012 560 <5.0 ‐‐ 560 0.69 270 55.1 6.56 10.1 J+ 3.8 70.2 207 0.13 ‐‐ <0.25 7.7 1170 2110 103

MW‐07 10/15/2012 632 <5.0 ‐‐ 632 0.82 331 69.3 J 7.59 13.4 J 4.21 J 106 J 365 J 0.085 ‐‐ <0.25 12.0 1720 2570 127

MW‐07 01/22/2013 582 <5.0 ‐‐ 582 0.97 381 68.5 6.36 13.8 4.4 108 331 0.12 ‐‐ <0.25 13.4 1310 2100 121

MW‐07 04/16/2013 550 <5.0 ‐‐ 550 0.93 336 46.1 4.32 8.76 3.1 92.4 330 0.14 ‐‐ <0.25 10.0 1290 2230 87.0

MW‐07 07/17/2013 398 <5.0 ‐‐ 398 1.0 366 36.9 1.3 7.81 1.86 89.0 J 325 0.091 ‐‐ <0.25 11.9 1130 2290 54.7

MW‐07 10/21/2013 468 <5.0 ‐‐ 468 ‐‐ 420 37.0 J 2.35 7.90 J 1.97 88.1 297 J ‐‐ ‐‐ <0.25 14.2 1160 2260 62.0

MW‐07 01/22/2014 406 <5.0 ‐‐ 406 ‐‐ 367 37.4 2.21 7.16 2.58 84.8 292 ‐‐ ‐‐ <0.25 19.0 1210 2120 67.8

MW‐07 04/22/2014 422 <5.0 ‐‐ 422 ‐‐ 381 47.5 0.745 9.48 J 2.99 109 J 371 J ‐‐ ‐‐ <0.25 <14.4. U 1170 2080 72.0

MW‐07 10/20/2014 491 <5.0 ‐‐ 491 ‐‐ 362 45.0 3.5 8.94 3.02 100 342 ‐‐ ‐‐ <0.10 5.9 1240 1980 73.6

MW‐07 04/15/2015 547 <5.0 ‐‐ 547 ‐‐ 335 75.7 J 6.05 J 13.2 J 4.66 J 111 J 322 J ‐‐ ‐‐ <0.10 4.6 1410 2030 119

MW‐07 10/15/2015 414 <5.0 ‐‐ 414 ‐‐ 424 61.3 6.28 12.6 3.61 J 57.5 446 ‐‐ ‐‐ <0.10 8.7 1680 2780 327

MW‐07 04/14/2016 390 <5.0 ‐‐ 390 ‐‐ 284 63.2 5.55 14.6 3.53 J 44.5 373 J ‐‐ ‐‐ <0.10 4.2 J+ 1470 2430 372

MW‐07 10/12/2016 358 <5.0 ‐‐ 361 ‐‐ 200 75 7.12 18 3.66 37.6 J 278 ‐‐ ‐‐ 0.11 4.7 J‐ 1050 1650 230

MW‐08 11/14/1994 84 <1 <1 84 ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27 <1.1 460 566 30

MW‐08 12/02/1994 48 <1 <1 48 ‐‐ 35 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27 <1.1 372 597 38

MW‐08 01/19/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 22 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 20 ‐‐ 458 497 ‐‐

MW‐08 02/20/1995 280.5 <1 <1 280.5 ‐‐ 51 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 ‐‐ 450 829 12

MW‐08 03/14/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 90 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.81 ‐‐ 1424 1898 ‐‐

MW‐08 05/11/1995 949 <1 <1 949 ‐‐ 69.9 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 ‐‐ 1526 1940 4

MW‐08 06/19/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 98 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.3 1700 2000 ‐‐

MW‐08 07/11/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 55 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.6 <1.1 860 1200 ‐‐

MW‐08 08/15/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.1 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 10 <1.1 230 360 ‐‐

MW‐08 11/14/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.6 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.9 1.1 220 280 ‐‐

MW‐08 02/14/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.8 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1.1 180 210 ‐‐

MW‐08 05/21/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 68 2500 3300 ‐‐

MW‐08 08/20/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 81 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 6.4 1000 1600 ‐‐

MW‐08 11/19/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 61 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8.2 630 1100 ‐‐

MW‐08 02/18/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 74 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 6.6 630 1100 ‐‐

MW‐08 05/20/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 32 1000 1800 ‐‐

MW‐08 08/25/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 87 830 1700 ‐‐

MW‐08 11/20/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 21.4 1400 2500 ‐‐

MW‐08 02/26/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.3 27 1400 2400 ‐‐

Page 35 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐08 05/19/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.72 22 980 1700 ‐‐

MW‐08 08/20/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 24 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.41 9.3 240 450 ‐‐

MW‐08 11/24/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 42 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.56 14 370 670 ‐‐

MW‐08 02/15/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 26 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.7 320 460 ‐‐

MW‐08 05/24/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 48 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.9 5.9 410 630 ‐‐

MW‐08 08/20/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 28 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.9 5.1 270 410 ‐‐

MW‐08 11/22/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 20 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.23 2.2 250 360 ‐‐

MW‐08 02/11/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.6 2.4 170 310 ‐‐

MW‐08 05/02/2000 350 <1 <1 350 ‐‐ 48 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.18 3.7 520 830 3.4

MW‐08 08/09/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 61 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 3.8 700 1000 ‐‐

MW‐08 09/20/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 14 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.6 370 460 ‐‐

MW‐08 11/30/2000 1100 <1 <1 1100 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.11 5.2 1600 2400 ‐‐

MW‐08 12/14/2000 1100 <1 <1 1100 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 3.1 1500 2200 ‐‐

MW‐08 01/07/2001 1100 <1 <1 1100 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 5.2 1400 2200 ‐‐

MW‐08 02/08/2001 970 <1 <1 970 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ 1500 2200 <0.5

MW‐08 03/20/2001 1000 <1 <1 1000 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 5.6 1500 2200 <0.5

MW‐08 04/16/2001 960 <1 <1 960 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 5.1 1400 2200 <0.5

MW‐08 05/23/2001 900 <1 <1 900 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 6.4 1500 2200 3.4

MW‐08 06/18/2001 990 <1 <1 990 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 5.3 1400 2100 1.1

MW‐08 07/18/2001 980 <1 <1 980 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.3 12 1300 2100 13

MW‐08 08/02/2001 920 <1 <1 920 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.9 12 1400 2200 19

MW‐08 09/05/2001 520 <1 <1 520 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.5 13 1100 1700 170

MW‐08 10/01/2001 360 <1 <1 360 ‐‐ 100 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 14 810 1200 140

MW‐08 11/06/2001 290 <1 <1 290 ‐‐ 96 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 11 670 1000 100

MW‐08 12/03/2001 310 <1 <1 310 ‐‐ 83 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 12 560 1000 110

MW‐08 01/04/2002 250 <1 <1 250 ‐‐ 74 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 12 620 970 110

MW‐08 02/04/2002 250 <1 <1 250 ‐‐ 66 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 12 560 940 110

MW‐08 03/04/2002 210 <1 <1 210 ‐‐ 75 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 16 600 1000 140

MW‐08 04/02/2002 190 <1 <1 190 ‐‐ 98 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 21 12 720 1200 130

MW‐08 05/07/2002 210 <1 <1 210 ‐‐ 81 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.8 13 500 880 85

MW‐08 06/04/2002 120 <1 <1 120 ‐‐ 36 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.6 8.9 390 580 77

MW‐08 07/02/2002 110 <1 <1 110 ‐‐ 34 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.2 8.4 350 570 86

MW‐08 08/06/2002 130 <1 <1 130 ‐‐ 70 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 28 5.8 530 820 51

MW‐08 09/03/2002 310 <1 <1 310 ‐‐ 58 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.4 12 500 860 25

MW‐08 10/08/2002 700 <1 <1 700 ‐‐ 130 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.5 36 1000 1700 5.1

Page 36 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐08 11/05/2002 1000 <1 <1 1000 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 23 1500 2300 2.5

MW‐08 12/05/2002 710 <1 <1 710 ‐‐ 130 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 21 990 1700 12

MW‐08 01/06/2003 590 <1 <1 590 ‐‐ 110 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 37 810 1500 12

MW‐08 02/04/2003 680 <1 <1 680 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 28 1100 1700 13

MW‐08 03/04/2003 580 <1 <1 580 ‐‐ 110 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.3 24 870 1500 12

MW‐08 04/02/2003 660 <1 <1 660 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.2 18 1000 1600 10

MW‐08 05/01/2003 700 <1 <1 700 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 11 1100 1800 11

MW‐08 06/05/2003 670 <1 <1 670 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 13 1100 1700 8.1

MW‐08 07/01/2003 780 <1 <1 780 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 16 1200 1900 2.4

MW‐08 08/05/2003 950 <1 <1 950 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 31 1400 2400 15

MW‐08 09/06/2003 1100 <1 <1 1100 ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 44 1600 2900 100

MW‐08 10/02/2003 1300 <1 <1 1300 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 63 1700 3000 31

MW‐08 11/05/2003 920 <1 <1 920 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 36 1400 2300 22

MW‐08 12/03/2003 880 <1 <1 880 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 28 1200 2100 3.4

MW‐08 01/14/2004 740 <1 <1 740 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 21 1200 1900 3

MW‐08 02/05/2004 750 <1 <1 750 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 19 1100 1900 2.9

MW‐08 03/02/2004 840 <1 <1 840 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.2 14 1300 2100 11

MW‐08 04/07/2004 810 <1 <1 810 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.5 10 1400 2300 33

MW‐08 05/11/2004 940 <1 <1 940 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.3 23 1300 2200 17

MW‐08 06/03/2004 660 <1 <1 660 ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.7 17 1300 2200 35

MW‐08 07/06/2004 670 <1 <1 670 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.2 13 1200 1900 33

MW‐08 08/06/2004 630 <1 <1 630 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.2 13 1100 1900 45

MW‐08 09/02/2004 710 <1 <1 710 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 17 1200 2100 9.6

MW‐08 10/05/2004 610 <1 <1 610 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.8 12 1200 2000 43

MW‐08 11/04/2004 780 <1 <1 780 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.4 22 1400 2300 13

MW‐08 12/02/2004 770 <1 <1 770 ‐‐ 310 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.9 19 1400 2300 27

MW‐08 01/12/2005 730 <1 <1 730 ‐‐ 360 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 14 11 1500 2500 25

MW‐08 02/02/2005 690 <1 <1 690 ‐‐ 460 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 21 10 1800 2800 40

MW‐08 03/08/2005 510 <1 <1 510 ‐‐ 410 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 6 1400 2300 38

MW‐08 04/05/2005 460 <1 <1 460 ‐‐ 400 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 8 1500 2300 36

MW‐08 05/04/2005 490 <1 <1 490 ‐‐ 370 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 21 7.7 1400 2300 37

MW‐08 06/02/2005 510 <1 <1 510 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 15 7.4 1200 2100 29

MW‐08 07/21/2005 480 <1 <1 480 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 49 5 1500 2400 63

MW‐08 08/03/2005 470 <1 <1 470 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 24 5 1300 2200 48

MW‐08 09/09/2005 440 <1 <1 440 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 4 1200 1700 40

Page 37 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐08 10/06/2005 540 <1 <1 540 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 13 1300 2000 82

MW‐08 11/10/2005 570 <1 <1 570 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 10 9 1400 2200 83

MW‐08 12/08/2005 580 <1 <1 580 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.6 5.9 1400 1900 49

MW‐08 01/05/2006 380 <1 <1 380 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 42 4 1400 2100 110

MW‐08 02/08/2006 430 20 <1 430 ‐‐ 350 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 34 1700 2600 210

MW‐08 03/13/2006 500 <1 <1 500 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 44 15 1700 2500 270

MW‐08 08/03/2006 760 <20 <20 760 ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.8 1700 2620 87

MW‐08 09/05/2006 670 <10 <10 670 ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.7 1700 2570 130

MW‐08 10/09/2006 560 <10 <10 560 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.7 1300 2000 73

MW‐08 11/06/2006 440 <10 <10 440 ‐‐ 100 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.2 930 1300 64

MW‐08 12/11/2006 440 <10 <10 440 ‐‐ 91 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.9 940 1480 41

MW‐08 01/03/2007 530 <10 <10 530 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.4 990 1570 30

MW‐08 02/05/2007 760 <10 <10 760 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.9 1400 2180 41

MW‐08 03/05/2007 1100 <10 <10 1100 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.3 1900 2850 43

MW‐08 04/05/2007 1000 <10 <10 1000 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.4 1800 2870 43

MW‐08 05/03/2007 920 <10 <10 920 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.2 1600 2510 60

MW‐08 06/07/2007 960 <10 <10 960 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.9 1700 2750 56

MW‐08 07/02/2007 1000 <10 <10 1000 ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.2 1500 2930 64

MW‐08 08/02/2007 880 <10 <10 880 ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.3 1800 2840 75

MW‐08 09/10/2007 480 <10 <10 480 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.5 980 1530 47

MW‐08 10/08/2007 490 <20 <20 490 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.6 940 1480 68

MW‐08 11/07/2007 610 <10 <10 610 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.9 2000 1800 74

MW‐08 12/06/2007 640 <10 <10 640 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.1 1400 2080 94

MW‐08 01/14/2008 740 <10 <10 740 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.3 1900 2850 69

MW‐08 02/07/2008 770 <10 <10 770 ‐‐ 310 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.4 1800 2840 61

MW‐08 03/04/2008 620 <10 <10 620 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.3 1500 2350 44

MW‐08 04/10/2008 750 <10 <10 750 ‐‐ 360 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.8 1900 3000 75

MW‐08 05/05/2008 810 <10 <10 810 ‐‐ 350 77 0.44 16 2.2 160 500 ‐‐ ‐‐ ‐‐ 1.2 2000 3230 80

MW‐08 06/03/2008 1200 <20 <20 1200 ‐‐ 370 54 0.59 12 1.9 120 600 ‐‐ ‐‐ ‐‐ 7.0 2100 3330 60

MW‐08 07/01/2008 1400 <20 <20 1400 ‐‐ 400 48 0.65 11 2.2 120 720 ‐‐ ‐‐ ‐‐ 11 2400 3770 80

MW‐08 08/04/2008 1400 <20 <20 1400 ‐‐ 440 51 0.51 13 2.1 120 800 ‐‐ ‐‐ ‐‐ 8.2 2500 4050 88

MW‐08 09/08/2008 1400 <20 <20 1400 ‐‐ 500 53 0.52 15 2.6 120 820 ‐‐ ‐‐ ‐‐ 7.0 2700 4190 130

MW‐08 10/09/2008 1400 <20 <20 1400 ‐‐ 500 51 0.38 14 2.9 140 840 ‐‐ ‐‐ ‐‐ 9.2 2800 4430 230

MW‐08 11/04/2008 1500 <20 <20 1500 ‐‐ 440 45 0.43 13 2.4 140 840 ‐‐ ‐‐ ‐‐ 6.4 2700 4190 120

MW‐08 12/03/2008 1500 <20 <20 1500 ‐‐ 450 45 0.45 12 2.5 140 830 ‐‐ ‐‐ ‐‐ 4.6 2500 4090 110

Page 38 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐08 01/13/2009 860 <8.2 <8.2 860 ‐‐ 390 46 0.4 13 3.1 130 680 ‐‐ ‐‐ ‐‐ 2.3 2400 3350 200

MW‐08 02/04/2009 790 <8.2 <8.2 790 ‐‐ 330 48 0.5 14 2.9 120 570 ‐‐ ‐‐ ‐‐ 1.4 2100 3140 180

MW‐08 03/04/2009 750 <8.2 <8.2 750 ‐‐ 310 36 0.47 10 2.0 91 530 ‐‐ ‐‐ ‐‐ 1.3 1700 2770 100

MW‐08 04/14/2009 780 <8.2 <8.2 780 ‐‐ 340 43 0.25 12 2.1 120 630 ‐‐ ‐‐ ‐‐ 1.4 2000 3030 67

MW‐08 05/04/2009 830 <8.2 <8.2 830 ‐‐ 360 38 0.2 9.9 1.4 120 620 ‐‐ ‐‐ ‐‐ 1.7 2100 3070 66

MW‐08 06/09/2009 1300 <8.2 <8.2 1300 ‐‐ 500 55 0.16 22 1.4 180 710 ‐‐ ‐‐ ‐‐ 1.4 2600 3840 66

MW‐08 07/13/2009 1300 <8.2 <8.2 1300 ‐‐ 570 74 0.19 42 1.6 210 810 ‐‐ ‐‐ ‐‐ 1.5 3100 4600 88

MW‐08 08/04/2009 1400 <8.2 <8.2 1400 ‐‐ 600 70 0.19 41 1.7 210 820 ‐‐ ‐‐ ‐‐ 1.7 3200 4420 110

MW‐08 09/08/2009 1500 <16 <16 1500 ‐‐ 620 73 0.31 49 1.9 260 950 ‐‐ ‐‐ ‐‐ 1.8 3100 5090 110

MW‐08 10/06/2009 1500 <8.2 <8.2 1500 ‐‐ 640 66 0.21 61 1.7 260 890 ‐‐ ‐‐ ‐‐ 1.8 3600 4990 150

MW‐08 11/09/2009 1400 <8.2 <8.2 1400 ‐‐ 600 68 0.15 55 1.6 250 820 ‐‐ ‐‐ ‐‐ 1.8 3000 4650 140

MW‐08 12/08/2009 1200 <8.2 <8.2 1200 ‐‐ 510 56 0.11 29 2.0 200 640 ‐‐ ‐‐ ‐‐ 1.7 2600 3930 120

MW‐08 01/05/2010 1200 <4.1 <4.1 1200 ‐‐ 580 56 0.1 34 1.9 230 820 ‐‐ ‐‐ ‐‐ 1.1 2900 4270 120

MW‐08 02/10/2010 1300 <8.2 <8.2 1300 ‐‐ 600 51 0.11 35 1.8 200 830 ‐‐ ‐‐ ‐‐ 1.1 3200 4260 100

MW‐08 03/08/2010 1300 <8.2 <8.2 1300 ‐‐ 570 51 0.1 36 1.6 190 750 ‐‐ ‐‐ ‐‐ 1.2 2900 3710 93

MW‐08 04/15/2010 1200 <8.2 ‐‐ 1200 ‐‐ 590 57 0.084 35 1.9 190 870 ‐‐ ‐‐ ‐‐ 0.89 2700 4240 100

MW‐08 07/08/2010 920 <8.2 ‐‐ 920 ‐‐ 460 39 0.12 24 1.2 160 570 ‐‐ ‐‐ ‐‐ 1.1 2600 3700 110

MW‐08 10/27/2010 340 <8.2 ‐‐ 340 ‐‐ 44 6.1 0.8 2.9 0.026 56 200 0.023 ‐‐ ‐‐ 2.5 740 1020 20

MW‐08 01/19/2011 360 <4.1 ‐‐ 360 ‐‐ 36 5.4 0.94 3.3 0.1 52 180 ‐‐ ‐‐ ‐‐ 2.5 730 934 17

MW‐08 04/04/2011 340 <4.1 ‐‐ 340 ‐‐ 35 5.4 0.55 3.2 0.14 52 170 ‐‐ ‐‐ ‐‐ 1.9 620 896 14

MW‐08 07/07/2011 340 <8.2 ‐‐ 340 ‐‐ 69 18 0.19 15 0.25 77 170 ‐‐ ‐‐ 22 1.9 720 1110 13

MW‐08 10/04/2011 140 <4.1 ‐‐ 140 ‐‐ 25 6.9 0.57 2.9 0.097 50 72 ‐‐ ‐‐ 13 0.95 380 541 15

MW‐08 01/18/2012 140 <4.1 ‐‐ 140 ‐‐ 39 7.5 0.14 4.4 0.13 63 75 ‐‐ ‐‐ 15 0.8 410 600 16

MW‐08 04/04/2012 190 <4.1 ‐‐ 190 ‐‐ 31 8.1 0.41 5.3 0.15 51 87 ‐‐ ‐‐ 14 1.3 460 649 24

MW‐08 07/23/2012 150 <4.1 ‐‐ 150 ‐‐ 22 18 0.08 14 0.21 72 42 ‐‐ ‐‐ 21 1.1 420 624 20

MW‐08 10/15/2012 150 <4.1 ‐‐ 150 ‐‐ 22 9.9 0.18 7.3 0.16 52 36 ‐‐ ‐‐ 1.0 0.85 280 403 8.8

MW‐08 01/22/2013 170 <4.1 ‐‐ 170 ‐‐ 25 14 0.12 13 0.22 53 54 ‐‐ ‐‐ 11 1.0 350 559 14

MW‐08 04/17/2013 190 <4.1 ‐‐ 190 ‐‐ 22 13 0.12 8.2 0.31 59 50 ‐‐ ‐‐ 6.8 2.7 340 523 15

MW‐08 07/17/2013 170 <4.1 ‐‐ 170 ‐‐ 50 30 0.072 31 0.47 87 55 ‐‐ ‐‐ 46 1.0 650 930 26

MW‐08 10/21/2013 160 <4.1 ‐‐ 160 ‐‐ 54 28 <0.05 11 0.67 65 38 ‐‐ ‐‐ 11 1.2 410 651 16

MW‐08 01/22/2014 160 <4.1 ‐‐ 160 ‐‐ 33 25 0.075 12 0.74 79 37 ‐‐ ‐‐ 15 0.97 390 598 20

MW‐08 04/22/2014 170 <4.1 ‐‐ 170 ‐‐ 61 35 <0.05 19 0.48 79 51 ‐‐ ‐‐ 28 0.84 550 848 19

MW‐08 07/21/2014 200 <8.2 ‐‐ 200 ‐‐ 120 48 <0.05 26 0.81 120 110 ‐‐ ‐‐ 47 0.86 880 1320 22

MW‐08 10/20/2014 170 <4.1 ‐‐ 170 ‐‐ 65 26 <0.05 11 0.77 73 94 ‐‐ ‐‐ 27 0.83 500 847 15

MW‐08 01/21/2015 150 <4.1 ‐‐ 150 ‐‐ 63 21 <0.05 9.4 0.56 72 55 ‐‐ ‐‐ 16 1.1 490 702 14

Page 39 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐08 04/15/2015 140 <4.1 ‐‐ 140 ‐‐ 86 36 <0.05 19 1.1 83 72 ‐‐ ‐‐ 35 0.73 580 909 18

MW‐08 07/22/2015 180 <4.1 ‐‐ 180 ‐‐ 85 34 <0.05 18 0.43 78 72 ‐‐ ‐‐ 18 0.8 540 879 21

MW‐08 10/15/2015 190 <4.1 ‐‐ 190 ‐‐ 84 33 <0.05 15 0.75 69 68 ‐‐ ‐‐ 20 0.58 640 814 12

MW‐08 01/20/2016 150 <4.1 ‐‐ 150 ‐‐ 110 28 <0.05 11 0.99 73 94 ‐‐ ‐‐ 27 0.7 620 946 23

MW‐08 04/14/2016 160 <4.1 ‐‐ 160 ‐‐ 63 23 <0.05 9.9 0.42 55 79 ‐‐ ‐‐ 13 0.93 450 685 19

MW‐08 07/18/2016 150 <4.1 ‐‐ 150 ‐‐ 43 23 <0.05 10 0.12 48 66 ‐‐ ‐‐ 23 0.86 490 678 14

MW‐08 10/12/2016 110 <4.1 ‐‐ 110 ‐‐ 130 43 <0.05 18 0.74 77 92 ‐‐ ‐‐ 24 0.53 620 987 29

MW‐09 11/14/1994 264 <1 <1 264 ‐‐ 22 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 25 <1.1 562 801 36

MW‐09 12/02/1994 288 <1 <1 288 ‐‐ 28 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 <1.1 566 912 43

MW‐09 01/19/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 80 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 87 ‐‐ 1064 1699 ‐‐

MW‐09 02/20/1995 331.5 <1 <1 331.5 ‐‐ 61 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 81 ‐‐ 1014 1549 100

MW‐09 03/14/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 58 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 86 ‐‐ 1050 1681 ‐‐

MW‐09 05/11/1995 377 <1 <1 377 ‐‐ 42.2 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 48 ‐‐ 1036 1331 74

MW‐09 06/19/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 63 <1.1 990 1400 ‐‐

MW‐09 07/11/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 <1.1 690 970 ‐‐

MW‐09 08/15/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 4.1 680 930 ‐‐

MW‐09 11/14/1995 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 22 <1.1 840 1100 ‐‐

MW‐09 02/14/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.2 2.1 2300 2800 ‐‐

MW‐09 05/21/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.2 7.7 1700 2600 ‐‐

MW‐09 08/20/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.5 1.4 1400 2000 ‐‐

MW‐09 11/19/1996 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.23 2.3 1500 2300 ‐‐

MW‐09 02/18/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.1 2.1 1300 2200 ‐‐

MW‐09 05/20/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 95 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.45 <1.1 1000 1600 ‐‐

MW‐09 08/25/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.9 1.5 430 760 ‐‐

MW‐09 11/20/1997 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 71 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.5 1.3 890 1400 ‐‐

MW‐09 02/26/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 88 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.5 1.2 950 1500 ‐‐

MW‐09 05/19/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 51 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 23 1.9 750 1100 ‐‐

MW‐09 08/20/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 57 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 14 <1.1 600 1100 ‐‐

MW‐09 11/24/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 52 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.6 1.3 580 940 ‐‐

MW‐09 02/15/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 65 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.7 <1.1 800 1200 ‐‐

MW‐09 05/24/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.5 <1.1 460 690 ‐‐

MW‐09 08/20/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 25 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.9 <1.1 390 550 ‐‐

MW‐09 11/22/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 14 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.9 1.1 350 480 ‐‐

MW‐09 02/11/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 49 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.7 1.2 640 1000 ‐‐

MW‐09 05/02/2000 220 <1 <1 220 ‐‐ 28 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.4 <1.1 380 600 9.4

Page 40 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐09 08/09/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 21.1 390 520 ‐‐

MW‐09 09/20/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 15 <1.1 350 500 ‐‐

MW‐09 11/28/2000 410 <1 <1 410 ‐‐ 60 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 15 5.2 670 1000 ‐‐

MW‐09 12/14/2000 480 <1 <1 480 ‐‐ 75 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 20 2.2 790 1200 ‐‐

MW‐09 01/07/2001 610 <1 <1 610 ‐‐ 100 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 21 1.4 1000 1500 ‐‐

MW‐09 02/02/2001 760 <1 <1 760 ‐‐ 130 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27 ‐‐ 1400 1900 33

MW‐09 03/20/2001 590 <1 <1 590 ‐‐ 99 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 15 1.6 980 1500 24

MW‐09 04/16/2001 260 <1 <1 260 ‐‐ 36 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 <1.1 540 740 21

MW‐09 05/23/2001 520 <1 <1 520 ‐‐ 73 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 14 2.8 870 1300 18

MW‐09 06/18/2001 420 <1 <1 420 ‐‐ 63 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.5 <1.1 700 1000 11

MW‐09 07/18/2001 230 <1 <1 230 ‐‐ 30 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.5 <1.1 390 610 11

MW‐09 08/02/2001 160 <1 <1 160 ‐‐ 19 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.7 7.1 300 420 8.7

MW‐09 09/05/2001 110 <1 <1 110 ‐‐ 20 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.8 <1.1 340 410 9.1

MW‐09 10/01/2001 150 <1 <1 150 ‐‐ 28 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.7 <1.1 520 460 9.1

MW‐09 11/06/2001 200 <1 <1 200 ‐‐ 39 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.3 <1.1 350 570 12

MW‐09 12/05/2001 340 <1 <1 340 ‐‐ 59 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.9 4.5 530 870 14

MW‐09 01/06/2002 390 <1 <1 390 ‐‐ 71 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.6 <1.1 620 980 12

MW‐09 02/04/2002 420 <1 <1 420 ‐‐ 77 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.7 <1.1 700 1100 10

MW‐09 03/08/2002 570 <1 <1 570 ‐‐ 110 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.1 1.3 890 1400 9.7

MW‐09 04/02/2002 380 <1 <1 380 ‐‐ 70 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.1 <1.1 620 1000 9

MW‐09 05/07/2002 180 <1 <1 180 ‐‐ 28 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 10 <1.1 370 540 16

MW‐09 06/04/2002 190 <1 <1 190 ‐‐ 38 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 15 <1.1 450 640 14

MW‐09 07/02/2002 250 <1 <1 250 ‐‐ 46 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 10 <1.1 440 720 14

MW‐09 08/06/2002 120 <1 <1 120 ‐‐ 15 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.4 <1.1 250 360 10

MW‐09 09/05/2002 90 <1 <1 90 ‐‐ 11 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.8 2.5 230 300 11

MW‐09 10/09/2002 95 <1 <1 95 ‐‐ 13 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.8 1.7 210 280 8

MW‐09 11/08/2002 50 <1 <1 50 ‐‐ 5.9 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.2 <1.1 160 160 1.3

MW‐09 12/03/2002 110 <1 <1 110 ‐‐ 19 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3 1.2 210 340 6.1

MW‐09 01/06/2003 190 <1 <1 190 ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.6 <1.1 350 530 7.3

MW‐09 02/04/2003 250 <1 <1 250 ‐‐ 43 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.3 1.2 460 680 12

MW‐09 03/05/2003 420 <1 <1 420 ‐‐ 89 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.4 1.6 760 1100 18

MW‐09 04/03/2003 130 <1 <1 130 ‐‐ 19 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11 <1.1 290 450 8.3

MW‐09 05/05/2003 190 <1 <1 190 ‐‐ 38 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.2 1.2 500 580 11

MW‐09 06/05/2003 90 <1 <1 90 ‐‐ 14 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.8 <1.1 310 310 10

MW‐09 07/02/2003 130 <1 <1 130 ‐‐ 21 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5 3.9 300 370 8.3

Page 41 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐09 08/05/2003 200 <1 <1 200 ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6 1.2 350 570 12

MW‐09 09/05/2003 100 <1 <1 100 ‐‐ 15 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.6 2.6 200 280 9.1

MW‐09 10/02/2003 100 <1 <1 100 ‐‐ 11 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.7 <1.1 210 260 9.3

MW‐09 11/05/2003 350 <1 <1 350 ‐‐ 96 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5 3.8 710 1000 19

MW‐09 12/03/2003 480 <1 <1 480 ‐‐ 110 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.1 6.4 820 1200 16

MW‐09 01/14/2004 390 <1 <1 390 ‐‐ 75 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.2 2.8 650 1000 14

MW‐09 02/05/2004 470 <1 <1 470 ‐‐ 96 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.1 2 730 1200 15

MW‐09 03/03/2004 520 <1 <1 520 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7 2 900 1400 15

MW‐09 04/07/2004 550 <1 <1 550 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 3 1100 1600 28

MW‐09 05/12/2004 350 <1 <1 350 ‐‐ 54 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 <1 610 960 17

MW‐09 06/03/2004 510 <1 <1 510 ‐‐ 93 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.7 3 790 1300 12

MW‐09 07/06/2004 280 <1 <1 280 ‐‐ 34 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.6 3 400 620 10

MW‐09 08/06/2004 270 <1 <1 270 ‐‐ 47 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.1 2 440 700 9.9

MW‐09 09/02/2004 100 <1 <1 100 ‐‐ 10 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.3 <1 220 320 9

MW‐09 10/05/2004 360 <1 <1 360 ‐‐ 49 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.8 2 490 690 9.6

MW‐09 11/02/2004 330 <1 <1 330 ‐‐ 74 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.3 2 600 900 10

MW‐09 12/02/2004 460 <1 <1 460 ‐‐ 96 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.5 2 790 1200 11

MW‐09 01/12/2005 850 <1 <1 850 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 2 1400 2200 33

MW‐09 02/01/2005 1100 <1 <1 1100 ‐‐ 320 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.6 3 1900 2900 64

MW‐09 03/08/2005 1300 <1 <1 1300 ‐‐ 370 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.7 3 2100 3100 75

MW‐09 04/05/2005 1100 <1 <1 1100 ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 3 1800 2700 76

MW‐09 05/04/2005 1100 <1 <1 1100 ‐‐ 320 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.4 2.6 2000 3000 100

MW‐09 06/02/2005 710 <1 <1 710 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.9 1.5 1200 1800 43

MW‐09 07/21/2005 480 <1 <1 480 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 10 3 1100 1700 34

MW‐09 08/03/2005 560 <1 <1 560 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.7 2 1100 1700 34

MW‐09 09/07/2005 460 <1 <1 460 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.4 2 930 1300 29

MW‐09 10/06/2005 430 <1 <1 430 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.1 3 800 1300 27

MW‐09 11/11/2005 580 <1 <1 580 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11 3 1200 2000 67

MW‐09 12/07/2005 490 <1 <1 490 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.2 3.1 1100 1700 65

MW‐09 01/05/2006 750 <1 <1 750 ‐‐ 390 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 4 1900 2700 130

MW‐09 02/06/2006 640 <1 <1 640 ‐‐ 360 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 2 1600 2500 120

MW‐09 03/13/2006 710 <1 <1 710 ‐‐ 380 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 40 2.9 1900 2800 130

MW‐09 08/03/2006 500 <20 <20 500 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.4 1000 1620 60

MW‐09 09/05/2006 490 <10 <10 490 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.7 980 1530 67

MW‐09 10/09/2006 570 <10 <10 570 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.7 1300 1920 110

Page 42 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐09 11/06/2006 540 <10 <10 540 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.8 1100 1570 97

MW‐09 12/11/2006 600 <10 <10 600 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.1 1200 1960 110

MW‐09 01/03/2007 590 <10 <10 590 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.2 1200 1850 110

MW‐09 02/05/2007 630 <10 <10 630 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.4 1200 1800 86

MW‐09 03/05/2007 650 <10 <10 650 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6 1200 1930 95

MW‐09 04/05/2007 600 <10 <10 600 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.1 1100 1760 82

MW‐09 05/03/2007 570 <10 <10 570 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.1 1000 1640 73

MW‐09 06/07/2007 520 <10 <10 520 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.9 930 1580 64

MW‐09 07/02/2007 450 <10 <10 450 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.2 840 1270 53

MW‐09 08/02/2007 490 <10 <10 490 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.9 910 1390 60

MW‐09 09/10/2007 490 <10 <10 490 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6 900 1420 59

MW‐09 10/08/2007 500 <10 <10 500 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.4 920 1420 56

MW‐09 11/07/2007 650 <10 <10 650 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.4 1100 1880 84

MW‐09 12/06/2007 430 <5 <5 430 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.5 770 1170 40

MW‐09 01/14/2008 720 <10 <10 720 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.1 1500 2040 94

MW‐09 02/07/2008 860 <10 <10 860 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.2 1600 2420 77

MW‐09 03/04/2008 990 <10 <10 990 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.8 1800 2740 120

MW‐09 04/10/2008 940 <10 <10 940 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.7 1700 2680 120

MW‐09 05/05/2008 660 <10 <10 660 ‐‐ 200 98 0.48 23 2.4 39 280 ‐‐ ‐‐ ‐‐ 5.2 1200 1950 81

MW‐09 06/03/2008 410 <5.0 <5.0 410 ‐‐ 120 54 0.18 13 1.1 41 170 ‐‐ ‐‐ ‐‐ 5.4 760 1200 48

MW‐09 07/01/2008 410 <5.0 <5.0 410 ‐‐ 120 53 0.19 13 1.2 40 160 ‐‐ ‐‐ ‐‐ 5.9 720 1180 44

MW‐09 08/04/2008 490 <20 <20 490 ‐‐ 150 57 0.23 13 1.4 42 170 ‐‐ ‐‐ ‐‐ 6.7 810 1390 50

MW‐09 09/08/2008 510 <5.0 <5.0 510 ‐‐ 160 66 0.31 16 1.8 47 220 ‐‐ ‐‐ ‐‐ 7.1 910 1510 57

MW‐09 10/09/2008 510 <10 <10 510 ‐‐ 160 62 0.28 15 1.6 45 210 ‐‐ ‐‐ ‐‐ 6.4 890 1520 54

MW‐09 11/04/2008 620 <10 <10 620 ‐‐ 190 78 0.36 19 2.0 50 250 ‐‐ ‐‐ ‐‐ 6.5 1100 1780 68

MW‐09 12/03/2008 850 <20 <20 850 ‐‐ 280 100 0.65 24 3.0 59 360 ‐‐ ‐‐ ‐‐ 6.9 1400 2370 100

MW‐09 01/13/2009 950 <8.2 <8.2 950 ‐‐ 280 120 0.87 35 4.3 81 340 ‐‐ ‐‐ ‐‐ 22 1700 2620 91

MW‐09 02/04/2009 1000 <8.2 <8.2 1000 ‐‐ 320 140 0.78 37 4.3 76 410 ‐‐ ‐‐ ‐‐ 17 1600 2790 100

MW‐09 03/04/2009 1100 <8.2 <8.2 1100 ‐‐ 370 150 0.9 37 4.4 66 500 ‐‐ ‐‐ ‐‐ 11 1900 3040 130

MW‐09 04/14/2009 900 <8.2 <8.2 900 ‐‐ 320 130 0.77 30 3.8 58 440 ‐‐ ‐‐ ‐‐ 8.1 1700 2550 110

MW‐09 05/04/2009 1100 <8.2 <8.2 1100 ‐‐ 390 140 0.84 34 3.5 66 480 ‐‐ ‐‐ ‐‐ 12 1800 2940 110

MW‐09 06/09/2009 1100 <8.2 <8.2 1100 ‐‐ 360 140 0.76 31 3.5 59 480 ‐‐ ‐‐ ‐‐ 8.5 1900 2970 120

MW‐09 07/13/2009 890 <8.2 <8.2 890 ‐‐ 290 120 0.56 29 3.3 60 400 ‐‐ ‐‐ ‐‐ 10 1700 2560 93

MW‐09 08/04/2009 950 <8.2 <8.2 950 ‐‐ 300 130 0.59 31 3.5 55 400 ‐‐ ‐‐ ‐‐ 11 1700 2520 89

MW‐09 09/08/2009 910 <8.2 <8.2 910 ‐‐ 290 120 0.63 29 3.7 67 450 ‐‐ ‐‐ ‐‐ 10 1500 2610 97

Page 43 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐09 10/07/2009 860 <8.2 <8.2 860 ‐‐ 320 110 0.59 25 3.5 65 420 ‐‐ ‐‐ ‐‐ 9.6 1600 2570 120

MW‐09 11/09/2009 850 <8.2 <8.2 850 ‐‐ 310 100 0.56 24 3.2 69 400 ‐‐ ‐‐ ‐‐ 11 1600 2630 120

MW‐09 12/08/2009 1100 <8.2 <8.2 1100 ‐‐ 430 130 0.73 31 4.4 83 530 ‐‐ ‐‐ ‐‐ 11 2200 3250 180

MW‐09 01/05/2010 1100 <4.1 <4.1 1100 ‐‐ 470 150 0.79 35 5.1 96 610 ‐‐ ‐‐ ‐‐ 10 2300 3560 190

MW‐09 02/10/2010 970 <8.2 <8.2 970 ‐‐ 370 120 0.61 29 4.1 76 500 ‐‐ ‐‐ ‐‐ 9.4 2000 3010 170

MW‐09 03/08/2010 950 <8.2 <8.2 950 ‐‐ 390 120 0.61 28 4.0 72 470 ‐‐ ‐‐ ‐‐ 9.5 2000 2770 180

MW‐09 04/15/2010 1100 <8.2 ‐‐ 1100 ‐‐ 450 150 0.75 33 4.7 78 620 ‐‐ ‐‐ ‐‐ 8.7 2100 3340 180

MW‐09 07/08/2010 920 <8.2 ‐‐ 920 ‐‐ 380 120 0.56 29 3.7 82 400 ‐‐ ‐‐ ‐‐ 7.3 1800 2890 160

MW‐09 10/27/2010 1000 <8.2 ‐‐ 1000 ‐‐ 450 140 0.66 32 4.7 72 570 0.18 ‐‐ ‐‐ 7.0 2300 3430 200

MW‐09 01/19/2011 940 <8.2 ‐‐ 940 ‐‐ 370 110 0.41 27 3.7 70 510 ‐‐ ‐‐ ‐‐ 7.0 2000 3050 190

MW‐09 04/04/2011 1000 <8.2 ‐‐ 1000 ‐‐ 420 130 0.4 30 3.8 76 570 ‐‐ ‐‐ ‐‐ 7.3 2100 3300 180

MW‐09 07/07/2011 950 <8.2 ‐‐ 950 ‐‐ 360 110 0.28 27 3.3 75 540 ‐‐ ‐‐ 2.5 6.8 2000 3050 160

MW‐09 10/04/2011 1100 <8.2 ‐‐ 1100 ‐‐ 540 170 0.3 39 3.9 76 690 ‐‐ ‐‐ 43 5.8 2900 3990 230

MW‐09 01/18/2012 1200 <8.2 ‐‐ 1200 ‐‐ 570 120 0.25 27 3.7 79 790 ‐‐ ‐‐ 4.7 7.3 2700 4160 220

MW‐09 04/04/2012 1200 <8.2 ‐‐ 1200 ‐‐ 630 130 0.24 29 3.4 79 720 ‐‐ ‐‐ 5.0 6.8 3100 4060 240

MW‐09 07/23/2012 890 <8.2 ‐‐ 890 ‐‐ 430 100 0.15 25 2.7 71 550 ‐‐ ‐‐ 10 5.6 2000 3120 160

MW‐09 10/16/2012 940 <8.2 ‐‐ 940 ‐‐ 420 120 0.25 28 3.6 59 590 ‐‐ ‐‐ 8.2 4.1 2200 3140 170

MW‐09 01/22/2013 850 <8.2 ‐‐ 850 ‐‐ 400 110 0.17 25 3 60 510 ‐‐ ‐‐ 4.4 2.6 1900 2870 140

MW‐09 04/18/2013 1100 <8.2 ‐‐ 1100 ‐‐ 560 120 0.2 27 3.3 77 640 ‐‐ ‐‐ <0.50 Jo 5.8 2400 3440 170

MW‐09 07/17/2013 950 <8.2 ‐‐ 950 ‐‐ 410 110 0.14 27 2.9 47 560 ‐‐ ‐‐ 11 3.4 2100 3060 160

MW‐09 10/21/2013 640 <8.2 ‐‐ 640 ‐‐ 200 96 0.056 23 1.2 56 310 ‐‐ ‐‐ 28 1.7 1300 2210 110

MW‐09 01/22/2014 610 <8.2 ‐‐ 610 ‐‐ 220 93 0.11 23 1.4 52 320 ‐‐ ‐‐ 10 1.6 1300 1980 100

MW‐09 04/22/2014 810 <8.2 ‐‐ 810 ‐‐ 180 69 0.05 18 1.4 38 440 ‐‐ ‐‐ 10 2.5 1600 2430 130

MW‐09 07/21/2014 520 <8.2 ‐‐ 520 ‐‐ 150 66 <0.05 16 0.54 45 320 ‐‐ ‐‐ 26 0.85 1200 1880 90

MW‐09 10/20/2014 630 <8.2 ‐‐ 630 ‐‐ 130 61 0.13 15 0.7 40 370 ‐‐ ‐‐ 18 2.4 1200 1960 100

MW‐09 01/21/2015 500 <8.2 ‐‐ 500 ‐‐ 84 47 <0.05 12 0.33 37 240 ‐‐ ‐‐ 21 1.6 1100 1510 73

MW‐09 04/15/2015 650 <8.2 ‐‐ 650 ‐‐ 120 50 <0.05 Jo 13 0.78 35 380 ‐‐ ‐‐ 12 2.0 1200 1820 110

MW‐09 07/22/2015 560 <8.2 ‐‐ 560 ‐‐ 130 71 <0.05 16 0.82 53 320 ‐‐ ‐‐ 23 1.4 1200 1900 93

MW‐09 10/15/2015 430 <8.2 ‐‐ 430 ‐‐ 150 57 <0.05 14 0.45 54 230 ‐‐ ‐‐ 23 1.0 1100 1550 91

MW‐09 01/20/2016 440 <8.2 ‐‐ 440 ‐‐ 140 55 0.11 13 0.28 55 240 ‐‐ ‐‐ 26 1.3 1100 1600 80

MW‐09 04/14/2016 440 <8.2 ‐‐ 440 ‐‐ 130 54 <0.05 Jo 12 0.29 59 280 ‐‐ ‐‐ 21 1.4 1000 1560 79

MW‐09 07/18/2016 400 <8.2 ‐‐ 400 ‐‐ 190 96 <0.05 23 0.11 62 240 ‐‐ ‐‐ 47 0.73 1300 1910 69

MW‐09 10/12/2016 440 <8.2 ‐‐ 440 ‐‐ 140 72 <0.05 15 0.057 53 280 ‐‐ ‐‐ 35 0.75 1100 1680 79

MW‐11 01/20/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐

MW‐11 02/26/1998 160 <1 <1 160 ‐‐ 38 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 <1.1 470 750 63

Page 44 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐11 03/19/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 2.4 550 710 ‐‐

MW‐11 04/29/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 22 1.6 510 730 ‐‐

MW‐11 05/20/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 <1.1 520 720 ‐‐

MW‐11 06/16/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 44 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 25 <1.1 570 780 ‐‐

MW‐11 07/28/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 23 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 <1.1 300 470 ‐‐

MW‐11 08/21/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 22 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27 <1.1 420 560 ‐‐

MW‐11 09/24/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 46 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1.1 580 780 ‐‐

MW‐11 10/22/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 1.6 490 740 ‐‐

MW‐11 11/25/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 <1.1 500 690 ‐‐

MW‐11 12/15/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 23 <1.1 500 660 ‐‐

MW‐11 02/16/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 22 <1.1 540 680 ‐‐

MW‐11 05/23/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 56 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 <1.1 590 930 ‐‐

MW‐11 08/23/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 40 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 540 810 ‐‐

MW‐11 11/22/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 51 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 <1.1 720 950 ‐‐

MW‐11 02/11/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 28 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 1.7 540 750 ‐‐

MW‐11 05/02/2000 150 <1 <1 150 ‐‐ 43 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 600 850 82

MW‐11 08/09/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 24 1.1 630 720 ‐‐

MW‐11 09/13/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 61 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 1.2 610 870 ‐‐

MW‐11 11/21/2000 150 <1 <1 150 ‐‐ 83 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 25 9.2 700 970 ‐‐

MW‐11 12/12/2000 170 <1 <1 170 ‐‐ 80 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27 1.5 600 930 ‐‐

MW‐11 01/06/2001 170 <1 <1 170 ‐‐ 58 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 2.2 680 900 ‐‐

MW‐11 02/06/2001 180 <1 <1 180 ‐‐ 51 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 ‐‐ 750 900 76

MW‐11 03/27/2001 220 <1 <1 220 ‐‐ 50 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1.1 780 1100 110

MW‐11 04/18/2001 220 <1 <1 220 ‐‐ 53 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 1.2 800 1100 110

MW‐11 05/25/2001 98 <1 <1 98 ‐‐ 44 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 660 940 100

MW‐11 06/29/2001 280 <1 <1 280 ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 600 850 94

MW‐11 07/17/2001 190 <1 <1 190 ‐‐ 36 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 1.6 580 880 97

MW‐11 08/02/2001 190 <1 <1 190 ‐‐ 38 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 <1.1 680 920 100

MW‐11 09/04/2001 190 <1 <1 190 ‐‐ 34 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 <1.1 610 820 86

MW‐11 10/03/2001 150 <1 <1 150 ‐‐ 25 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 <1.1 620 790 82

MW‐11 11/08/2001 150 <1 <1 150 ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 620 830 96

MW‐11 12/10/2001 180 <1 <1 180 ‐‐ 48 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 41 1.4 720 990 130

MW‐11 01/06/2002 150 <1 <1 150 ‐‐ 58 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 37 1.5 740 1000 120

MW‐11 02/07/2002 38 <1 <1 38 ‐‐ 59 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 2.3 730 970 110

MW‐11 03/08/2002 160 <1 <1 160 ‐‐ 77 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 40 <1.1 710 1000 120

Page 45 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐11 04/03/2002 170 <1 <1 170 ‐‐ 48 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 1.3 740 980 110

MW‐11 05/09/2002 150 <1 <1 150 ‐‐ 73 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 <1.1 770 1100 120

MW‐11 06/06/2002 150 <1 <1 150 ‐‐ 56 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 <1.1 730 1000 110

MW‐11 07/03/2002 100 <1 <1 100 ‐‐ 64 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 <1.1 550 790 62

MW‐11 08/10/2002 290 <1 <1 290 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 <1.1 640 980 51

MW‐11 09/06/2002 170 <1 <1 170 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 1.3 680 1000 49

MW‐11 10/09/2002 180 <1 <1 180 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 14 <1.1 700 1000 52

MW‐11 11/06/2002 170 <1 <1 170 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 14 <1.1 660 980 48

MW‐11 12/03/2002 160 <1 <1 160 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 <1.1 690 1000 49

MW‐11 01/07/2003 170 <1 <1 170 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 22 1.1 680 1000 71

MW‐11 02/04/2003 180 <1 <1 180 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 24 1.1 740 1100 79

MW‐11 03/05/2003 180 <1 <1 180 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 24 1.1 760 1100 76

MW‐11 04/02/2003 200 <1 <1 200 ‐‐ 97 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 24 <1.1 730 1000 74

MW‐11 05/02/2003 190 <1 <1 190 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 15 1.6 760 1100 55

MW‐11 06/06/2003 140 <1 <1 140 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 14 2.6 730 1100 62

MW‐11 07/01/2003 170 <1 <1 170 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 1.5 760 1100 58

MW‐11 08/07/2003 170 <1 <1 170 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 15 <1.1 680 1100 50

MW‐11 09/04/2003 150 <1 <1 150 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.9 <1.1 700 1100 52

MW‐11 10/01/2003 190 <1 <1 190 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.1 1.3 640 1000 41

MW‐11 11/04/2003 170 <1 <1 170 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11 <1.1 710 1000 42

MW‐11 12/02/2003 170 <1 <1 170 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 <1.1 620 1000 45

MW‐11 01/13/2004 190 <1 <1 190 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 <1.1 660 1000 57

MW‐11 02/04/2004 200 <1 <1 200 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 1 650 1000 55

MW‐11 03/02/2004 210 <1 <1 210 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 14 <1 750 1100 60

MW‐11 04/06/2004 180 <1 <1 180 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 <1 690 1100 65

MW‐11 05/12/2004 200 <1 <1 200 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 15 <1 690 1100 60

MW‐11 06/03/2004 150 <1 <1 150 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.8 2 640 1100 46

MW‐11 07/08/2004 170 <1 <1 170 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.7 2 650 940 43

MW‐11 08/05/2004 180 <1 <1 180 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.5 <1 610 950 42

MW‐11 09/02/2004 180 <1 <1 180 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.4 <1 560 900 37

MW‐11 10/06/2004 160 <1 <1 160 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.8 <1 610 940 42

MW‐11 11/04/2004 170 <1 <1 170 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.3 2 640 940 40

MW‐11 12/01/2004 190 <1 <1 190 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 10 <1 650 960 45

MW‐11 01/14/2005 210 <1 <1 210 ‐‐ 130 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 10 1 640 950 49

MW‐11 02/02/2005 180 <1 <1 180 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 14 <1 680 1000 55

Page 46 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐11 03/09/2005 200 <1 <1 200 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 2 730 1100 64

MW‐11 04/06/2005 240 <1 <1 240 ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 <1 970 1300 83

MW‐11 05/06/2005 180 <1 <1 180 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 <1 760 1200 67

MW‐11 06/03/2005 160 <1 <1 160 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 14 <1 710 1100 65

MW‐11 07/22/2005 190 <1 <1 190 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 18 <1 780 1200 78

MW‐11 08/05/2005 190 <1 <1 190 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 1 860 1200 70

MW‐11 09/09/2005 180 <1 <1 180 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 <1 890 1100 56

MW‐11 10/05/2005 190 <1 <1 190 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 <1 670 1100 58

MW‐11 11/10/2005 180 <1 <1 180 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 18 <1 700 1100 57

MW‐11 12/08/2005 180 <1 <1 180 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 18 1.4 730 1100 58

MW‐11 01/04/2006 190 <1 <1 190 ‐‐ 130 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 23 <1 820 1100 66

MW‐11 02/08/2006 190 <1 <1 190 ‐‐ 130 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 24 2 800 1100 69

MW‐11 03/15/2006 190 <1 <1 190 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 <1 810 1100 77

MW‐11 08/03/2006 220 <10 <10 220 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.4 790 1330 72

MW‐11 09/05/2006 260 <10 <10 260 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.8 880 1310 79

MW‐11 10/09/2006 290 <5.0 <5.0 290 ‐‐ 130 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.2 820 1190 73

MW‐11 11/06/2006 270 <5.0 <5.0 270 ‐‐ 96 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.3 760 1020 65

MW‐11 12/11/2006 260 <5.0 <5.0 260 ‐‐ 81 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.7 630 934 49

MW‐11 01/03/2007 240 <5 <5 240 ‐‐ 81 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.1 610 878 45

MW‐11 02/05/2007 230 <5 <5 230 ‐‐ 81 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.9 590 851 47

MW‐11 03/05/2007 220 <5 <5 220 ‐‐ 66 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.7 550 797 45

MW‐11 04/05/2007 220 <5 <5 220 ‐‐ 90 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2 620 915 51

MW‐11 05/03/2007 240 <5 <5 240 ‐‐ 73 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.3 580 850 45

MW‐11 06/07/2007 240 <5 <5 240 ‐‐ 47 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.6 510 751 34

MW‐11 07/02/2007 220 <5 <5 220 ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.5 470 660 27

MW‐11 08/02/2007 250 <5 <5 250 ‐‐ 25 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.1 520 650 28

MW‐11 09/10/2007 260 <5 <5 260 ‐‐ 35 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.8 500 720 30

MW‐11 10/08/2007 270 <10 <10 270 ‐‐ 22 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.9 500 675 27

MW‐11 11/07/2007 270 <5 <5 270 ‐‐ 15 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3 570 635 23

MW‐11 12/06/2007 270 <5 <5 270 ‐‐ 23 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.9 510 649 25

MW‐11 01/14/2008 270 <5 <5 270 ‐‐ 29 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.8 530 715 28

MW‐11 02/07/2008 260 <5 <5 260 ‐‐ 63 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.7 530 820 39

MW‐11 03/04/2008 260 <5 <5 260 ‐‐ 67 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2 620 896 52

MW‐11 04/10/2008 260 <5 <5 260 ‐‐ 72 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.8 660 966 59

MW‐11 05/05/2008 260 <5 <5 260 ‐‐ 67 59 <0.05 17 0.44 8.6 120 ‐‐ ‐‐ ‐‐ 1.6 630 946 57

Page 47 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐11 06/03/2008 250 <5.0 <5.0 250 ‐‐ 120 51 <0.050 14 0.44 10 150 ‐‐ ‐‐ ‐‐ 1.8 700 1030 60

MW‐11 07/01/2008 250 <5.0 <5.0 250 ‐‐ 73 42 <0.050 Jo 11 0.44 9.9 130 ‐‐ ‐‐ ‐‐ 2.1 600 884 43

MW‐11 08/04/2008 200 <2.5 <2.5 200 ‐‐ 75 32 <0.050 Jo 8.2 0.33 8.9 120 ‐‐ ‐‐ ‐‐ 1.9 550 843 41

MW‐11 09/08/2008 210 <5.0 <5.0 210 ‐‐ 53 27 <0.050 Jo 7.3 0.3 8.7 120 ‐‐ ‐‐ ‐‐ 1.6 490 736 35

MW‐11 10/09/2008 200 <5.0 <5.0 200 ‐‐ 64 22 <0.050 Jo 5.9 0.25 7.9 100 ‐‐ ‐‐ ‐‐ 1.3 460 710 30

MW‐11 11/04/2008 190 <2.5 <2.5 190 ‐‐ 73 28 <0.050 Jo 7.3 0.27 8.7 100 ‐‐ ‐‐ ‐‐ 1.1 440 689 25

MW‐11 12/03/2008 210 <5.0 <5.0 210 ‐‐ 83 40 <0.050 Jo 10 0.34 10 110 ‐‐ ‐‐ ‐‐ 1.4 510 763 36

MW‐11 01/13/2009 210 <4.1 <4.1 210 ‐‐ 75 46 <0.050 Jo 14 0.37 8.8 100 ‐‐ ‐‐ ‐‐ 1.5 530 748 43

MW‐11 02/04/2009 210 <4.1 <4.1 210 ‐‐ 77 52 <0.050 Jo 15 0.3 9.2 110 ‐‐ ‐‐ ‐‐ 1.3 570 783 46

MW‐11 03/04/2009 220 <4.1 <4.1 220 ‐‐ 86 64 <0.050 19 0.42 8.9 100 ‐‐ ‐‐ ‐‐ 1.1 600 864 56

MW‐11 04/13/2009 220 <4.1 <4.1 220 ‐‐ 84 65 <0.050 20 0.39 8.3 93 ‐‐ ‐‐ ‐‐ 1.0 630 870 52

MW‐11 05/04/2009 230 <4.1 <4.1 230 ‐‐ 86 70 <0.050 22 0.4 8.2 91 ‐‐ ‐‐ ‐‐ 1.3 630 896 55

MW‐11 06/08/2009 200 <8.2 <8.2 200 ‐‐ 110 83 <0.05 24 0.46 9.3 91 ‐‐ ‐‐ ‐‐ 1.1 710 1030 77

MW‐11 07/13/2009 210 <4.1 <4.1 210 ‐‐ 75 73 <0.050 21 0.44 10 87 ‐‐ ‐‐ ‐‐ 1.1 660 954 62

MW‐11 08/04/2009 230 <4.1 <4.1 230 ‐‐ 71 71 <0.05 21 0.42 9.2 91 ‐‐ ‐‐ ‐‐ 1.4 670 916 65

MW‐11 08/13/2009 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 76 ‐‐ ‐‐ ‐‐ ‐‐ 3.4 90 ‐‐ ‐‐ ‐‐ ‐‐ 730 1000 ‐‐

MW‐11 09/08/2009 270 <8.2 <8.2 270 ‐‐ 64 75 <0.050 21 0.48 13 120 ‐‐ ‐‐ ‐‐ 0.99 680 990 69

MW‐11 10/07/2009 230 <4.1 <4.1 230 ‐‐ 63 64 <0.050 19 0.45 13 110 ‐‐ ‐‐ ‐‐ 1.2 640 920 74

MW‐11 11/09/2009 250 <8.2 <8.2 250 ‐‐ 75 81 <0.050 25 0.51 13 91 ‐‐ ‐‐ ‐‐ 1.1 740 1000 95

MW‐11 12/08/2009 240 <4.1 <4.1 240 ‐‐ 65 81 <0.050 24 0.52 13 91 ‐‐ ‐‐ ‐‐ 1.0 710 967 96

MW‐11 01/05/2010 220 <4.1 <4.1 220 ‐‐ 78 86 <0.050 26 0.5 13 89 ‐‐ ‐‐ ‐‐ 0.98 770 1070 110

MW‐11 02/10/2010 240 <8.2 <8.2 240 ‐‐ 67 86 <0.050 29 0.38 12 94 ‐‐ ‐‐ ‐‐ 0.94 740 1030 91

MW‐11 03/08/2010 210 <8.2 <8.2 210 ‐‐ 66 88 <0.050 29 0.43 13 86 ‐‐ ‐‐ ‐‐ 1.2 820 1100 98

MW‐11 04/15/2010 220 <8.2 ‐‐ 220 ‐‐ 75 91 <0.05 31 0.36 10 91 ‐‐ ‐‐ ‐‐ 0.93 780 1070 95

MW‐11 07/08/2010 200 <8.2 ‐‐ 200 ‐‐ 78 110 <0.05 37 0.54 10 98 ‐‐ ‐‐ ‐‐ 1.0 880 1240 110

MW‐11 10/27/2010 210 <8.2 ‐‐ 210 ‐‐ 65 94 <0.05 31 0.65 14 83 0.058 ‐‐ ‐‐ 0.9 820 1100 95

MW‐11 01/19/2011 220 <8.2 ‐‐ 220 ‐‐ 63 82 <0.05 30 0.55 12 77 ‐‐ ‐‐ ‐‐ 0.92 870 1060 77

MW‐11 04/04/2011 230 <8.2 ‐‐ 230 ‐‐ 60 91 <0.05 30 0.54 13 89 ‐‐ ‐‐ ‐‐ 0.95 91 1080 81

MW‐11 07/07/2011 230 <8.2 ‐‐ 230 ‐‐ 45 95 <0.05 29 0.56 14 89 ‐‐ ‐‐ 44 0.96 770 1070 78

MW‐11 10/04/2011 200 <8.2 ‐‐ 200 ‐‐ 60 88 <0.05 29 0.57 17 75 ‐‐ ‐‐ 46 0.64 760 1050 81

MW‐11 01/19/2012 180 <8.2 ‐‐ 180 ‐‐ 55 91 <0.05 32 0.62 18 57 ‐‐ ‐‐ 45 0.96 720 1030 65

MW‐11 04/04/2012 170 <4.1 ‐‐ 170 ‐‐ 58 86 <0.05 31 0.55 16 59 ‐‐ ‐‐ 48 0.86 720 986 73

MW‐11 07/23/2012 170 <4.1 ‐‐ 170 ‐‐ 39 83 <0.05 Jo 33 0.69 17 53 ‐‐ ‐‐ 53 0.8 660 973 65

MW‐11 10/15/2012 130 <8.2 ‐‐ 130 ‐‐ 77 99 <0.05 Jo 36 0.91 17 52 ‐‐ ‐‐ 48 0.73 730 1040 95

MW‐11 01/22/2013 150 <4.1 ‐‐ 150 ‐‐ 72 85 <0.05 31 0.66 16 58 ‐‐ ‐‐ 40 0.78 710 941 76

Page 48 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐11 04/17/2013 150 <4.1 ‐‐ 150 ‐‐ 73 90 <0.05 Jo 34 0.7 15 50 ‐‐ ‐‐ 43 0.65 660 952 84

MW‐11 07/17/2013 150 <4.1 ‐‐ 150 ‐‐ 59 72 <0.05 27 0.76 16 59 ‐‐ ‐‐ 35 0.83 600 868 60

MW‐11 10/21/2013 150 <4.1 ‐‐ 150 ‐‐ 54 56 <0.05 22 0.64 12 78 ‐‐ ‐‐ 36 0.8 650 872 51

MW‐11 01/22/2014 120 <4.1 ‐‐ 120 ‐‐ 38 41 <0.05 Jo 16 0.37 9.3 64 ‐‐ ‐‐ 27 0.7 430 620 30

MW‐11 04/22/2014 130 <4.1 ‐‐ 130 ‐‐ 37 34 <0.05 14 0.2 8.0 59 ‐‐ ‐‐ 17 0.71 400 591 22

MW‐11 07/21/2014 120 <4.1 ‐‐ 120 ‐‐ 37 37 <0.05 14 0.48 9.0 60 ‐‐ ‐‐ 20 0.48 420 598 22

MW‐11 10/20/2014 130 <4.1 ‐‐ 130 ‐‐ 45 49 <0.05 20 0.66 9.2 65 ‐‐ ‐‐ 27 0.65 440 711 30

MW‐11 01/21/2015 100 <4.1 ‐‐ 100 ‐‐ 32 35 <0.05 14 0.15 6.5 57 ‐‐ ‐‐ 32 0.8 440 634 24

MW‐11 04/15/2015 110 <4.1 ‐‐ 110 ‐‐ 34 36 <0.05 14 0.24 6.8 59 ‐‐ ‐‐ 23 0.68 360 572 21

MW‐11 07/22/2015 110 <4.1 ‐‐ 110 ‐‐ 66 61 <0.05 26 0.48 9.4 95 ‐‐ ‐‐ 57 0.66 630 987 35

MW‐11 10/15/2015 94 <4.1 ‐‐ 94 ‐‐ 65 33 <0.05 14 0.13 6.0 88 ‐‐ ‐‐ 37 0.61 580 729 24

MW‐11 01/20/2016 110 <4.1 ‐‐ 110 ‐‐ 74 37 0.084 15 0.14 6.5 90 ‐‐ ‐‐ 36 0.66 550 794 26

MW‐11 04/14/2016 150 <4.1 ‐‐ 150 ‐‐ 96 48 <0.05 19 0.17 7.9 130 ‐‐ ‐‐ 34 0.67 620 910 23

MW‐11 07/18/2016 100 <4.1 ‐‐ 100 ‐‐ 45 38 <0.05 13 0.068 6.7 87 ‐‐ ‐‐ 36 0.68 520 713 21

MW‐11 10/12/2016 55 <4.1 ‐‐ 55 ‐‐ 26 53 <0.05 19 0.18 8.2 100 ‐‐ ‐‐ 73 0.56 670 908 30

MW‐12 01/20/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐

MW‐12 02/09/1998 <5 81 380 461 ‐‐ 24 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 25 <1.1 740 1800 12

MW‐12 03/19/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 23 <1.1 520 1100 ‐‐

MW‐12 04/29/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 1.2 600 1200 ‐‐

MW‐12 05/21/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 28 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27 1.7 430 780 ‐‐

MW‐12 06/16/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 26 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27 <1.1 460 750 ‐‐

MW‐12 07/28/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 25 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 25 1.5 410 600 ‐‐

MW‐12 08/21/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 500 570 ‐‐

MW‐12 09/24/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 20 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27 <1.1 380 460 ‐‐

MW‐12 10/22/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 22 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 <1.1 340 480 ‐‐

MW‐12 11/25/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 24 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 <1.1 300 420 ‐‐

MW‐12 12/15/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 26 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 18 1.5 360 420 ‐‐

MW‐12 02/16/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 14 <1.1 310 430 ‐‐

MW‐12 05/23/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 22 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.4 1.3 290 530 ‐‐

MW‐12 08/23/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 1.6 460 620 ‐‐

MW‐12 11/22/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 20 <1.1 550 630 ‐‐

MW‐12 02/17/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 15 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 18 <1.1 400 590 ‐‐

MW‐12 05/02/2000 130 <1 <1 130 ‐‐ 13 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 18 <1.1 430 540 36

MW‐12 08/08/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 1.1 470 690 ‐‐

MW‐12 09/15/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 10 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 23 1.1 440 590 ‐‐

Page 49 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐12 11/22/2000 280 <1 <1 280 ‐‐ 96 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 41 <1.1 810 1200 ‐‐

MW‐12 12/12/2000 270 <1 <1 270 ‐‐ 13 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 1.5 520 760 ‐‐

MW‐12 01/06/2001 210 <1 <1 210 ‐‐ 12 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 20 <1.1 490 660 ‐‐

MW‐12 02/06/2001 210 <1 <1 210 ‐‐ 14 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 21 ‐‐ 610 700 45

MW‐12 03/25/2001 170 <1 <1 170 ‐‐ 11 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 22 <1.1 460 650 42

MW‐12 04/16/2001 220 <1 <1 220 ‐‐ 12 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 21 <1.1 560 690 47

MW‐12 05/23/2001 180 <1 <1 180 ‐‐ 12 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 22 1.1 490 630 47

MW‐12 06/25/2001 200 <1 <1 200 ‐‐ 13 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 22 <1.1 490 680 52

MW‐12 07/19/2001 220 <1 <1 220 ‐‐ 13 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 21 2.8 480 680 55

MW‐12 08/01/2001 150 <1 <1 150 ‐‐ 12 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 22 1.4 460 580 47

MW‐12 09/05/2001 190 <1 <1 190 ‐‐ 15 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 24 <1.1 500 670 55

MW‐12 10/02/2001 200 <1 <1 200 ‐‐ 13 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 24 <1.1 520 700 57

MW‐12 11/06/2001 220 <1 <1 220 ‐‐ 16 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 28 <1.1 560 740 62

MW‐12 12/05/2001 220 <1 <1 220 ‐‐ 16 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 25 1.1 560 770 64

MW‐12 01/04/2002 220 <1 <1 220 ‐‐ 15 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 26 1.9 610 800 67

MW‐12 02/05/2002 210 <1 <1 210 ‐‐ 16 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 25 <1.1 530 760 57

MW‐12 03/05/2002 210 <1 <1 210 ‐‐ 15 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 25 3.5 550 730 53

MW‐12 04/03/2002 220 <1 <1 220 ‐‐ 17 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 24 <1.1 560 760 55

MW‐12 05/07/2002 210 <1 <1 210 ‐‐ 14 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27 3.1 550 720 51

MW‐12 06/04/2002 210 <1 <1 210 ‐‐ 13 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27 <1.1 520 730 51

MW‐12 07/02/2002 200 <1 <1 200 ‐‐ 13 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 <1.1 540 760 57

MW‐12 08/10/2002 190 <1 <1 190 ‐‐ 13 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 <1.1 540 710 47

MW‐12 09/05/2002 140 <1 <1 140 ‐‐ 12 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 <1.1 620 730 62

MW‐12 10/09/2002 150 <1 <1 150 ‐‐ 15 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 540 710 71

MW‐12 11/06/2002 200 <1 <1 200 ‐‐ 14 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 1.2 600 790 67

MW‐12 12/03/2002 200 <1 <1 200 ‐‐ 13 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 <1.1 590 790 68

MW‐12 01/06/2003 180 <1 <1 180 ‐‐ 15 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 1.2 770 790 65

MW‐12 02/04/2003 200 <1 <1 200 ‐‐ 17 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 <1.1 650 800 65

MW‐12 03/04/2003 190 <1 <1 190 ‐‐ 17 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 <1.1 680 810 68

MW‐12 04/01/2003 180 <1 <1 180 ‐‐ 18 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 <1.1 650 830 74

MW‐12 05/01/2003 170 <1 <1 170 ‐‐ 20 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 39 <1.1 640 810 75

MW‐12 06/03/2003 140 <1 <1 140 ‐‐ 24 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 1.7 610 750 71

MW‐12 07/01/2003 140 <1 <1 140 ‐‐ 25 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 37 <1.1 630 770 72

MW‐12 08/05/2003 140 <1 <1 140 ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 <1.1 590 770 70

MW‐12 09/04/2003 350 <1 <1 350 ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 1.3 600 840 60

Page 50 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐12 10/01/2003 220 <1 <1 220 ‐‐ 30 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 <1.1 650 860 58

MW‐12 11/04/2003 220 <1 <1 220 ‐‐ 29 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 1.2 630 820 52

MW‐12 12/02/2003 220 <1 <1 220 ‐‐ 30 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 570 840 56

MW‐12 01/13/2004 220 <1 <1 220 ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1.1 680 840 62

MW‐12 02/04/2004 200 <1 <1 200 ‐‐ 28 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1 580 820 65

MW‐12 03/02/2004 230 <1 <1 230 ‐‐ 26 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1 640 860 67

MW‐12 04/06/2004 210 <1 <1 210 ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1 630 830 67

MW‐12 05/11/2004 200 <1 <1 200 ‐‐ 26 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1 600 830 58

MW‐12 06/01/2004 180 <1 <1 180 ‐‐ 26 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 56 2 690 970 57

MW‐12 07/06/2004 160 <1 <1 160 ‐‐ 23 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 <1 620 790 47

MW‐12 08/05/2004 170 <1 <1 170 ‐‐ 21 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 37 <1 590 770 43

MW‐12 09/02/2004 170 <1 <1 170 ‐‐ 24 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 40 2 570 790 41

MW‐12 10/05/2004 180 <1 <1 180 ‐‐ 25 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 1 560 760 38

MW‐12 11/02/2004 200 <1 <1 200 ‐‐ 25 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 2 580 750 36

MW‐12 12/01/2004 180 <1 <1 180 ‐‐ 26 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1 620 800 39

MW‐12 01/12/2005 230 <1 <1 230 ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 1 620 820 43

MW‐12 02/01/2005 200 <1 <1 200 ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1 580 820 44

MW‐12 03/08/2005 250 <1 <1 250 ‐‐ 25 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1 680 830 45

MW‐12 04/05/2005 210 <1 <1 210 ‐‐ 22 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1 620 780 39

MW‐12 05/04/2005 190 <1 <1 190 ‐‐ 22 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1 570 750 37

MW‐12 06/02/2005 200 <1 <1 200 ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 39 <1 590 830 41

MW‐12 07/20/2005 180 <1 <1 180 ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 <1 570 810 39

MW‐12 08/03/2005 200 <1 <1 200 ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 <1 690 840 39

MW‐12 09/07/2005 210 <1 <1 210 ‐‐ 35 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1 720 840 38

MW‐12 10/04/2005 220 <1 <1 220 ‐‐ 43 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 <1 680 910 42

MW‐12 11/09/2005 220 <1 <1 220 ‐‐ 45 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 37 1 700 910 44

MW‐12 12/06/2005 230 <1 <1 230 ‐‐ 60 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 43 <1 750 990 42

MW‐12 01/04/2006 240 <1 <1 240 ‐‐ 63 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 41 2 750 1000 47

MW‐12 02/06/2006 190 <1 <1 190 ‐‐ 69 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 51 <1 740 1100 47

MW‐12 03/15/2006 230 <1 <1 230 ‐‐ 56 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 45 1.4 750 1100 46

MW‐12 08/03/2006 220 <5.0 <5.0 220 ‐‐ 66 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.95 840 1020 45

MW‐12 09/05/2006 250 <5.0 <5.0 250 ‐‐ 64 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.8 800 1030 45

MW‐12 10/09/2006 270 <5.0 <5.0 270 ‐‐ 71 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.97 740 1020 48

MW‐12 11/06/2006 270 <5.0 <5.0 270 ‐‐ 80 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.0 890 1010 49

MW‐12 12/11/2006 230 <5.0 <5.0 230 ‐‐ 74 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.87 780 978 40

Page 51 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐12 01/03/2007 210 <5 <5 210 ‐‐ 65 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.1 770 949 37

MW‐12 02/05/2007 250 <5 <5 250 ‐‐ 81 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.92 760 1000 42

MW‐12 03/05/2007 250 <5 <5 250 ‐‐ 90 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.79 840 1030 43

MW‐12 04/05/2007 260 <5 <5 260 ‐‐ 90 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.93 840 1070 44

MW‐12 05/03/2007 290 <5 <5 290 ‐‐ 100 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.1 850 1120 59

MW‐12 06/07/2007 280 <5 <5 280 ‐‐ 100 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.2 900 1160 58

MW‐12 07/02/2007 280 <5 <5 280 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.3 930 1190 62

MW‐12 08/02/2007 360 <10 <10 360 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.99 1300 1430 79

MW‐12 09/10/2007 310 <10 <10 310 ‐‐ 130 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.83 940 1240 64

MW‐12 10/08/2007 300 <10 <10 300 ‐‐ 130 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.94 970 1260 66

MW‐12 11/07/2007 340 <10 <10 340 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.87 1200 1320 74

MW‐12 12/06/2007 300 <5 <5 300 ‐‐ 110 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.98 950 1160 67

MW‐12 01/14/2008 300 <5 <5 300 ‐‐ 110 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.99 870 1080 64

MW‐12 02/07/2008 390 <5 <5 390 ‐‐ 110 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.85 930 1280 62

MW‐12 03/04/2008 310 <5 <5 310 ‐‐ 130 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.89 1000 1320 73

MW‐12 04/10/2008 330 <5 <5 330 ‐‐ 130 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.1 900 1270 72

MW‐12 05/05/2008 330 <5 <5 330 ‐‐ 110 150 <0.05 48 <0.01 3.3 48 ‐‐ ‐‐ ‐‐ 1.1 870 1290 76

MW‐12 06/03/2008 320 <5.0 <5.0 320 ‐‐ 120 150 <0.050 44 <0.010 Jo 3.1 47 ‐‐ ‐‐ ‐‐ 1.1 880 1230 72

MW‐12 07/01/2008 330 <5.0 <5.0 330 ‐‐ 140 160 <0.050 50 <0.010 Jo 3.0 46 ‐‐ ‐‐ ‐‐ 1.2 1000 1380 76

MW‐12 08/04/2008 330 <5.0 <5.0 330 ‐‐ 150 160 <0.050 48 <0.010 Jo 2.9 45 ‐‐ ‐‐ ‐‐ 0.8 1000 1470 83

MW‐12 09/08/2008 340 <5.0 <5.0 340 ‐‐ 150 180 <0.050 54 <0.010 Jo 3.2 53 ‐‐ ‐‐ ‐‐ 1.4 1100 1470 89

MW‐12 10/09/2008 300 <5.0 <5.0 300 ‐‐ 120 130 <0.050 40 <0.010 Jo 2.8 50 ‐‐ ‐‐ ‐‐ 1.5 850 1290 71

MW‐12 11/04/2008 310 <5.0 <5.0 310 ‐‐ 120 140 <0.050 42 0.012 3.2 55 ‐‐ ‐‐ ‐‐ 1.5 940 1290 72

MW‐12 12/03/2008 340 <5.0 <5.0 340 ‐‐ 150 170 <0.050 47 0.02 3.6 58 ‐‐ ‐‐ ‐‐ 1.3 1000 1410 91

MW‐12 01/13/2009 320 <8.2 <8.2 320 ‐‐ 130 150 <0.050 43 0.019 2.8 54 ‐‐ ‐‐ ‐‐ 1.5 1100 1260 84

MW‐12 02/04/2009 330 <8.2 <8.2 330 ‐‐ 140 180 <0.050 50 0.023 3.0 53 ‐‐ ‐‐ ‐‐ 1.4 1000 1410 86

MW‐12 03/04/2009 340 <8.2 <8.2 340 ‐‐ 120 160 <0.050 46 0.014 2.6 51 ‐‐ ‐‐ ‐‐ 1.1 900 1310 78

MW‐12 04/13/2009 320 <8.2 <8.2 320 ‐‐ 120 160 <0.050 46 0.018 2.8 54 ‐‐ ‐‐ ‐‐ 1.1 890 1240 78

MW‐12 05/04/2009 320 <8.2 <8.2 320 ‐‐ 110 140 <0.050 41 0.015 2.6 51 ‐‐ ‐‐ ‐‐ 1.3 880 1200 73

MW‐12 06/08/2009 310 <8.2 <8.2 310 ‐‐ 110 140 <0.05 40 0.015 2.5 55 ‐‐ ‐‐ ‐‐ 1.3 860 1190 77

MW‐12 07/13/2009 320 <8.2 <8.2 320 ‐‐ 120 160 <0.050 45 <0.010 Jo 2.6 55 ‐‐ ‐‐ ‐‐ 1.2 1000 1360 85

MW‐12 08/04/2009 330 <8.2 <8.2 330 ‐‐ 120 150 <0.05 Jo 45 0.024 2.5 57 ‐‐ ‐‐ ‐‐ 1.4 950 1300 84

MW‐12 09/08/2009 330 <8.2 <8.2 330 ‐‐ 120 170 <0.050 49 0.021 2.9 62 ‐‐ ‐‐ ‐‐ 1.3 960 1320 84

MW‐12 10/07/2009 310 <8.2 <8.2 310 ‐‐ 100 140 <0.050 42 <0.010 Jo 2.3 55 ‐‐ ‐‐ ‐‐ 0.96 820 1180 73

MW‐12 11/09/2009 320 <8.2 <8.2 320 ‐‐ 85 120 <0.050 37 0.02 2.7 53 ‐‐ ‐‐ ‐‐ 1.2 770 1090 59

Page 52 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐12 12/08/2009 300 <4.1 <4.1 300 ‐‐ 74 110 <0.050 32 0.015 2.4 55 ‐‐ ‐‐ ‐‐ 0.85 680 945 64

MW‐12 01/05/2010 320 <4.1 <4.1 320 ‐‐ 86 120 <0.050 35 0.015 2.6 58 ‐‐ ‐‐ ‐‐ 0.95 750 1110 65

MW‐12 02/11/2010 300 <8.2 <8.2 300 ‐‐ 79 120 <0.050 35 0.014 3.4 65 ‐‐ ‐‐ ‐‐ 0.71 730 1050 65

MW‐12 03/08/2010 310 <8.2 <8.2 310 ‐‐ 89 120 <0.050 34 0.016 2.4 64 ‐‐ ‐‐ ‐‐ 0.99 770 1040 71

MW‐12 04/15/2010 320 <8.2 ‐‐ 320 ‐‐ 86 120 <0.05 35 0.016 2.5 70 ‐‐ ‐‐ ‐‐ 0.76 730 1110 64

MW‐12 07/08/2010 310 <8.2 ‐‐ 310 ‐‐ 93 130 <0.05 37 <0.01 Jo 2.4 62 ‐‐ ‐‐ ‐‐ 0.92 780 1150 74

MW‐12 10/27/2010 330 <8.2 ‐‐ 330 ‐‐ 99 140 <0.05 Jo 40 0.024 2.7 75 0.059 ‐‐ ‐‐ 0.98 940 1280 71

MW‐12 01/19/2011 320 <8.2 ‐‐ 320 ‐‐ 84 120 <0.05 36 <0.01 Jo 2.7 64 ‐‐ ‐‐ ‐‐ 0.92 900 1140 70

MW‐12 04/04/2011 350 <8.2 ‐‐ 350 ‐‐ 94 140 <0.05 40 0.011 3.2 81 ‐‐ ‐‐ ‐‐ 0.94 880 1290 72

MW‐12 07/07/2011 320 <8.2 ‐‐ 320 ‐‐ 78 120 <0.05 33 0.022 3.4 77 ‐‐ ‐‐ 23 0.83 780 1080 57

MW‐12 10/04/2011 340 <8.2 ‐‐ 340 ‐‐ 100 140 <0.05 38 0.014 3.4 93 ‐‐ ‐‐ 42 1.2 960 1340 81

MW‐12 01/18/2012 350 <8.2 ‐‐ 350 ‐‐ 81 130 <0.05 Jo 36 0.032 4.0 86 ‐‐ ‐‐ 33 0.99 860 1250 71

MW‐12 04/04/2012 340 <8.2 ‐‐ 340 ‐‐ 85 130 <0.05 34 0.029 3.4 72 ‐‐ ‐‐ 22 0.95 810 1140 77

MW‐12 07/23/2012 330 <8.2 ‐‐ 330 ‐‐ 82 120 <0.05 Jo 34 <0.01 Jo 3.2 86 ‐‐ ‐‐ 26 0.83 810 1190 86

MW‐12 10/16/2012 340 <8.2 ‐‐ 340 ‐‐ 89 130 <0.05 Jo 33 0.022 4.3 84 ‐‐ ‐‐ 18 0.84 820 1130 83

MW‐12 01/22/2013 370 <8.2 ‐‐ 370 ‐‐ 86 150 <0.05 39 0.011 3.7 110 ‐‐ ‐‐ 34 1.0 980 1410 150

MW‐12 04/18/2013 320 <8.2 ‐‐ 320 ‐‐ 100 120 <0.05 Jo 31 0.027 4.6 86 ‐‐ ‐‐ 20 0.6 790 1100 80

MW‐12 07/17/2013 350 <8.2 ‐‐ 350 ‐‐ 110 130 <0.05 35 0.054 4.9 85 ‐‐ ‐‐ 20 0.99 840 1240 75

MW‐12 10/21/2013 360 <8.2 ‐‐ 360 ‐‐ 120 120 <0.05 32 0.042 4.3 88 ‐‐ ‐‐ 19 0.76 660 1270 84

MW‐12 01/22/2014 350 <8.2 ‐‐ 350 ‐‐ 99 130 <0.05 Jo 36 <0.01 Jo 3.9 110 ‐‐ ‐‐ 27 0.87 870 1270 85

MW‐12 04/22/2014 370 <8.2 ‐‐ 370 ‐‐ 120 130 <0.05 39 0.015 4.5 95 ‐‐ ‐‐ 28 0.89 940 1470 79

MW‐12 07/21/2014 360 <8.2 ‐‐ 360 ‐‐ 120 140 <0.05 50 0.019 5.6 100 ‐‐ ‐‐ 31 0.67 1000 1520 100

MW‐12 10/20/2014 340 <8.2 ‐‐ 340 ‐‐ 120 140 <0.05 47 0.024 5.8 100 ‐‐ ‐‐ 24 0.85 820 1370 86

MW‐12 01/21/2015 350 <8.2 ‐‐ 350 ‐‐ 130 130 <0.05 39 <0.01 Jo 4.4 94 ‐‐ ‐‐ 29 0.9 920 1420 94

MW‐12 04/15/2015 380 <8.2 ‐‐ 380 ‐‐ 130 160 <0.05 51 0.019 5.2 110 ‐‐ ‐‐ 38 0.82 1000 1510 97

MW‐12 07/22/2015 380 <8.2 ‐‐ 380 ‐‐ 160 150 <0.05 47 0.077 6.6 98 ‐‐ ‐‐ 19 0.39 920 1530 82

MW‐12 10/15/2015 380 <8.2 ‐‐ 380 ‐‐ 170 130 <0.05 49 0.067 6.0 95 ‐‐ ‐‐ 22 0.69 1000 1430 91

MW‐12 01/20/2016 360 <8.2 ‐‐ 360 ‐‐ 170 130 <0.05 Jo 50 0.078 6.4 92 ‐‐ ‐‐ 20 0.74 950 1470 90

MW‐12 04/14/2016 370 <8.2 ‐‐ 370 ‐‐ 150 140 <0.05 54 0.053 6.5 98 ‐‐ ‐‐ 23 0.75 950 1470 85

MW‐12 07/18/2016 360 <8.2 ‐‐ 360 ‐‐ 150 150 <0.05 52 0.071 6.2 110 ‐‐ ‐‐ 31 0.66 1000 1500 90

MW‐12 10/12/2016 320 <8.2 ‐‐ 320 ‐‐ 140 150 <0.05 48 0.023 6.2 120 ‐‐ ‐‐ 43 0.46 980 1500 92

MW‐13 01/20/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐

MW‐13 02/09/1998 200 <1 <1 200 ‐‐ 9.6 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 25 <1.1 450 630 27

MW‐13 03/19/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 1.4 550 690 ‐‐

MW‐13 04/29/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 22 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 65 6.6 780 980 ‐‐

Page 53 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐13 05/20/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 15 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 65 1.6 690 860 ‐‐

MW‐13 06/16/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 1.3 510 660 ‐‐

MW‐13 07/28/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.8 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 25 <1.1 430 570 ‐‐

MW‐13 08/21/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.5 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 <1.1 490 540 ‐‐

MW‐13 09/24/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.8 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 41 <1.1 550 690 ‐‐

MW‐13 10/22/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.4 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1.1 480 650 ‐‐

MW‐13 11/25/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.7 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 470 590 ‐‐

MW‐13 12/15/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.9 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 <1.1 480 580 ‐‐

MW‐13 02/16/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 <1.1 460 610 ‐‐

MW‐13 05/23/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 14 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 <1.1 950 630 ‐‐

MW‐13 08/23/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 <1.1 480 650 ‐‐

MW‐13 11/22/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 21 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 43 <1.1 730 920 ‐‐

MW‐13 02/17/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 18 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 25 <1.1 520 680 ‐‐

MW‐13 05/02/2000 190 <1 <1 190 ‐‐ 19 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 <1.1 600 790 44

MW‐13 08/08/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 22 <1.1 490 640 ‐‐

MW‐13 09/21/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.7 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 <1.1 480 550 ‐‐

MW‐13 11/30/2000 180 <1 <1 180 ‐‐ 21 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 570 770 ‐‐

MW‐13 12/15/2000 190 <1 <1 190 ‐‐ 22 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.8 <1.1 590 780 ‐‐

MW‐13 01/07/2001 190 <1 <1 190 ‐‐ 22 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 580 760 ‐‐

MW‐13 02/08/2001 180 <1 <1 180 ‐‐ 21 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 ‐‐ 640 790 47

MW‐13 03/20/2001 160 <1 <1 160 ‐‐ 23 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 2.1 600 750 43

MW‐13 04/17/2001 160 <1 <1 160 ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 <1.1 610 770 44

MW‐13 05/22/2001 170 <1 <1 170 ‐‐ 24 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 43 <1.1 670 820 50

MW‐13 06/25/2001 220 <1 <1 220 ‐‐ 34 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1.1 580 800 48

MW‐13 07/19/2001 210 <1 <1 210 ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 23 <1.1 500 750 46

MW‐13 08/03/2001 220 <1 <1 220 ‐‐ 88 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 25 <1.1 610 920 40

MW‐13 09/06/2001 240 <1 <1 240 ‐‐ 90 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 18 1.8 690 960 37

MW‐13 10/03/2001 230 <1 <1 230 ‐‐ 89 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 24 2.3 770 1000 37

MW‐13 11/06/2001 290 <1 <1 290 ‐‐ 68 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 21 <1.1 640 890 26

MW‐13 12/05/2001 210 <1 <1 210 ‐‐ 72 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 22 <1.1 600 880 33

MW‐13 01/06/2002 210 <1 <1 210 ‐‐ 79 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 24 9 610 890 39

MW‐13 02/07/2002 150 <1 <1 150 ‐‐ 89 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 56 <1.1 770 1100 42

MW‐13 03/08/2002 220 <1 <1 220 ‐‐ 100 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 <1.1 810 1000 35

MW‐13 04/03/2002 220 <1 <1 220 ‐‐ 100 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 40 <1.1 790 1100 40

MW‐13 05/09/2002 280 <1 <1 280 ‐‐ 78 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 <1.1 830 1100 37

Page 54 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐13 10/09/2002 380 <1 <1 380 ‐‐ 51 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 18 <1.1 730 1000 32

MW‐13 11/07/2002 990 <1 <1 990 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.3 <1.1 1400 2100 29

MW‐13 12/06/2002 1500 <1 <1 1500 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.8 2.7 2200 3000 21

MW‐13 01/07/2003 1700 <1 <1 1700 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.7 2.9 2300 3200 15

MW‐13 02/04/2003 1400 <1 <1 1400 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 2.7 2100 3000 78

MW‐13 03/04/2003 1400 <1 <1 1400 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.2 2.4 2000 2900 50

MW‐13 04/03/2003 1200 <1 <1 1200 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.8 2.9 2000 2900 120

MW‐13 05/01/2003 1300 <1 <1 1300 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.5 2 1900 2700 23

MW‐13 06/03/2003 ‐‐ <1 <1 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐

MW‐13 10/05/2004 1500 <1 <1 1500 ‐‐ 370 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 3 2400 3400 24

MW‐13 11/02/2004 1300 <1 <1 1300 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 2 2100 3100 21

MW‐13 12/01/2004 1300 <1 <1 1300 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.4 2 2000 3000 13

MW‐13 01/12/2005 1200 <1 <1 1200 ‐‐ 410 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 <1 2100 3100 14

MW‐13 02/01/2005 1000 <1 <1 1000 ‐‐ 780 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 3 2600 3700 4.3

MW‐13 03/09/2005 1200 <1 <1 1200 ‐‐ 740 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.3 3 2400 3700 14

MW‐13 04/06/2005 1100 <1 <1 1100 ‐‐ 660 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.6 3 2400 3600 31

MW‐13 05/06/2005 1000 <1 <1 1000 ‐‐ 720 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.2 3 2600 3700 23

MW‐13 06/06/2005 1000 <1 <1 1000 ‐‐ 730 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 2.7 2500 3800 34

MW‐13 07/22/2005 880 <1 <1 880 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 3 1700 2600 36

MW‐13 08/05/2005 900 <1 <1 900 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.8 1 1700 2400 13

MW‐13 09/06/2005 930 <1 <1 930 ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.2 2 1600 2400 17

MW‐13 10/05/2005 980 <1 <1 980 ‐‐ 500 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 10 2 2100 3200 80

MW‐13 11/11/2005 950 <1 <1 950 ‐‐ 440 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.5 4 2000 3200 100

MW‐13 12/08/2005 970 <1 <1 970 ‐‐ 380 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.9 2.1 2200 3200 97

MW‐13 01/05/2006 1000 <1 <1 1000 ‐‐ 480 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.5 3 2200 3300 97

MW‐13 02/06/2006 1000 <1 <1 1000 ‐‐ 530 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.9 3 1900 3400 99

MW‐13 03/15/2006 1100 <1 <1 1100 ‐‐ 750 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 83 1.8 3200 4600 150

MW‐13 08/03/2006 990 <10 <10 990 ‐‐ 410 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.3 2100 3180 140

MW‐13 09/05/2006 940 <10 <10 940 ‐‐ 330 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.7 2000 2980 240

MW‐13 10/09/2006 1000 <10 <10 1000 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.4 1800 2800 130

MW‐13 11/06/2006 1100 <10 <10 1100 ‐‐ 300 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.8 2000 2750 110

MW‐13 12/11/2006 1100 <20 <20 1100 ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.1 1900 2870 120

MW‐13 01/03/2007 1100 <20 <20 1100 ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.7 1900 2880 120

MW‐13 02/05/2007 1000 <10 <10 1000 ‐‐ 280 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.2 1800 2670 120

MW‐13 03/05/2007 1100 <20 <20 1100 ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4 2000 2860 140

Page 55 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐13 04/05/2007 1400 <20 <20 1400 ‐‐ 320 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.2 2000 3300 93

MW‐13 05/03/2007 1500 <20 <20 1500 ‐‐ 440 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 10 2700 3950 130

MW‐13 06/07/2007 1600 <20 <20 1600 ‐‐ 330 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11 2500 3860 76

MW‐13 07/02/2007 1500 <20 <20 1500 ‐‐ 350 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11 2300 3640 62

MW‐13 08/02/2007 1400 <20 <20 1400 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5 2300 3530 81

MW‐13 09/10/2007 1100 <10 <10 1100 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.9 2700 3890 96

MW‐13 10/08/2007 980 <10 <10 980 ‐‐ 350 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.6 2700 3820 95

MW‐13 11/07/2007 1100 <20 <20 1100 ‐‐ 360 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.1 2800 3840 100

MW‐13 12/06/2007 1000 <10 <10 1000 ‐‐ 330 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.4 2600 3650 96

MW‐13 01/14/2008 960 <10 <10 960 ‐‐ 370 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.64 2800 3700 130

MW‐13 02/07/2008 1100 <20 <20 1100 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.6 2600 3770 130

MW‐13 03/04/2008 1300 <20 <20 1300 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2 2400 3580 100

MW‐13 04/10/2008 1300 <20 <20 1300 ‐‐ 410 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.3 2400 3610 110

MW‐13 05/05/2008 1200 <20 <20 1200 ‐‐ 400 93 0.59 14 4.5 200 620 ‐‐ ‐‐ ‐‐ 2.3 2400 3800 150

MW‐13 06/03/2008 1200 <20 <20 1200 ‐‐ 460 94 0.64 16 3.6 200 710 ‐‐ ‐‐ ‐‐ 2.2 2800 3950 160

MW‐13 07/01/2008 1300 <20 <20 1300 ‐‐ 480 95 0.62 17 3.9 210 730 ‐‐ ‐‐ ‐‐ 2.6 2700 4220 150

MW‐13 08/04/2008 1200 <20 <20 1200 ‐‐ 360 60 0.38 13 2.5 160 580 ‐‐ ‐‐ ‐‐ 1.7 2400 3610 59

MW‐13 09/08/2008 1300 <20 <20 1300 ‐‐ 370 67 0.47 19 3.2 180 690 ‐‐ ‐‐ ‐‐ 2.1 2400 3690 76

MW‐13 10/09/2008 1300 <20 <20 1300 ‐‐ 390 60 0.44 18 3.1 160 620 ‐‐ ‐‐ ‐‐ 2.0 2300 3630 74

MW‐13 11/04/2008 1400 <20 <20 1400 ‐‐ 420 76 0.29 20 2.7 190 710 ‐‐ ‐‐ ‐‐ 2.0 2500 3810 86

MW‐13 12/03/2008 1400 <20 <20 1400 ‐‐ 450 69 0.31 19 3.5 170 670 ‐‐ ‐‐ ‐‐ 1.8 2500 3810 97

MW‐13 01/13/2009 1300 <8.2 <8.2 1300 ‐‐ 430 72 0.4 22 4.0 180 730 ‐‐ ‐‐ ‐‐ 2.1 2600 3770 100

MW‐13 02/04/2009 1200 <8.2 <8.2 1200 ‐‐ 460 85 0.4 23 3.2 200 750 ‐‐ ‐‐ ‐‐ 1.9 2900 4020 110

MW‐13 03/04/2009 1200 <8.2 <8.2 1200 ‐‐ 490 81 0.34 22 3.0 190 760 ‐‐ ‐‐ ‐‐ 1.9 2800 3270 120

MW‐13 04/14/2009 1200 <8.2 <8.2 1200 ‐‐ 540 92 0.25 27 3.4 200 920 ‐‐ ‐‐ ‐‐ 2.0 3000 4370 120

MW‐13 05/04/2009 1100 <8.2 <8.2 1100 ‐‐ 560 84 0.16 25 2.7 190 850 ‐‐ ‐‐ ‐‐ 2.3 3200 4540 110

MW‐13 06/08/2009 1200 <8.2 <8.2 1200 ‐‐ 450 65 0.063 19 1.9 170 800 ‐‐ ‐‐ ‐‐ 1.8 2800 4080 79

MW‐13 07/14/2009 1400 <8.2 <8.2 1400 ‐‐ 410 63 0.059 19 1.8 170 800 ‐‐ ‐‐ ‐‐ 1.8 2900 4130 60

MW‐13 08/04/2009 1400 <8.2 <8.2 1400 ‐‐ 390 60 0.062 18 1.7 150 780 ‐‐ ‐‐ ‐‐ 1.5 2900 4050 53

MW‐13 08/13/2009 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 410 ‐‐ ‐‐ ‐‐ ‐‐ 150 820 ‐‐ ‐‐ ‐‐ ‐‐ 2600 4000 ‐‐

MW‐13 09/08/2009 1500 <16 <16 1500 ‐‐ 410 66 0.075 20 1.8 170 790 ‐‐ ‐‐ ‐‐ 1.3 2600 4100 55

MW‐13 10/07/2009 1400 <8.2 <8.2 1400 ‐‐ 470 62 0.06 20 2.0 160 820 ‐‐ ‐‐ ‐‐ 1.2 3100 4100 57

MW‐13 11/09/2009 1500 <8.2 <8.2 1500 ‐‐ 480 60 <0.050 Jo 19 1.5 170 800 ‐‐ ‐‐ ‐‐ 1.3 2900 4210 55

MW‐13 12/08/2009 1500 <8.2 <8.2 1500 ‐‐ 510 62 <0.050 Jo 18 1.4 180 800 ‐‐ ‐‐ ‐‐ 0.97 3000 4290 60

MW‐13 01/05/2010 1500 <4.1 <4.1 1500 ‐‐ 540 69 <0.050 Jo 19 1.2 200 960 ‐‐ ‐‐ ‐‐ 1.0 3000 4490 62

Page 56 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐13 02/10/2010 1500 <8.2 <8.2 1500 ‐‐ 740 90 <0.050 Jo 24 1.1 210 1000 ‐‐ ‐‐ ‐‐ 0.94 3800 5180 120

MW‐13 03/08/2010 1500 <8.2 <8.2 1500 ‐‐ 820 92 <0.050 Jo 25 1.2 200 1100 ‐‐ ‐‐ ‐‐ 1.3 3700 5660 140

MW‐13 04/15/2010 1500 <8.2 ‐‐ 1500 ‐‐ 690 90 <0.1 Jo 23 1.2 200 1100 ‐‐ ‐‐ ‐‐ 0.78 3200 5120 120

MW‐13 07/08/2010 1500 <8.2 ‐‐ 1500 ‐‐ 740 87 <0.05 Jo 24 1.4 200 1100 ‐‐ ‐‐ ‐‐ 0.95 3500 5230 110

MW‐13 10/27/2010 800 <8.2 ‐‐ 800 ‐‐ 510 58 <0.05 Jo 14 1.2 160 790 0.03 ‐‐ ‐‐ 1.0 3400 4340 130

MW‐13 01/19/2011 880 <8.2 ‐‐ 880 ‐‐ 520 59 <0.05 Jo 16 1 150 770 ‐‐ ‐‐ ‐‐ 0.46 3400 4320 140

MW‐13 04/04/2011 1200 <8.2 ‐‐ 1200 ‐‐ 600 71 <0.05 Jo 21 0.9 160 880 ‐‐ ‐‐ ‐‐ 0.58 3300 4750 120

MW‐13 07/07/2011 960 <8.2 ‐‐ 960 ‐‐ 590 88 <0.05 Jo 25 1.6 200 900 ‐‐ ‐‐ 150 1.1 3500 4870 140

MW‐13 11/09/2011 486 J <5.0 ‐‐ 486 J <5.0 J‐ 586 103 J <0.20 30.2 J 2.11 J 222 807 J 0.052 ‐‐ 159 <0.20 3120 4920 148

MW‐13 01/19/2012 560 ‐‐ ‐‐ 560 2.0 300 27 <0.050 Jo 7.8 0.51 99 480 0.053 ‐‐ 64 0.88 1700 2580 70

MW‐13 04/03/2012 486 <5.0 ‐‐ 486 <1.0 <197 U 17.8 <0.20 5.07 0.262 77.6 341 0.046 ‐‐ 51.4 <0.26 1240 1950 <71.5 U

MW‐13 07/24/2012 666 <5.0 ‐‐ 666 <0.50 139 27.9 <0.20 7.48 J+ 0.384 112 402 0.046 ‐‐ 51.3 <0.20 1330 2100 39.2

MW‐13 10/15/2012 392 <5.0 ‐‐ 392 <0.50 202 12.4 J <0.20 <5.0 0.302 J 78.6 J 286 J 0.043 ‐‐ 13.5 1.8 J 940 1670 <27.0 U

MW‐13 01/22/2013 628 <5.0 ‐‐ 628 0.62 383 40.9 <0.20 11.7 0.112 109 475 0.028 ‐‐ 55.0 <0.20 1690 2410 71.5

MW‐13 04/16/2013 406 <5.0 ‐‐ 406 <0.50 232 17.6 <0.20 <5.0 0.101 88.8 350 0.03 ‐‐ 50.6 <0.20 1260 1910 59.2

MW‐13 07/17/2013 327 <5.0 ‐‐ 327 <0.50 130 12.7 <0.20 <5.0 0.158 92.4 J 231 0.023 ‐‐ 30.4 <0.20 910 1550 32.4

MW‐13 10/21/2013 260 <5.0 ‐‐ 260 ‐‐ 53.1 12.8 J <0.20 <5.0 0.201 111 105 J ‐‐ ‐‐ 14.7 <0.20 561 948 22.2

MW‐13 01/22/2014 334 <5.0 ‐‐ 334 ‐‐ 95.7 17.8 <0.20 <5.0 0.115 114 147 ‐‐ ‐‐ 16.9 <3.6 U 740 969 25.4

MW‐13 04/22/2014 256 <5.0 ‐‐ 256 ‐‐ 52.9 13.3 <0.20 <5.0 0.167 113 J 107 J ‐‐ ‐‐ 22.2 <0.99 U 590 956 19.2

MW‐13 10/20/2014 414 <5.0 ‐‐ 414 ‐‐ 93.7 <5.0 <0.20 <5.0 <0.015 <10 <10 ‐‐ ‐‐ 17.3 0.45 863 1280 29.2

MW‐13 04/15/2015 505 <5.0 ‐‐ 505 ‐‐ 137 65.1 J <0.20 26.2 J <0.015 183 J 155 J ‐‐ ‐‐ 25.8 0.51 J 1070 1450 49.2

MW‐13 04/14/2016 430 <5.0 ‐‐ 430 ‐‐ 200 49.6 <0.20 15.4 <0.015 110 353 J ‐‐ ‐‐ 88.5 <0.20 1550 2420 76.6

MW‐13 10/12/2016 285 <5.0 ‐‐ 288 ‐‐ 120 42.2 <0.3 15.6 <0.015 154 J 134 ‐‐ ‐‐ 43 <0.53 R 853 1270 37

MW‐15 01/20/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.2 ‐‐ ‐‐ ‐‐ ‐‐

MW‐15 02/09/1998 170 <1 <1 170 ‐‐ 12 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.3 2 530 470 22

MW‐15 03/19/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 110 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.18 1.6 1700 1800 ‐‐

MW‐15 04/29/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 460 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 41 5.7 1700 2900 ‐‐

MW‐15 05/20/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 390 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.9 5.4 1500 2300 ‐‐

MW‐15 06/16/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 610 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 25 9.5 2400 3400 ‐‐

MW‐15 07/28/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 720 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 90 21 3300 4900 ‐‐

MW‐15 08/21/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 460 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 45 7.8 2100 3100 ‐‐

MW‐15 09/24/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 640 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 14 2400 3600 ‐‐

MW‐15 10/22/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 18 21 2400 3000 ‐‐

MW‐15 11/25/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 390 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9 12 2100 3000 ‐‐

MW‐15 12/15/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.8 21 2200 2500 ‐‐

Page 57 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐15 02/16/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 14 2400 2900 ‐‐

MW‐15 05/23/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1 99 1800 2800 ‐‐

MW‐15 08/23/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 350 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 8 1800 2700 ‐‐

MW‐15 11/22/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.14 5.7 1700 2500 ‐‐

MW‐15 02/17/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.2 19 2500 3100 ‐‐

MW‐15 05/02/2000 1200 <1 <1 1200 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.14 10 1900 2800 17

MW‐15 08/08/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 5.7 1300 2000 ‐‐

MW‐15 09/13/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 210 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 5.4 1200 1800 ‐‐

MW‐15 11/30/2000 770 <1 <1 770 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 6.9 1500 2400 ‐‐

MW‐15 12/15/2000 810 <1 <1 810 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 5.9 1600 2400 ‐‐

MW‐15 01/07/2001 790 <1 <1 790 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 6.6 1600 2300 ‐‐

MW‐15 02/07/2001 820 <1 <1 820 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 ‐‐ 1800 2400 28

MW‐15 03/28/2001 870 <1 <1 870 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 12 1600 2300 8

MW‐15 04/17/2001 950 <1 <1 950 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 85 1500 2400 4

MW‐15 05/22/2001 1000 <1 <1 1000 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 16 1800 2600 18

MW‐15 06/27/2001 510 <1 <1 510 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.5 3.5 1300 2000 100

MW‐15 07/19/2001 380 <1 <1 380 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.6 2.4 1000 1500 81

MW‐15 08/03/2001 250 <1 <1 250 ‐‐ 80 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 2.6 690 1100 67

MW‐15 09/06/2001 140 <1 <1 140 ‐‐ 22 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 2.1 460 610 43

MW‐15 10/03/2001 110 <1 <1 110 ‐‐ 16 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 21 3.1 440 570 43

MW‐15 11/08/2001 200 <1 <1 200 ‐‐ 58 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 1.7 520 810 46

MW‐15 12/05/2001 410 <1 <1 410 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11 6.2 1000 1500 93

MW‐15 01/06/2002 540 <1 <1 540 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 23 5.4 1400 2100 170

MW‐15 02/04/2002 1100 <1 <1 1100 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.4 5.3 1800 2800 120

MW‐15 03/05/2002 1700 <1 <1 1700 ‐‐ 180 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5 11 2700 3800 92

MW‐15 04/03/2002 1600 <1 <1 1600 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.6 23 2200 3400 15

MW‐15 05/09/2002 620 <1 <1 620 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 22 5.6 1600 2400 190

MW‐15 06/05/2002 570 <1 <1 570 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 23 5.2 1500 2100 120

MW‐15 07/03/2002 240 <1 <1 240 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 2.4 1000 1500 83

MW‐15 08/06/2002 290 <1 <1 290 ‐‐ 50 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 2.4 720 1000 45

MW‐15 09/06/2002 140 <1 <1 140 ‐‐ 36 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 20 2.2 650 750 39

MW‐15 10/10/2002 250 <1 <1 250 ‐‐ 72 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 18 2.1 760 990 56

MW‐15 11/07/2002 210 <1 <1 210 ‐‐ 45 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 2.1 600 800 41

MW‐15 12/05/2002 340 <1 <1 340 ‐‐ 86 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 14 2.7 820 1200 69

MW‐15 01/07/2003 450 <1 <1 450 ‐‐ 94 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.2 3 1100 1500 88

Page 58 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐15 02/05/2003 620 <1 <1 620 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 4 1400 2000 130

MW‐15 03/06/2003 960 <1 <1 960 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 5.9 1700 2400 17

MW‐15 04/03/2003 1200 <1 <1 1200 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.1 13 1900 2700 4

MW‐15 05/01/2003 660 <1 <1 660 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 5.2 1300 2000 54

MW‐15 06/05/2003 410 <1 <1 410 ‐‐ 110 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 4.3 1300 1800 93

MW‐15 07/03/2003 300 <1 <1 300 ‐‐ 91 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 41 2.3 1100 1500 62

MW‐15 08/07/2003 110 <1 <1 110 ‐‐ 19 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 24 2.3 540 630 41

MW‐15 09/06/2003 92 <1 <1 92 ‐‐ 17 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 1.5 400 430 17

MW‐15 10/02/2003 76 <1 <1 76 ‐‐ 23 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 <1.1 380 470 19

MW‐15 11/05/2003 87 <1 <1 87 ‐‐ 22 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 <1.1 370 480 19

MW‐15 12/03/2003 100 <1 <1 100 ‐‐ 20 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 10 2.3 450 480 24

MW‐15 01/14/2004 240 <1 <1 240 ‐‐ 42 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.8 1.7 540 800 40

MW‐15 02/05/2004 270 <1 <1 270 ‐‐ 56 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.5 1 620 900 43

MW‐15 03/03/2004 350 <1 <1 350 ‐‐ 73 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4 2 760 1100 41

MW‐15 04/08/2004 590 <1 <1 590 ‐‐ 200 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 15 4 1300 2000 41

MW‐15 05/13/2004 520 <1 <1 520 ‐‐ 220 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 20 3 1500 2200 150

MW‐15 06/04/2004 450 <1 <1 450 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 15 3 1200 1700 66

MW‐15 07/09/2004 440 <1 <1 440 ‐‐ 86 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 15 4 1300 1500 76

MW‐15 08/06/2004 290 <1 <1 290 ‐‐ 85 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 43 2 1100 1400 63

MW‐15 09/07/2004 100 <1 <1 100 ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 21 <1 550 600 32

MW‐15 10/05/2004 130 <1 <1 130 ‐‐ 50 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 2 640 850 35

MW‐15 11/02/2004 240 <1 <1 240 ‐‐ 42 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.8 3 730 850 31

MW‐15 12/01/2004 260 <1 <1 260 ‐‐ 53 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.8 2 710 930 42

MW‐15 01/12/2005 380 <1 <1 380 ‐‐ 78 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.5 2 860 1200 48

MW‐15 02/01/2005 310 <1 <1 310 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 22 2 1200 1800 61

MW‐15 03/08/2005 290 <1 <1 290 ‐‐ 390 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.5 2 1200 2000 62

MW‐15 04/05/2005 290 <1 <1 290 ‐‐ 390 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.3 5 1300 2100 54

MW‐15 05/04/2005 280 <1 <1 280 ‐‐ 440 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 58 1.7 1800 2800 120

MW‐15 06/02/2005 300 <1 <1 300 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 56 1.7 1600 2400 81

MW‐15 07/22/2005 330 <1 <1 330 ‐‐ 430 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 55 3 1800 2700 91

MW‐15 08/05/2005 300 <1 <1 300 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 89 2 1900 2800 100

MW‐15 09/06/2005 540 <1 <1 540 ‐‐ 270 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 28 2 1700 2300 65

MW‐15 10/05/2005 440 <1 <1 440 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 28 3 1500 2100 73

MW‐15 11/11/2005 400 <1 <1 400 ‐‐ 320 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 65 8 1700 2700 130

MW‐15 12/07/2005 640 <1 <1 640 ‐‐ 430 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 41 5 2000 3000 57

Page 59 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐15 01/04/2006 610 <1 <1 610 ‐‐ 550 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 56 3 2300 3500 190

MW‐15 02/06/2006 460 <1 <1 460 ‐‐ 400 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 63 1 1900 2800 270

MW‐15 03/15/2006 560 <1 <1 560 ‐‐ 290 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 24 1.5 1600 2500 250

MW‐15 08/03/2006 560 <20 <20 560 ‐‐ 380 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11 1700 2700 200

MW‐15 09/05/2006 400 <10 <10 400 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.5 1300 1910 77

MW‐15 10/09/2006 330 <10 <10 330 ‐‐ 110 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.2 1200 1660 73

MW‐15 11/06/2006 400 <10 <10 400 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.8 1300 1650 79

MW‐15 12/11/2006 750 <10 <10 750 ‐‐ 450 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.7 2300 3430 160

MW‐15 01/03/2007 630 <10 <10 630 ‐‐ 340 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.9 2000 2920 120

MW‐15 02/05/2007 500 <10 <10 500 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.9 1200 1760 130

MW‐15 03/05/2007 600 <10 <10 600 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.7 1400 1950 180

MW‐15 04/05/2007 550 <10 <10 550 ‐‐ 190 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.4 1300 2030 200

MW‐15 05/03/2007 410 <10 <10 410 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.1 800 1360 78

MW‐15 06/07/2007 400 <10 <10 400 ‐‐ 110 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.5 960 1400 57

MW‐15 07/02/2007 630 <10 <10 630 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.2 1700 2490 110

MW‐15 08/02/2007 250 <10 <10 250 ‐‐ 98 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.7 1100 1490 73

MW‐15 09/10/2007 200 <5 <5 200 ‐‐ 62 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.2 750 1090 48

MW‐15 10/08/2007 520 <10 <10 520 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.1 1400 2160 110

MW‐15 11/07/2007 530 <10 <10 530 ‐‐ 260 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.7 1600 2270 100

MW‐15 12/06/2007 550 <10 <10 550 ‐‐ 240 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.6 1400 2150 100

MW‐15 01/14/2008 190 <2.5 <2.5 190 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.2 920 1360 48

MW‐15 02/07/2008 370 <5 <5 370 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.6 1400 1990 130

MW‐15 03/04/2008 500 <10 <10 500 ‐‐ 230 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.7 1500 2340 130

MW‐15 04/10/2008 670 <10 <10 670 ‐‐ 250 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.9 1400 2360 88

MW‐15 05/05/2008 560 <10 <10 560 ‐‐ 260 34 0.55 11 1.3 140 380 ‐‐ ‐‐ ‐‐ 2 1500 2430 110

MW‐15 06/03/2008 560 <10 <10 560 ‐‐ 210 33 0.58 11 1.2 130 320 ‐‐ ‐‐ ‐‐ 1.6 1200 1950 38

MW‐15 07/01/2008 550 <10 <10 550 ‐‐ 340 52 0.78 18 1.8 170 370 ‐‐ ‐‐ ‐‐ 2.3 1600 2560 74

MW‐15 08/04/2008 300 <5.0 <5.0 300 ‐‐ 49 17 0.14 6.4 0.65 300 74 ‐‐ ‐‐ ‐‐ 1.7 1000 1550 29

MW‐15 09/08/2008 140 <2.5 <2.5 140 ‐‐ 39 5.0 0.27 1.9 0.2 150 31 ‐‐ ‐‐ ‐‐ 1.1 500 683 23

MW‐15 10/09/2008 140 <2.5 <2.5 140 ‐‐ 35 7.5 0.54 3.6 0.39 190 29 ‐‐ ‐‐ ‐‐ 1.2 710 943 41

MW‐15 11/04/2008 170 <2.5 <2.5 170 ‐‐ 52 9.1 1.3 3.2 0.33 150 49 ‐‐ ‐‐ ‐‐ 1.3 590 820 30

MW‐15 12/03/2008 250 <5.0 <5.0 250 ‐‐ 130 20 0.12 8.6 0.83 330 63 ‐‐ ‐‐ ‐‐ 1.1 1000 1520 71

MW‐15 01/13/2009 580 <8.2 <8.2 580 ‐‐ 360 66 0.13 26 2.9 410 250 ‐‐ ‐‐ ‐‐ 2.5 1900 2900 95

MW‐15 02/04/2009 700 <8.2 <8.2 700 ‐‐ 440 80 0.17 29 2.3 270 500 ‐‐ ‐‐ ‐‐ 2.5 2300 3420 100

MW‐15 03/04/2009 610 <8.2 <8.2 610 ‐‐ 420 62 0.19 23 2.0 190 500 ‐‐ ‐‐ ‐‐ 2.1 2100 3160 110

Page 60 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐15 04/13/2009 890 <8.2 <8.2 890 ‐‐ 450 58 0.22 24 1.5 150 720 ‐‐ ‐‐ ‐‐ 2.3 2500 3630 86

MW‐15 05/04/2009 880 <8.2 <8.2 880 ‐‐ 480 59 0.19 22 1.5 150 740 ‐‐ ‐‐ ‐‐ 2.5 2600 3750 98

MW‐15 06/08/2009 870 <8.2 <8.2 870 ‐‐ 500 53 0.2 20 1 140 740 ‐‐ ‐‐ ‐‐ 2.3 2700 3900 110

MW‐15 07/13/2009 820 <8.2 <8.2 820 ‐‐ 370 35 0.32 15 0.83 120 620 ‐‐ ‐‐ ‐‐ 2.0 2200 3180 65

MW‐15 08/04/2009 1000 <8.2 <8.2 1000 ‐‐ 350 39 0.11 15 0.83 140 640 ‐‐ ‐‐ ‐‐ 2.3 2200 3320 60

MW‐15 09/08/2009 980 <16 <16 980 ‐‐ 340 32 0.097 13 0.71 170 630 ‐‐ ‐‐ ‐‐ 2.1 2000 3240 69

MW‐15 10/07/2009 880 <8.2 <8.2 880 ‐‐ 320 28 0.11 10 0.6 150 570 ‐‐ ‐‐ ‐‐ 2.1 2000 2910 60

MW‐15 11/09/2009 790 <8.2 <8.2 790 ‐‐ 280 25 0.34 9.6 0.56 130 490 ‐‐ ‐‐ ‐‐ 2.2 1800 2660 47

MW‐15 12/08/2009 670 <8.2 <8.2 670 ‐‐ 210 20 0.46 7.9 0.46 98 360 ‐‐ ‐‐ ‐‐ 1.5 1400 2170 40

MW‐15 01/05/2010 460 <4.1 <4.1 460 ‐‐ 190 15 0.42 6.0 0.36 87 310 ‐‐ ‐‐ ‐‐ 1.7 1200 1840 39

MW‐15 02/10/2010 510 <8.2 <8.2 510 ‐‐ 180 20 0.23 8.3 0.45 100 370 ‐‐ ‐‐ ‐‐ 1.4 1400 1960 45

MW‐15 03/08/2010 500 <8.2 <8.2 500 ‐‐ 190 28 0.082 9.8 0.45 100 350 ‐‐ ‐‐ ‐‐ 1.5 1500 2020 59

MW‐15 04/15/2010 580 <8.2 ‐‐ 580 ‐‐ 170 32 0.061 12 0.46 100 410 ‐‐ ‐‐ ‐‐ 1.6 1300 2270 89

MW‐15 07/08/2010 710 <8.2 ‐‐ 710 ‐‐ 210 28 0.067 12 0.51 100 400 ‐‐ ‐‐ ‐‐ 2.1 1600 2520 140

MW‐15 10/27/2010 230 <4.1 ‐‐ 230 ‐‐ 110 19 0.49 6.4 0.31 84 130 0.026 ‐‐ ‐‐ 1.7 670 970 30

MW‐15 01/19/2011 260 <8.2 ‐‐ 260 ‐‐ 140 31 0.057 12 0.51 110 150 ‐‐ ‐‐ ‐‐ 1.2 1000 1290 39

MW‐15 04/04/2011 240 <8.2 ‐‐ 240 ‐‐ 110 29 0.098 10 0.42 99 140 ‐‐ ‐‐ ‐‐ 1.6 760 1130 39

MW‐15 07/07/2011 69 <4.1 ‐‐ 69 ‐‐ 34 17 0.15 5.9 0.25 60 24 ‐‐ ‐‐ 13 0.86 330 429 17

MW‐15 11/09/2011 450 <5.0 ‐‐ 450 0.57 346 72.1 J <0.20 28.1 J 2.10 J 293 194 J 0.085 ‐‐ 8.6 5.1 1420 2320 79.3

MW‐15 01/19/2012 360 ‐‐ ‐‐ 360 2.7 350 73 <0.050 Jo 31 1.6 290 170 0.069 ‐‐ 9.1 2.3 1400 2200 83

MW‐15 04/03/2012 220 <5.0 ‐‐ 220 <1.0 52.2 30.8 <0.20 10.2 0.53 133 39.1 0.011 ‐‐ 23.0 2.7 578 867 <44.5 U

MW‐15 07/23/2012 424 <5.0 ‐‐ 424 0.42 175 92.6 <0.20 36.8 1.7 285 136 0.023 ‐‐ 26.3 J‐ <0.57 U 1170 1880 65.1

MW‐15 10/15/2012 418 <5.0 ‐‐ 418 <0.50 324 62.5 J <0.20 24.6 J 1.14 J 311 J 152 J 0.037 ‐‐ 6.7 2.1 1310 2260 86.8

MW‐15 01/22/2013 278 <5.0 ‐‐ 278 <0.50 113 48.9 <0.20 17.1 0.208 233 82.7 0.028 ‐‐ 53.0 <0.20 928 1240 35.7

MW‐15 04/16/2013 298 <5.0 ‐‐ 298 <0.50 60.0 58.8 <0.20 21.3 0.442 238 102 0.012 ‐‐ 26.9 <0.20 1030 1480 27.4

MW‐15 07/17/2013 250 <5.0 ‐‐ 250 <0.50 232 57.6 <0.20 22.1 1.06 288 J 70.0 <0.01 ‐‐ 23.5 <2.2 U 1050 1850 74.0

MW‐15 10/21/2013 176 <5.0 ‐‐ 176 ‐‐ 92.2 23.0 J <0.20 8.52 J 0.121 204 51.5 J ‐‐ ‐‐ 28.3 <0.20 748 1160 39.2

MW‐15 01/22/2014 168 <5.0 ‐‐ 168 ‐‐ 118 29.6 <0.20 11.2 0.257 222 49.1 ‐‐ ‐‐ 41.5 <2.9 U 836 1050 51.1

MW‐15 04/22/2014 180 <5.0 ‐‐ 180 ‐‐ 67.0 20.6 <0.20 8.97 J 0.205 182 J 40.0 J ‐‐ ‐‐ 25.2 <0.44 U 542 912 25.5

MW‐15 10/20/2014 97.1 <5.0 ‐‐ 97.1 ‐‐ 8.7 13.7 <0.20 5.34 0.0508 44.0 17.2 ‐‐ ‐‐ 8.6 <0.20 226 315 10.9

MW‐15 04/15/2015 152 <5.0 ‐‐ 152 ‐‐ 121 110 J <0.20 36.5 J 0.183 J 108 J 121 J ‐‐ ‐‐ 93.2 <0.20 1280 1510 83.5

MW‐15 10/15/2015 441 <5.0 ‐‐ 441 ‐‐ 127 114 <0.20 46.2 <0.015 32.6 138 ‐‐ ‐‐ 27.5 <0.20 965 1560 47.4

MW‐15 04/14/2016 366 <5.0 ‐‐ 366 ‐‐ 92.7 94.2 <0.20 38.1 <0.015 16.7 119 J ‐‐ ‐‐ 34.1 <0.20 837 1350 50.5

MW‐15 10/12/2016 771 19.5 ‐‐ 791 ‐‐ 45 36.3 1.18 10.1 0.0643 857 J 114 ‐‐ ‐‐ 100 25.0 J‐ 2890 2890 92

MW‐16 01/20/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 43 ‐‐ ‐‐ ‐‐ ‐‐

Page 61 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐16 02/09/1998 81 <1 <1 81 ‐‐ 21 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 43 3.2 460 650 38

MW‐16 03/19/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 45 3.2 650 700 ‐‐

MW‐16 04/29/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 22 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 43 2.9 560 640 ‐‐

MW‐16 05/21/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 47 2.8 540 630 ‐‐

MW‐16 06/16/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 4.1 530 610 ‐‐

MW‐16 07/28/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 53 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 47 2.7 640 810 ‐‐

MW‐16 08/21/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 45 2.5 580 650 ‐‐

MW‐16 09/24/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27 <1.1 460 520 ‐‐

MW‐16 10/22/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 2.3 430 540 ‐‐

MW‐16 11/25/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 14 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 1.9 430 510 ‐‐

MW‐16 12/15/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.3 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 25 3.6 410 440 ‐‐

MW‐16 02/16/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 10 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 3.2 420 530 ‐‐

MW‐16 05/23/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 2 480 540 ‐‐

MW‐16 08/23/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.1 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.3 <1.1 240 230 ‐‐

MW‐16 11/22/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.5 <1.1 210 210 ‐‐

MW‐16 02/17/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4.4 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.6 4.5 230 260 ‐‐

MW‐16 05/02/2000 81 <1 <1 81 ‐‐ 6.9 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 1.5 350 400 16

MW‐16 08/08/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 63 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 84 2.1 850 1100 ‐‐

MW‐16 09/15/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 25 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 56 3.1 580 740 ‐‐

MW‐16 11/28/2000 76 <1 <1 76 ‐‐ 17 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 1.9 490 590 ‐‐

MW‐16 12/12/2000 81 <1 <1 81 ‐‐ 16 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 2.5 470 580 ‐‐

MW‐16 01/06/2001 86 <1 <1 86 ‐‐ 14 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 2 410 520 ‐‐

MW‐16 02/06/2001 86 <1 <1 86 ‐‐ 11 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 25 ‐‐ 480 490 22

MW‐16 03/23/2001 61 <1 <1 61 ‐‐ 18 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 20 4 360 460 25

MW‐16 04/16/2001 84 <1 <1 84 ‐‐ 28 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 22 1.7 410 500 25

MW‐16 05/23/2001 41 <1 <1 41 ‐‐ 34 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 28 1.9 430 550 30

MW‐16 06/22/2001 130 <1 <1 130 ‐‐ 84 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 45 2.5 730 990 37

MW‐16 07/19/2001 170 <1 <1 170 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 76 3 960 1300 43

MW‐16 08/01/2001 170 <1 <1 170 ‐‐ 110 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 84 8.2 1100 1400 49

MW‐16 09/04/2001 140 <1 <1 140 ‐‐ 29 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 48 3.9 710 850 39

MW‐16 10/02/2001 98 <1 <1 98 ‐‐ 18 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 37 5.2 550 700 30

MW‐16 11/06/2001 130 <1 <1 130 ‐‐ 29 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 40 2.8 540 700 30

MW‐16 12/05/2001 130 <1 <1 130 ‐‐ 19 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 37 5.4 530 660 27

MW‐16 01/08/2002 140 <1 <1 140 ‐‐ 21 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 3.4 520 650 26

MW‐16 02/05/2002 200 <1 <1 200 ‐‐ 19 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 3.5 520 690 24

Page 62 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐16 03/05/2002 120 <1 <1 120 ‐‐ 16 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 39 6.2 490 670 25

MW‐16 04/02/2002 110 <1 <1 110 ‐‐ 19 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 3.7 530 680 25

MW‐16 05/07/2002 120 <1 <1 120 ‐‐ 23 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 41 2.4 600 720 33

MW‐16 06/04/2002 100 <1 <1 100 ‐‐ 37 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 56 2.9 650 860 44

MW‐16 07/03/2002 110 <1 <1 110 ‐‐ 46 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 52 3 710 880 42

MW‐16 08/06/2002 110 <1 <1 110 ‐‐ 70 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 84 3.3 860 1200 46

MW‐16 09/05/2002 170 <1 <1 170 ‐‐ 40 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 55 3.2 760 910 26

MW‐16 10/09/2002 140 <1 <1 140 ‐‐ 22 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 50 3.2 660 820 30

MW‐16 11/08/2002 140 <1 <1 140 ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 42 3.5 650 750 30

MW‐16 12/03/2002 140 <1 <1 140 ‐‐ 21 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 3.3 610 710 25

MW‐16 01/06/2003 130 <1 <1 130 ‐‐ 21 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 43 3.2 660 800 37

MW‐16 02/04/2003 140 <1 <1 140 ‐‐ 25 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 44 3 700 810 38

MW‐16 03/04/2003 140 <1 <1 140 ‐‐ 25 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 41 2.9 700 800 37

MW‐16 04/01/2003 120 <1 <1 120 ‐‐ 23 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 41 3.4 650 790 42

MW‐16 05/01/2003 140 <1 <1 140 ‐‐ 28 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 42 8.7 650 800 42

MW‐16 06/03/2003 130 <1 <1 130 ‐‐ 35 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 45 3.3 720 840 41

MW‐16 07/01/2003 130 <1 <1 130 ‐‐ 65 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 57 2.6 760 1000 42

MW‐16 08/05/2003 90 <1 <1 90 ‐‐ 150 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 110 2.8 1200 1600 45

MW‐16 09/04/2003 130 <1 <1 130 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 100 5.8 1100 1500 47

MW‐16 10/01/2003 150 <1 <1 150 ‐‐ 85 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 89 5.8 1000 1300 44

MW‐16 11/04/2003 150 <1 <1 150 ‐‐ 71 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 77 5.4 930 1200 41

MW‐16 12/02/2003 160 <1 <1 160 ‐‐ 47 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 69 4.2 790 1100 41

MW‐16 01/13/2004 170 <1 <1 170 ‐‐ 28 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 41 4.8 690 840 37

MW‐16 02/04/2004 190 <1 <1 190 ‐‐ 35 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 44 4 680 920 36

MW‐16 03/02/2004 220 <1 <1 220 ‐‐ 44 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 48 5 730 960 37

MW‐16 04/06/2004 180 <1 <1 180 ‐‐ 69 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 56 3 850 1100 38

MW‐16 05/11/2004 200 <1 <1 200 ‐‐ 89 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 71 4 1000 1300 46

MW‐16 06/01/2004 190 <1 <1 190 ‐‐ 97 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 80 4 1100 1400 54

MW‐16 07/06/2004 180 <1 <1 180 ‐‐ 100 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 62 3 1000 1400 57

MW‐16 08/04/2004 120 <1 <1 120 ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 92 7 1100 1500 52

MW‐16 09/02/2004 110 <1 <1 110 ‐‐ 61 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 67 2 770 990 26

MW‐16 10/05/2004 160 <1 <1 160 ‐‐ 18 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 4 570 700 25

MW‐16 11/02/2004 160 <1 <1 160 ‐‐ 24 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 3 580 760 23

MW‐16 12/01/2004 160 <1 <1 160 ‐‐ 19 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1 580 750 23

MW‐16 01/12/2005 160 <1 <1 160 ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 42 4 640 840 27

Page 63 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐16 02/01/2005 130 <1 <1 130 ‐‐ 35 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 40 4 660 850 28

MW‐16 03/08/2005 170 <1 <1 170 ‐‐ 38 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 42 3 700 890 29

MW‐16 04/05/2005 170 <1 <1 170 ‐‐ 34 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 37 4 630 830 25

MW‐16 05/04/2005 140 <1 <1 140 ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 3 580 730 23

MW‐16 06/01/2005 140 <1 <1 140 ‐‐ 41 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 39 1.2 640 880 30

MW‐16 07/20/2005 160 <1 <1 160 ‐‐ 76 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 55 2 850 1100 48

MW‐16 08/03/2005 130 <1 <1 130 ‐‐ 71 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 59 <1 960 1200 57

MW‐16 09/07/2005 100 <1 <1 100 ‐‐ 58 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 50 2 840 930 36

MW‐16 10/06/2005 220 <1 <1 220 ‐‐ 87 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 39 7 750 1000 47

MW‐16 11/09/2005 140 <1 <1 140 ‐‐ 25 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 5 650 810 32

MW‐16 12/06/2005 140 <1 <1 140 ‐‐ 16 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 5.6 550 710 25

MW‐16 01/04/2006 130 <1 <1 130 ‐‐ 16 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 21 3 590 640 25

MW‐16 02/06/2006 180 <1 <1 180 ‐‐ 17 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 24 4 460 670 29

MW‐16 03/15/2006 130 <1 <1 130 ‐‐ 7.1 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 21 3.6 430 600 26

MW‐16 08/03/2006 74 <2.5 <2.5 74 ‐‐ 75 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.5 960 1210 41

MW‐16 09/05/2006 100 <5.0 <5.0 100 ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.1 590 733 23

MW‐16 10/09/2006 120 <2.5 <2.5 120 ‐‐ 13 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.3 460 567 21

MW‐16 11/06/2006 120 <2.5 <2.5 120 ‐‐ 6.6 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.4 420 460 18

MW‐16 12/11/2006 110 <5.0 <5.0 110 ‐‐ 7.1 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.4 390 474 18

MW‐16 01/03/2007 110 <2.5 <2.5 110 ‐‐ 8 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.6 390 456 15

MW‐16 02/05/2007 110 <2.5 <2.5 110 ‐‐ 11 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.6 390 486 16

MW‐16 03/05/2007 120 <5 <5 120 ‐‐ 44 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.5 700 888 29

MW‐16 04/05/2007 110 <5 <5 110 ‐‐ 28 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.5 530 741 28

MW‐16 05/03/2007 110 <5 <5 110 ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.5 590 712 25

MW‐16 06/07/2007 99 <5 <5 99 ‐‐ 36 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.5 620 806 26

MW‐16 07/02/2007 72 <2.5 <2.5 72 ‐‐ 42 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.2 660 839 30

MW‐16 08/02/2007 97 <5 <5 97 ‐‐ 63 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2 800 960 27

MW‐16 09/10/2007 86 <2.5 <2.5 86 ‐‐ 37 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.5 630 781 20

MW‐16 10/08/2007 94 <2.5 <2.5 94 ‐‐ 10 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.1 420 542 20

MW‐16 11/07/2007 100 <2.5 <2.5 100 ‐‐ 6.7 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3 390 464 19

MW‐16 12/06/2007 110 <2.5 <2.5 110 ‐‐ 6.1 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.2 380 443 18

MW‐16 01/14/2008 93 <2.5 <2.5 93 ‐‐ 9.7 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.6 350 442 19

MW‐16 02/07/2008 100 <2.5 <2.5 100 ‐‐ 13 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.6 390 511 20

MW‐16 03/04/2008 87 <2.5 <2.5 87 ‐‐ 19 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.3 460 582 28

MW‐16 04/10/2008 93 <2.5 <2.5 93 ‐‐ 23 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.3 490 644 32

Page 64 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐16 05/05/2008 87 <2.5 <2.5 87 ‐‐ 34 41 <0.05 Jo 19 0.33 60 39 ‐‐ ‐‐ ‐‐ 2.5 540 747 36

MW‐16 06/03/2008 93 <2.5 <2.5 93 ‐‐ 52 49 <0.050 24 0.31 65 39 ‐‐ ‐‐ ‐‐ 2.4 630 826 37

MW‐16 07/01/2008 86 <2.5 <2.5 86 ‐‐ 89 71 <0.050 35 0.54 76 43 ‐‐ ‐‐ ‐‐ 1.9 890 1140 44

MW‐16 08/04/2008 100 <5.0 <5.0 100 ‐‐ 95 74 <0.050 35 0.84 72 45 ‐‐ ‐‐ ‐‐ 1.0 960 1250 46

MW‐16 09/08/2008 100 <2.5 <2.5 100 ‐‐ 45 52 <0.050 Jo 25 0.69 62 61 ‐‐ ‐‐ ‐‐ 2.7 760 968 40

MW‐16 10/09/2008 99 <2.5 <2.5 99 ‐‐ 26 32 <0.050 Jo 15 0.41 45 59 ‐‐ ‐‐ ‐‐ 3.0 560 789 33

MW‐16 11/04/2008 110 <2.5 <2.5 110 ‐‐ 22 24 <0.050 Jo 11 0.3 39 62 ‐‐ ‐‐ ‐‐ 3.1 450 625 26

MW‐16 12/03/2008 100 <2.5 <2.5 100 ‐‐ 21 22 <0.050 Jo 10 0.2 37 55 ‐‐ ‐‐ ‐‐ 3.3 400 542 25

MW‐16 01/13/2009 100 <4.1 <4.1 100 ‐‐ 25 24 <0.050 Jo 12 0.25 39 55 ‐‐ ‐‐ ‐‐ 2.9 450 557 26

MW‐16 02/04/2009 110 <4.1 <4.1 110 ‐‐ 29 27 <0.050 13 0.24 41 52 ‐‐ ‐‐ ‐‐ 2.8 430 580 25

MW‐16 03/04/2009 110 <4.1 <4.1 110 ‐‐ 37 31 <0.050 Jo 15 0.28 42 54 ‐‐ ‐‐ ‐‐ 2.6 490 648 31

MW‐16 04/14/2009 110 <4.1 <4.1 110 ‐‐ 48 40 <0.050 19 0.45 48 59 ‐‐ ‐‐ ‐‐ 2.7 550 718 37

MW‐16 05/04/2009 110 <4.1 <4.1 110 ‐‐ 55 41 <0.050 Jo 20 0.37 50 59 ‐‐ ‐‐ ‐‐ 3.0 600 781 40

MW‐16 06/08/2009 110 <4.1 <4.1 110 ‐‐ 48 46 <0.05 Jo 22 0.46 53 57 ‐‐ ‐‐ ‐‐ 2.8 650 830 42

MW‐16 07/13/2009 120 <4.1 <4.1 120 ‐‐ 72 63 <0.050 Jo 30 0.56 58 52 ‐‐ ‐‐ ‐‐ 2.9 830 980 40

MW‐16 08/04/2009 140 <8.2 <8.2 140 ‐‐ 130 88 0.051 41 0.77 64 70 ‐‐ ‐‐ ‐‐ 2.9 1000 1310 52

MW‐16 09/08/2009 150 <8.2 <8.2 150 ‐‐ 90 89 <0.050 Jo 41 1.0 75 110 ‐‐ ‐‐ ‐‐ 3.3 1100 1360 56

MW‐16 10/07/2009 140 <4.1 <4.1 140 ‐‐ 15 28 0.05 13 0.29 39 71 ‐‐ ‐‐ ‐‐ 4.6 510 642 25

MW‐16 11/09/2009 130 <4.1 <4.1 130 ‐‐ 15 24 0.097 11 0.31 37 70 ‐‐ ‐‐ ‐‐ 4.8 540 629 19

MW‐16 12/08/2009 120 <4.1 <4.1 120 ‐‐ 16 22 0.26 9.9 0.28 37 67 ‐‐ ‐‐ ‐‐ 3.7 500 623 21

MW‐16 01/05/2010 130 <4.1 <4.1 130 ‐‐ 20 24 <0.050 Jo 11 0.3 42 74 ‐‐ ‐‐ ‐‐ 3.7 560 708 26

MW‐16 02/11/2010 130 <4.1 <4.1 130 ‐‐ 31 33 <0.050 Jo 15 0.38 48 80 ‐‐ ‐‐ ‐‐ 2.8 600 770 28

MW‐16 03/08/2010 130 <4.1 <4.1 130 ‐‐ 46 38 <0.050 Jo 17 0.46 53 78 ‐‐ ‐‐ ‐‐ 3.7 660 829 29

MW‐16 04/15/2010 130 <8.2 ‐‐ 130 ‐‐ 72 55 <0.05 25 0.42 61 83 ‐‐ ‐‐ ‐‐ 3.3 760 1060 33

MW‐16 07/08/2010 140 <8.2 ‐‐ 140 ‐‐ 81 69 <0.05 Jo 30 0.54 73 78 ‐‐ ‐‐ ‐‐ 3.1 840 1200 45

MW‐16 10/27/2010 130 <4.1 ‐‐ 130 ‐‐ 54 48 <0.05 Jo 19 0.45 66 64 0.074 ‐‐ ‐‐ 2.1 700 860 24

MW‐16 01/19/2011 160 <4.1 ‐‐ 160 ‐‐ 48 51 <0.05 21 0.48 66 72 ‐‐ ‐‐ ‐‐ 4.2 830 944 31

MW‐16 04/04/2011 160 <4.1 ‐‐ 160 ‐‐ 53 51 <0.05 Jo 19 0.47 69 84 ‐‐ ‐‐ ‐‐ 4.0 730 964 29

MW‐16 07/07/2011 140 <8.2 ‐‐ 140 ‐‐ 75 70 <0.05 25 0.55 79 110 ‐‐ ‐‐ 70 3.4 960 1260 38

MW‐16 10/04/2011 120 <4.1 ‐‐ 120 ‐‐ 18 22 0.18 7.6 0.2 46 71 ‐‐ ‐‐ 28 3.9 500 619 16

MW‐16 01/18/2012 150 <4.1 ‐‐ 150 ‐‐ 26 25 <0.05 Jo 9.3 0.25 56 92 ‐‐ ‐‐ 30 3.0 540 736 22

MW‐16 04/04/2012 160 <4.1 ‐‐ 160 ‐‐ 39 37 <0.05 Jo 13 0.34 56 78 ‐‐ ‐‐ 38 3.0 650 841 32

MW‐16 07/23/2012 120 <8.2 ‐‐ 120 ‐‐ 72 60 <0.05 Jo 22 0.42 73 70 ‐‐ ‐‐ 66 2.6 810 1090 33

MW‐16 10/16/2012 140 <8.2 ‐‐ 140 ‐‐ 74 60 0.066 21 0.51 76 95 ‐‐ ‐‐ 54 2.9 810 1060 25

MW‐16 01/22/2013 170 <4.1 ‐‐ 170 ‐‐ 43 43 <0.05 14 0.23 60 110 ‐‐ ‐‐ 51 3.7 710 944 27

Page 65 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐16 04/17/2013 170 <8.2 ‐‐ 170 ‐‐ 56 49 0.057 18 0.46 66 110 ‐‐ ‐‐ 62 4.2 830 1050 34

MW‐16 07/17/2013 140 <8.2 ‐‐ 140 ‐‐ 95 67 <0.05 23 0.34 84 130 ‐‐ ‐‐ 78 3.3 1000 1350 44

MW‐16 10/21/2013 200 <8.2 ‐‐ 200 ‐‐ 100 74 <0.05 29 0.7 99 150 ‐‐ ‐‐ 110 3.8 1200 1700 44

MW‐16 01/22/2014 190 <4.1 ‐‐ 190 ‐‐ 49 33 0.06 11 0.22 68 120 ‐‐ ‐‐ 34 4.5 590 882 25

MW‐16 04/22/2014 180 <8.2 ‐‐ 180 ‐‐ 54 33 <0.05 12 0.25 69 110 ‐‐ ‐‐ 43 3.3 700 1030 24

MW‐16 07/21/2014 180 <8.2 ‐‐ 180 ‐‐ 68 51 <0.05 19 0.37 91 130 ‐‐ ‐‐ 61 2.8 830 1260 31

MW‐16 10/20/2014 130 <8.2 ‐‐ 130 ‐‐ 130 100 <0.05 42 0.79 130 160 ‐‐ ‐‐ 150 2.6 1400 1940 46

MW‐16 01/21/2015 190 <8.2 ‐‐ 190 ‐‐ 72 58 <0.05 22 0.36 96 140 ‐‐ ‐‐ 95 3.6 1100 1520 44

MW‐16 04/15/2015 180 <8.2 ‐‐ 180 ‐‐ 62 59 <0.05 25 0.38 100 110 ‐‐ ‐‐ 77 3.6 860 1280 45

MW‐16 07/22/2015 160 <8.2 ‐‐ 160 ‐‐ 34 49 <0.05 20 0.3 93 91 ‐‐ ‐‐ 57 3.9 660 1090 40

MW‐16 10/15/2015 180 <8.2 ‐‐ 180 ‐‐ 69 56 <0.05 24 0.27 99 82 ‐‐ ‐‐ 59 3.1 900 1160 41

MW‐16 01/20/2016 170 <8.2 ‐‐ 170 ‐‐ 78 63 0.054 26 0.25 110 81 ‐‐ ‐‐ 62 2.3 910 1280 49

MW‐16 04/14/2016 130 <8.2 ‐‐ 130 ‐‐ 80 69 <0.05 28 0.22 120 81 ‐‐ ‐‐ 81 2.0 900 1290 48

MW‐16 07/18/2016 110 <8.2 ‐‐ 110 ‐‐ 76 90 <0.05 37 0.39 160 80 ‐‐ ‐‐ 120 2.8 1400 1680 63

MW‐16 10/12/2016 97 <8.2 ‐‐ 97 ‐‐ 54 66 <0.05 25 0.16 140 62 ‐‐ ‐‐ 78 2.8 880 1190 46

MW‐17 01/20/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.7 ‐‐ ‐‐ ‐‐ ‐‐

MW‐17 02/09/1998 60 <1 <1 60 ‐‐ 6.7 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.8 2.7 190 260 15

MW‐17 03/19/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 18 3.4 400 460 ‐‐

MW‐17 04/29/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 10 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 2.1 300 330 ‐‐

MW‐17 05/21/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 10 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 10 2.5 290 300 ‐‐

MW‐17 06/16/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 26 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 2.3 330 440 ‐‐

MW‐17 07/28/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 20 2.3 310 450 ‐‐

MW‐17 08/21/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.1 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11 2.3 290 310 ‐‐

MW‐17 09/24/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.6 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11 2.2 270 320 ‐‐

MW‐17 10/22/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.4 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 15 1.9 220 330 ‐‐

MW‐17 11/25/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.8 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 1.5 230 300 ‐‐

MW‐17 12/15/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.3 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9 4 270 250 ‐‐

MW‐17 02/16/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.9 <1.1 220 240 ‐‐

MW‐17 05/23/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11 <1.1 260 290 ‐‐

MW‐17 08/23/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 10 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.9 <1.1 290 310 ‐‐

MW‐17 11/22/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6.2 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.6 <1.1 240 260 ‐‐

MW‐17 02/18/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7.8 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7 <1.1 210 230 ‐‐

MW‐17 05/02/2000 25 <1 <1 25 ‐‐ 12 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 10 1.2 230 260 12

MW‐17 08/08/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 20 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 10 <1.1 220 320 ‐‐

MW‐17 09/21/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.9 1.1 270 260 ‐‐

Page 66 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐17 11/28/2000 30 <1 <1 30 ‐‐ 9.8 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.8 1.8 210 240 ‐‐

MW‐17 12/15/2000 40 <1 <1 40 ‐‐ 12 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2 <1.1 210 240 ‐‐

MW‐17 01/06/2001 40 <1 <1 40 ‐‐ 8.5 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.7 4 220 230 ‐‐

MW‐17 02/02/2001 41 <1 <1 41 ‐‐ 12 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.6 ‐‐ 310 230 13

MW‐17 03/21/2001 49 <1 <1 49 ‐‐ 9.3 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.4 <1.1 170 230 13

MW‐17 04/16/2001 31 <1 <1 31 ‐‐ 21 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 <1.1 260 320 16

MW‐17 05/22/2001 21 <1 <1 21 ‐‐ 28 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 2 340 410 36

MW‐17 06/25/2001 21 <1 <1 21 ‐‐ 12 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.3 <1.1 220 260 21

MW‐17 07/17/2001 30 <1 <1 30 ‐‐ 13 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.3 4 190 280 28

MW‐17 08/01/2001 35 <1 <1 35 ‐‐ 15 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 3.1 290 350 44

MW‐17 09/05/2001 50 <1 <1 50 ‐‐ 16 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 22 1.1 350 420 40

MW‐17 10/02/2001 40 <1 <1 40 ‐‐ 14 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 20 1.2 370 380 20

MW‐17 11/06/2001 30 <1 <1 30 ‐‐ 6.9 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 <1.1 220 260 13

MW‐17 12/04/2001 30 <1 <1 30 ‐‐ 10 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 2 420 260 15

MW‐17 01/08/2002 30 <1 <1 30 ‐‐ 11 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 1.6 250 260 18

MW‐17 02/05/2002 100 <1 <1 100 ‐‐ 9.4 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 <1.1 200 250 16

MW‐17 03/08/2002 20 <1 <1 20 ‐‐ 8.7 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 9.8 <1.1 440 220 13

MW‐17 04/02/2002 30 <1 <1 30 ‐‐ 8.8 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 12 <1.1 230 250 14

MW‐17 05/07/2002 30 <1 <1 30 ‐‐ 7 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 <1.1 270 340 53

MW‐17 06/05/2002 20 <1 <1 20 ‐‐ 8.7 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 23 <1.1 290 360 38

MW‐17 07/02/2002 25 <1 <1 25 ‐‐ 30 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 26 1.7 350 480 46

MW‐17 08/06/2002 40 <1 <1 40 ‐‐ 56 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 1.3 440 600 40

MW‐17 09/05/2002 35 <1 <1 35 ‐‐ 19 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 <1.1 280 320 14

MW‐17 10/08/2002 30 <1 <1 30 ‐‐ 20 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 21 <1.1 290 350 19

MW‐17 11/06/2002 25 <1 <1 25 ‐‐ 14 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 <1.1 240 270 16

MW‐17 12/05/2002 20 <1 <1 20 ‐‐ 19 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 19 <1.1 230 310 19

MW‐17 01/06/2003 35 <1 <1 35 ‐‐ 18 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 20 <1.1 470 310 18

MW‐17 02/04/2003 80 <1 <1 80 ‐‐ 65 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 <1.1 400 570 30

MW‐17 03/04/2003 75 <1 <1 75 ‐‐ 52 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 20 <1.1 430 550 33

MW‐17 04/02/2003 20 <1 <1 20 ‐‐ 18 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 <1.1 270 300 17

MW‐17 05/02/2003 20 <1 <1 20 ‐‐ 16 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 22 <1.1 260 310 18

MW‐17 06/03/2003 20 <1 <1 20 ‐‐ 12 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 18 <1.1 350 280 20

MW‐17 07/01/2003 19 <1 <1 19 ‐‐ 16 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 23 <1.1 330 350 25

MW‐17 08/05/2003 30 <1 <1 30 ‐‐ 25 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 23 <1.1 330 410 23

MW‐17 09/06/2003 31 <1 <1 31 ‐‐ 28 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27 1.5 290 440 25

Page 67 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐17 10/02/2003 31 <1 <1 31 ‐‐ 16 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 14 <1.1 250 290 18

MW‐17 11/05/2003 25 <1 <1 25 ‐‐ 34 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 18 <1.1 310 370 17

MW‐17 12/02/2003 36 <1 <1 36 ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 13 <1.1 240 320 16

MW‐17 01/13/2004 30 <1 <1 30 ‐‐ 38 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 <1.1 330 370 21

MW‐17 02/04/2004 31 <1 <1 31 ‐‐ 41 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 18 <1 300 390 20

MW‐17 03/04/2004 10 <1 <1 10 ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 <1 330 360 22

MW‐17 04/08/2004 15 <1 <1 15 ‐‐ 41 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 1 250 350 21

MW‐17 05/12/2004 36 <1 <1 36 ‐‐ 44 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27 1 390 510 27

MW‐17 06/04/2004 31 <1 <1 31 ‐‐ 41 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1 390 510 24

MW‐17 07/08/2004 26 <1 <1 26 ‐‐ 81 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 <1 510 680 22

MW‐17 08/07/2004 31 <1 <1 31 ‐‐ 62 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 37 <1 460 610 25

MW‐17 09/02/2004 31 <1 <1 31 ‐‐ 47 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 1 410 520 25

MW‐17 10/06/2004 51 <1 <1 51 ‐‐ 42 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 2 420 510 23

MW‐17 11/04/2004 20 <1 <1 20 ‐‐ 39 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 28 <1 360 490 25

MW‐17 12/01/2004 30 <1 <1 30 ‐‐ 45 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27 <1 360 500 20

MW‐17 01/12/2005 30 <1 <1 30 ‐‐ 52 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 26 <1 350 500 20

MW‐17 02/01/2005 25 <1 <1 25 ‐‐ 53 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 26 <1 470 520 22

MW‐17 03/08/2005 30 <1 <1 30 ‐‐ 61 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 <1 430 550 23

MW‐17 04/05/2005 46 <1 <1 46 ‐‐ 36 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 24 1 340 450 20

MW‐17 05/04/2005 41 <1 <1 41 ‐‐ 34 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 24 <1 340 440 21

MW‐17 06/01/2005 30 <1 <1 30 ‐‐ 65 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 71 2 680 920 52

MW‐17 07/20/2005 76 <1 <1 76 ‐‐ 110 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 85 2 1000 1400 84

MW‐17 08/04/2005 81 <1 <1 81 ‐‐ 54 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 57 <1 780 960 54

MW‐17 09/06/2005 81 <1 <1 81 ‐‐ 29 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 16 2 450 490 29

MW‐17 10/05/2005 61 <1 <1 61 ‐‐ 53 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 28 <1 420 620 43

MW‐17 11/09/2005 51 <1 <1 51 ‐‐ 54 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 25 2 560 610 44

MW‐17 12/06/2005 45 <1 <1 45 ‐‐ 76 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 17 1.5 410 610 50

MW‐17 01/04/2006 40 <1 <1 40 ‐‐ 160 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 20 <1 600 870 58

MW‐17 02/06/2006 61 <1 <1 61 ‐‐ 140 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 <1 530 860 55

MW‐17 03/13/2006 51 <1 <1 51 ‐‐ 170 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27 <1 650 990 66

MW‐17 08/03/2006 210 <10 <10 210 ‐‐ 88 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.2 580 902 37

MW‐17 09/05/2006 180 <5.0 <5.0 180 ‐‐ 62 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.2 530 784 30

MW‐17 10/09/2006 170 <5.0 <5.0 170 ‐‐ 45 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.0 470 671 26

MW‐17 11/06/2006 230 <5.0 <5.0 230 ‐‐ 82 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.2 660 894 33

MW‐17 12/11/2006 210 <2.5 <2.5 210 ‐‐ 81 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.5 590 895 30

Page 68 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐17 01/03/2007 210 <5 <5 210 ‐‐ 76 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.3 590 893 33

MW‐17 02/05/2007 190 <5 <5 190 ‐‐ 90 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.9 600 874 37

MW‐17 03/05/2007 160 <5 <5 160 ‐‐ 93 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.3 560 813 37

MW‐17 04/05/2007 170 <2.5 <2.5 170 ‐‐ 85 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.8 540 881 36

MW‐17 05/03/2007 130 <5 <5 130 ‐‐ 79 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.6 560 809 34

MW‐17 06/07/2007 120 <5 <5 120 ‐‐ 93 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.8 610 906 45

MW‐17 07/02/2007 110 <5 <5 110 ‐‐ 100 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.8 640 913 48

MW‐17 08/02/2007 120 <5 <5 120 ‐‐ 74 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.5 550 780 49

MW‐17 09/10/2007 150 <5 <5 150 ‐‐ 65 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.4 550 784 41

MW‐17 10/08/2007 160 <5 <5 160 ‐‐ 66 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.7 570 840 39

MW‐17 11/07/2007 170 <5 <5 170 ‐‐ 50 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.3 600 821 42

MW‐17 12/06/2007 170 <5 <5 170 ‐‐ 65 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.1 590 832 44

MW‐17 01/14/2008 180 <5 <5 180 ‐‐ 57 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.4 610 840 41

MW‐17 02/07/2008 160 <2.5 <2.5 160 ‐‐ 61 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2 580 845 41

MW‐17 03/04/2008 150 <2.5 <2.5 150 ‐‐ 51 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.2 550 760 39

MW‐17 04/10/2008 140 <2.5 <2.5 140 ‐‐ 65 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.7 570 847 47

MW‐17 05/05/2008 130 <5 <5 130 ‐‐ 58 32 <0.05 Jo 9.1 0.14 30 100 ‐‐ ‐‐ ‐‐ 1.5 570 823 47

MW‐17 06/03/2008 110 <2.5 <2.5 110 ‐‐ 59 36 <0.050 Jo 10 0.18 28 85 ‐‐ ‐‐ ‐‐ 1.5 530 753 49

MW‐17 07/01/2008 110 <5.0 <5.0 110 ‐‐ 41 30 <0.050 Jo 9.0 0.13 27 87 ‐‐ ‐‐ ‐‐ 1.6 500 720 38

MW‐17 08/04/2008 120 <5.0 <5.0 120 ‐‐ 66 32 <0.050 Jo 8.9 0.32 26 90 ‐‐ ‐‐ ‐‐ 1.2 530 803 45

MW‐17 09/08/2008 120 <2.5 <2.5 120 ‐‐ 49 32 <0.050 Jo 9.4 0.44 20 90 ‐‐ ‐‐ ‐‐ 1.6 500 710 45

MW‐17 10/09/2008 150 <2.5 <2.5 150 ‐‐ 90 33 <0.050 Jo 9.4 0.29 29 98 ‐‐ ‐‐ ‐‐ 1.5 570 880 44

MW‐17 11/04/2008 190 <5.0 <5.0 190 ‐‐ 120 45 <0.050 Jo 13 0.39 44 140 ‐‐ ‐‐ ‐‐ 1.4 740 1150 58

MW‐17 12/03/2008 200 <5.0 <5.0 200 ‐‐ 120 43 <0.050 Jo 12 0.31 46 140 ‐‐ ‐‐ ‐‐ 1.3 740 1150 66

MW‐17 01/13/2009 180 <8.2 <8.2 180 ‐‐ 120 43 <0.050 Jo 12 0.39 43 130 ‐‐ ‐‐ ‐‐ 1.6 750 1060 60

MW‐17 02/04/2009 170 <8.2 <8.2 170 ‐‐ 110 49 <0.050 14 0.42 43 140 ‐‐ ‐‐ ‐‐ 1.3 720 1020 58

MW‐17 03/04/2009 180 <8.2 <8.2 180 ‐‐ 110 42 <0.050 Jo 11 0.35 44 140 ‐‐ ‐‐ ‐‐ 1.3 700 1060 61

MW‐17 04/13/2009 170 <8.2 <8.2 170 ‐‐ 120 62 <0.050 18 0.48 49 140 ‐‐ ‐‐ ‐‐ 1.4 910 1180 70

MW‐17 05/04/2009 190 <8.2 <8.2 190 ‐‐ 120 59 <0.050 Jo 18 0.42 49 150 ‐‐ ‐‐ ‐‐ 2.0 840 1200 73

MW‐17 06/08/2009 430 <8.2 <8.2 430 ‐‐ 180 81 <0.05 23 0.5 59 240 ‐‐ ‐‐ ‐‐ 2.8 1200 1760 49

MW‐17 07/13/2009 610 <8.2 <8.2 610 ‐‐ 110 130 <0.050 49 0.87 62 150 ‐‐ ‐‐ ‐‐ 5.2 1200 1750 66

MW‐17 08/04/2009 500 <8.2 <8.2 500 ‐‐ 85 100 <0.05 40 0.95 85 100 ‐‐ ‐‐ ‐‐ 11 1100 1430 48

MW‐17 09/08/2009 370 <16 <16 370 ‐‐ 64 75 0.1 25 0.88 86 91 ‐‐ ‐‐ ‐‐ 9.5 760 1160 34

MW‐17 10/06/2009 240 <8.2 <8.2 240 ‐‐ 77 61 <0.050 Jo 20 0.7 95 100 ‐‐ ‐‐ ‐‐ 8.9 860 1170 39

MW‐17 11/10/2009 200 <8.2 <8.2 200 ‐‐ 64 46 <0.050 Jo 15 0.57 95 74 ‐‐ ‐‐ ‐‐ 5.1 700 1030 42

Page 69 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐17 12/08/2009 210 <8.2 <8.2 210 ‐‐ 88 52 <0.050 19 0.66 86 85 ‐‐ ‐‐ ‐‐ 10 810 1150 46

MW‐17 01/05/2010 210 <4.1 <4.1 210 ‐‐ 96 49 <0.050 18 0.63 84 92 ‐‐ ‐‐ ‐‐ 3.5 800 1170 48

MW‐17 02/10/2010 210 <8.2 <8.2 210 ‐‐ 85 50 <0.050 19 0.56 82 84 ‐‐ ‐‐ ‐‐ 2.8 710 1040 46

MW‐17 03/08/2010 170 <8.2 <8.2 170 ‐‐ 100 67 <0.050 23 0.84 74 90 ‐‐ ‐‐ ‐‐ 3.0 860 1110 56

MW‐17 04/15/2010 290 <8.2 ‐‐ 290 ‐‐ 140 100 <0.05 35 1.4 85 110 ‐‐ ‐‐ ‐‐ 2.4 920 1390 59

MW‐17 07/08/2010 270 <8.2 ‐‐ 270 ‐‐ 110 75 <0.05 26 1.9 53 110 ‐‐ ‐‐ ‐‐ 2.0 800 1180 47

MW‐17 10/28/2010 280 <8.2 ‐‐ 280 ‐‐ 89 58 <0.05 Jo 19 1.4 73 140 0.092 ‐‐ ‐‐ 6.2 860 1220 39

MW‐17 01/19/2011 220 <4.1 ‐‐ 220 ‐‐ 60 39 0.13 14 0.9 47 110 ‐‐ ‐‐ ‐‐ 1.9 760 958 28

MW‐17 04/04/2011 130 <4.1 ‐‐ 130 ‐‐ 42 27 <0.05 Jo 12 0.91 58 100 ‐‐ ‐‐ ‐‐ 2.0 610 863 27

MW‐17 07/07/2011 180 <8.2 ‐‐ 180 ‐‐ 70 60 <0.05 22 2.8 64 110 ‐‐ ‐‐ 58 2.0 840 1210 41

MW‐17 10/04/2011 260 <8.2 ‐‐ 260 ‐‐ 71 73 <0.05 23 3.2 82 87 ‐‐ ‐‐ 50 2.8 860 1190 37

MW‐17 01/17/2012 180 <4.1 ‐‐ 180 ‐‐ 47 43 <0.05 16 2.8 67 74 ‐‐ ‐‐ 37 1.6 630 870 23

MW‐17 04/04/2012 180 <8.2 ‐‐ 180 ‐‐ 68 54 <0.05 22 3.5 64 79 ‐‐ ‐‐ 54 1.4 740 1050 35

MW‐17 07/23/2012 270 <8.2 ‐‐ 270 ‐‐ 90 85 <0.05 37 3.3 88 120 ‐‐ ‐‐ 79 2.9 1200 1560 78

MW‐17 10/16/2012 190 <4.1 ‐‐ 190 ‐‐ 71 55 <0.05 Jo 20 1.3 58 83 ‐‐ ‐‐ 37 2.1 690 945 24

MW‐17 01/22/2013 160 <4.1 ‐‐ 160 ‐‐ 65 41 <0.05 16 0.99 49 94 ‐‐ ‐‐ 39 1.7 630 886 25

MW‐17 04/17/2013 110 <4.1 ‐‐ 110 ‐‐ 77 36 <0.05 Jo 15 0.89 43 84 ‐‐ ‐‐ 40 1.3 590 830 24

MW‐17 07/17/2013 460 <8.2 ‐‐ 460 ‐‐ 120 130 <0.05 50 3 79 120 ‐‐ ‐‐ 43 4.2 1100 1570 47

MW‐17 10/21/2013 220 <8.2 ‐‐ 220 ‐‐ 88 47 <0.05 18 0.84 50 100 ‐‐ ‐‐ 36 1.7 680 1070 20

MW‐17 01/22/2014 190 <4.1 ‐‐ 190 ‐‐ 39 39 0.07 14 0.67 36 94 ‐‐ ‐‐ 29 2.3 490 754 17

MW‐17 04/22/2014 220 <8.2 ‐‐ 220 ‐‐ 98 55 <0.05 22 0.92 55 110 ‐‐ ‐‐ 33 1.5 740 1160 34

MW‐17 07/21/2014 230 <8.2 ‐‐ 230 ‐‐ 160 110 <0.05 50 2.5 120 170 ‐‐ ‐‐ 120 5.8 1600 2110 98

MW‐17 10/20/2014 260 <8.2 ‐‐ 260 ‐‐ 120 120 <0.05 44 2.4 96 110 ‐‐ ‐‐ 71 3.2 1000 1610 70

MW‐17 01/21/2015 240 <8.2 ‐‐ 240 ‐‐ 110 83 <0.05 31 1.5 79 100 ‐‐ ‐‐ 72 2.3 1000 1490 53

MW‐17 04/15/2015 200 <8.2 ‐‐ 200 ‐‐ 87 71 <0.05 29 1.3 80 120 ‐‐ ‐‐ 75 2.0 910 1330 41

MW‐17 07/22/2015 170 <8.2 ‐‐ 170 ‐‐ 130 81 <0.05 30 2 95 110 ‐‐ ‐‐ 73 1.9 990 1510 32

MW‐17 10/15/2015 180 <4.1 ‐‐ 180 ‐‐ 51 44 <0.05 20 0.98 64 58 ‐‐ ‐‐ 35 2.3 660 864 26

MW‐17 01/20/2016 180 <4.1 ‐‐ 180 ‐‐ 63 53 <0.05 Jo 23 0.99 56 62 ‐‐ ‐‐ 40 2.0 660 960 26

MW‐17 04/14/2016 170 <8.2 ‐‐ 170 ‐‐ 72 66 <0.05 29 1 66 74 ‐‐ ‐‐ 54 2.0 680 1010 26

MW‐17 07/18/2016 170 <8.2 ‐‐ 170 ‐‐ 77 66 <0.05 33 0.22 78 98 ‐‐ ‐‐ 70 2.2 1000 1330 27

MW‐17 10/12/2016 250 <8.2 ‐‐ 250 ‐‐ 49 75 <0.05 33 0.41 99 86 ‐‐ ‐‐ 55 3.2 860 1180 33

MW‐18 01/20/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐

MW‐18 02/09/1998 160 <1 <1 160 ‐‐ 25 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27 <1.1 540 710 58

MW‐18 03/19/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27 <1.1 580 760 ‐‐

MW‐18 04/29/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 28 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27 19 550 770 ‐‐

Page 70 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐18 05/20/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 590 800 ‐‐

MW‐18 06/16/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 <1.1 570 800 ‐‐

MW‐18 07/28/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 1.3 580 820 ‐‐

MW‐18 08/21/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 <1.1 640 850 ‐‐

MW‐18 09/24/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 620 840 ‐‐

MW‐18 10/22/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 28 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 <1.1 580 860 ‐‐

MW‐18 11/25/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1.1 650 870 ‐‐

MW‐18 12/15/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 1.9 610 840 ‐‐

MW‐18 02/16/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 2.2 580 860 ‐‐

MW‐18 05/23/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 710 850 ‐‐

MW‐18 08/23/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 650 860 ‐‐

MW‐18 11/22/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 700 890 ‐‐

MW‐18 02/18/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 640 900 ‐‐

MW‐18 05/02/2000 200 <1 <1 200 ‐‐ 35 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 660 900 100

MW‐18 08/09/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 <1.1 660 920 ‐‐

MW‐18 09/13/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 39 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1.1 660 930 ‐‐

MW‐18 11/21/2000 210 <1 <1 210 ‐‐ 36 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 650 960 ‐‐

MW‐18 12/12/2000 210 <1 <1 210 ‐‐ 37 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 680 920 ‐‐

MW‐18 01/06/2001 210 <1 <1 210 ‐‐ 39 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1.1 670 930 ‐‐

MW‐18 02/06/2001 210 <1 <1 210 ‐‐ 35 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 ‐‐ 790 950 110

MW‐18 03/27/2001 200 <1 <1 200 ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 680 940 100

MW‐18 04/18/2001 200 <1 <1 200 ‐‐ 35 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 <1.1 700 950 110

MW‐18 05/25/2001 200 <1 <1 200 ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1.1 610 930 110

MW‐18 06/29/2001 200 <1 <1 200 ‐‐ 34 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1.1 650 930 110

MW‐18 07/17/2001 220 <1 <1 220 ‐‐ 34 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1.1 610 920 110

MW‐18 08/02/2001 270 <1 <1 270 ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 <1.1 680 930 110

MW‐18 09/04/2001 210 <1 <1 210 ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1.1 680 910 110

MW‐18 10/03/2001 210 <1 <1 210 ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1.1 730 890 110

MW‐18 11/08/2001 200 <1 <1 200 ‐‐ 35 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 <1.1 530 920 120

MW‐18 12/10/2001 210 <1 <1 210 ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 <1.1 710 940 120

MW‐18 01/06/2002 210 <1 <1 210 ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 <1.1 680 940 110

MW‐18 02/07/2002 210 <1 <1 210 ‐‐ 36 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 <1.1 660 930 110

MW‐18 03/08/2002 200 <1 <1 200 ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 <1.1 600 950 110

MW‐18 04/03/2002 220 <1 <1 220 ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 20 710 960 110

MW‐18 05/09/2002 190 <1 <1 190 ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 710 940 100

Page 71 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐18 06/06/2002 180 <1 <1 180 ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1.1 680 940 110

MW‐18 07/03/2002 180 <1 <1 180 ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 <1.1 670 950 110

MW‐18 08/10/2002 360 <1 <1 360 ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 37 <1.1 690 920 110

MW‐18 09/06/2002 200 <1 <1 200 ‐‐ 29 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1.1 690 930 99

MW‐18 10/09/2002 190 <1 <1 190 ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 <1.1 720 920 110

MW‐18 11/06/2002 200 <1 <1 200 ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 <1.1 710 920 110

MW‐18 12/03/2002 200 <1 <1 200 ‐‐ 23 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 <1.1 740 920 110

MW‐18 01/07/2003 190 <1 <1 190 ‐‐ 28 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 <1.1 400 910 110

MW‐18 02/04/2003 200 <1 <1 200 ‐‐ 30 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 <1.1 780 920 100

MW‐18 03/05/2003 190 <1 <1 190 ‐‐ 30 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 <1.1 700 920 110

MW‐18 04/02/2003 240 <1 <1 240 ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 680 940 100

MW‐18 05/02/2003 210 <1 <1 210 ‐‐ 28 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 <1.1 700 910 100

MW‐18 06/06/2003 200 <1 <1 200 ‐‐ 28 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1.1 710 910 99

MW‐18 07/01/2003 210 <1 <1 210 ‐‐ 26 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1.1 730 900 98

MW‐18 08/07/2003 210 <1 <1 210 ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 650 860 87

MW‐18 09/04/2003 190 <1 <1 190 ‐‐ 25 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 <1.1 590 840 84

MW‐18 10/01/2003 190 <1 <1 190 ‐‐ 26 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 690 830 89

MW‐18 11/04/2003 180 <1 <1 180 ‐‐ 26 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1.1 690 840 91

MW‐18 12/02/2003 180 <1 <1 180 ‐‐ 25 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 <1.1 610 830 93

MW‐18 01/13/2004 200 <1 <1 200 ‐‐ 26 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 37 <1.1 710 880 100

MW‐18 02/04/2004 190 <1 <1 190 ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 <1 610 870 100

MW‐18 03/02/2004 190 <1 <1 190 ‐‐ 25 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 <1 650 860 98

MW‐18 04/06/2004 180 <1 <1 180 ‐‐ 26 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1 640 850 98

MW‐18 05/12/2004 180 <1 <1 180 ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1 630 860 94

MW‐18 06/03/2004 160 <1 <1 160 ‐‐ 28 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1 620 860 95

MW‐18 07/08/2004 180 <1 <1 180 ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1 680 820 90

MW‐18 08/05/2004 170 <1 <1 170 ‐‐ 30 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 <1 640 840 96

MW‐18 09/02/2004 200 <1 <1 200 ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 <1 680 840 96

MW‐18 10/06/2004 150 <1 <1 150 ‐‐ 30 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 <1 600 840 94

MW‐18 11/04/2004 180 <1 <1 180 ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1 680 820 88

MW‐18 12/01/2004 170 <1 <1 170 ‐‐ 29 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1 650 840 88

MW‐18 01/14/2005 180 <1 <1 180 ‐‐ 36 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 <1 620 840 98

MW‐18 02/02/2005 170 <1 <1 170 ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1 620 840 94

MW‐18 03/09/2005 170 <1 <1 170 ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 <1 660 850 96

MW‐18 04/06/2005 200 <1 <1 200 ‐‐ 34 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1 670 850 91

Page 72 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐18 05/06/2005 170 <1 <1 170 ‐‐ 34 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1 650 840 91

MW‐18 06/03/2005 150 <1 <1 150 ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1 630 850 93

MW‐18 07/22/2005 160 <1 <1 160 ‐‐ 34 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 <1 650 860 97

MW‐18 08/05/2005 180 <1 <1 180 ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1 720 860 93

MW‐18 09/09/2005 180 <1 <1 180 ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1 770 850 91

MW‐18 10/05/2005 170 <1 <1 170 ‐‐ 35 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 <1 570 850 95

MW‐18 11/10/2005 170 <1 <1 170 ‐‐ 35 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1 680 870 93

MW‐18 12/08/2005 170 <1 <1 170 ‐‐ 37 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 <1 640 860 98

MW‐18 01/04/2006 120 <1 <1 120 ‐‐ 35 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1 680 870 95

MW‐18 02/08/2006 66 <1 <1 66 ‐‐ 34 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 1.7 950 850 110

MW‐18 03/15/2006 170 <1 <1 170 ‐‐ 36 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1 640 850 96

MW‐18 08/03/2006 200 <10 <10 200 ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.3 570 863 97

MW‐18 09/05/2006 170 19 <5.0 190 ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.33 620 843 94

MW‐18 10/09/2006 180 <5.0 <5.0 180 ‐‐ 37 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.29 580 822 92

MW‐18 11/06/2006 180 <5.0 <5.0 180 ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.2 630 786 85

MW‐18 12/11/2006 180 <5.0 <5.0 180 ‐‐ 38 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.20 590 846 96

MW‐18 01/03/2007 180 <5 <5 180 ‐‐ 30 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 590 836 91

MW‐18 02/05/2007 180 <5 <5 180 ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 580 823 96

MW‐18 03/05/2007 190 <5 <5 190 ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 610 815 99

MW‐18 04/05/2007 180 <5 <5 180 ‐‐ 30 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 570 851 96

MW‐18 05/03/2007 190 <5 <5 190 ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.28 620 838 97

MW‐18 06/07/2007 180 <5 <5 180 ‐‐ 29 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.39 600 865 95

MW‐18 07/02/2007 180 <5 <5 180 ‐‐ 30 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.38 600 836 94

MW‐18 08/02/2007 190 <5 <5 190 ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 600 837 95

MW‐18 09/10/2007 180 <5 <5 180 ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 580 841 96

MW‐18 10/08/2007 170 <5 <5 170 ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 600 816 93

MW‐18 11/07/2007 180 <5 <5 180 ‐‐ 33 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 640 804 91

MW‐18 12/06/2007 170 <2.5 <2.5 170 ‐‐ 34 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.21 610 782 87

MW‐18 01/14/2008 180 <5 <5 180 ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 640 815 96

MW‐18 02/07/2008 180 <2.5 <2.5 180 ‐‐ 29 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 Jo 610 867 87

MW‐18 03/04/2008 180 <5 <5 180 ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.21 640 852 94

MW‐18 04/10/2008 140 <2.5 <2.5 140 ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 610 852 96

MW‐18 05/05/2008 180 <2.5 <2.5 180 ‐‐ 30 92 <0.05 30 <0.01 Jo 3.6 38 ‐‐ ‐‐ ‐‐ 0.25 580 857 94

MW‐18 06/03/2008 180 <5.0 <5.0 180 ‐‐ 31 89 <0.050 30 <0.010 3.3 38 ‐‐ ‐‐ ‐‐ <0.20 620 831 92

MW‐18 07/01/2008 170 <5.0 <5.0 170 ‐‐ 31 86 <0.050 29 <0.010 Jo 3.8 39 ‐‐ ‐‐ ‐‐ <0.20 Jo 600 842 89

Page 73 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐18 08/04/2008 180 <5.0 <5.0 180 ‐‐ 32 82 <0.050 27 <0.010 3.1 36 ‐‐ ‐‐ ‐‐ <0.20 580 841 88

MW‐18 09/08/2008 170 <2.5 <2.5 170 ‐‐ 32 88 <0.050 30 <0.010 2.9 39 ‐‐ ‐‐ ‐‐ 0.21 630 838 89

MW‐18 10/09/2008 160 <2.5 <2.5 160 ‐‐ 32 78 <0.050 26 <0.010 Jo 2.9 34 ‐‐ ‐‐ ‐‐ 0.25 630 836 86

MW‐18 11/04/2008 170 <2.5 <2.5 170 ‐‐ 31 86 <0.050 29 <0.010 Jo 2.9 38 ‐‐ ‐‐ ‐‐ <0.20 600 825 86

MW‐18 12/03/2008 170 <5.0 <5.0 170 ‐‐ 34 84 <0.050 28 <0.010 Jo 3.4 38 ‐‐ ‐‐ ‐‐ <0.20 560 817 93

MW‐18 01/13/2009 170 <4.1 <4.1 170 ‐‐ 32 87 <0.050 30 <0.010 3.0 37 ‐‐ ‐‐ ‐‐ 0.27 620 822 93

MW‐18 02/04/2009 170 <4.1 <4.1 170 ‐‐ 29 90 <0.050 31 <0.010 Jo 3.1 40 ‐‐ ‐‐ ‐‐ 0.24 540 767 89

MW‐18 03/04/2009 170 <4.1 <4.1 170 ‐‐ 33 87 <0.050 29 <0.010 2.9 37 ‐‐ ‐‐ ‐‐ 0.23 590 828 98

MW‐18 04/13/2009 170 <4.1 <4.1 170 ‐‐ 32 85 <0.050 28 <0.010 3.0 39 ‐‐ ‐‐ ‐‐ <0.20 Jo 640 800 95

MW‐18 05/04/2009 170 <4.1 <4.1 170 ‐‐ 32 88 <0.050 30 <0.010 3.0 39 ‐‐ ‐‐ ‐‐ 0.22 640 824 94

MW‐18 06/08/2009 170 <4.1 <4.1 170 ‐‐ 31 86 <0.05 28 <0.01 2.9 38 ‐‐ ‐‐ ‐‐ 0.22 600 819 94

MW‐18 07/13/2009 170 <4.1 <4.1 170 ‐‐ 29 86 <0.050 29 <0.010 Jo 3.1 38 ‐‐ ‐‐ ‐‐ <0.20 Jo 640 837 87

MW‐18 08/04/2009 170 <4.1 <4.1 170 ‐‐ 29 86 <0.05 29 <0.01 Jo 2.7 37 ‐‐ ‐‐ ‐‐ <0.2 Jo 700 826 91

MW‐18 09/08/2009 180 <8.2 <8.2 180 ‐‐ 28 96 <0.050 32 <0.010 Jo 3.5 42 ‐‐ ‐‐ ‐‐ <0.20 Jo 590 845 92

MW‐18 10/07/2009 180 <4.1 <4.1 180 ‐‐ 29 88 <0.050 31 0.018 3.0 38 ‐‐ ‐‐ ‐‐ <0.20 Jo 640 799 88

MW‐18 11/09/2009 170 <4.1 <4.1 170 ‐‐ 28 90 <0.050 32 <0.010 Jo 3.2 35 ‐‐ ‐‐ ‐‐ <0.20 Jo 630 813 88

MW‐18 12/08/2009 170 <4.1 <4.1 170 ‐‐ 28 87 <0.050 30 <0.010 Jo 3.1 38 ‐‐ ‐‐ ‐‐ 0.2 570 798 91

MW‐18 01/05/2010 170 <4.1 <4.1 170 ‐‐ 29 80 <0.050 27 <0.010 Jo 3.3 37 ‐‐ ‐‐ ‐‐ <0.20 Jo 610 826 92

MW‐18 02/10/2010 180 <4.1 <4.1 180 ‐‐ 28 91 <0.050 32 0.015 3.9 43 ‐‐ ‐‐ ‐‐ <0.20 660 825 92

MW‐18 03/08/2010 170 <4.1 <4.1 170 ‐‐ 28 86 <0.050 30 <0.010 Jo 3.1 37 ‐‐ ‐‐ ‐‐ 0.27 610 833 93

MW‐18 04/15/2010 170 <4.1 ‐‐ 170 ‐‐ 27 91 <0.05 31 <0.01 3.1 40 ‐‐ ‐‐ ‐‐ <0.20 Jo 630 804 92

MW‐18 07/08/2010 170 <4.1 ‐‐ 170 ‐‐ 27 85 <0.05 30 <0.01 2.9 37 ‐‐ ‐‐ ‐‐ <0.20 Jo 560 799 94

MW‐18 10/27/2010 160 <4.1 ‐‐ 160 ‐‐ 31 87 <0.05 Jo 30 <0.01 3.2 37 ‐‐ ‐‐ ‐‐ <0.20 610 818 88

MW‐18 01/19/2011 170 <4.1 ‐‐ 170 ‐‐ 28 89 <0.05 31 <0.01 3.3 40 ‐‐ ‐‐ ‐‐ <0.20 650 807 89

MW‐18 04/04/2011 170 <4.1 ‐‐ 170 ‐‐ 28 84 <0.05 29 <0.01 Jo 2.9 40 ‐‐ ‐‐ ‐‐ <0.20 Jo 600 811 88

MW‐18 07/07/2011 170 <4.1 ‐‐ 170 ‐‐ 23 85 <0.05 29 <0.01 Jo 3.2 40 ‐‐ ‐‐ 31 <0.20 Jo 560 788 79

MW‐18 10/04/2011 170 <4.1 ‐‐ 170 ‐‐ 30 83 <0.05 28 <0.01 2.9 38 ‐‐ ‐‐ 34 <0.20 Jo 590 814 88

MW‐18 01/19/2012 160 <4.1 ‐‐ 160 ‐‐ 29 83 <0.05 28 <0.01 2.9 38 ‐‐ ‐‐ 32 <0.20 Jo 580 827 81

MW‐18 04/04/2012 160 <4.1 ‐‐ 160 ‐‐ 31 83 <0.05 29 <0.01 Jo 2.9 36 ‐‐ ‐‐ 32 <0.20 Jo 580 791 87

MW‐18 07/23/2012 160 <4.1 ‐‐ 160 ‐‐ 30 81 <0.05 29 <0.01 Jo 2.9 39 ‐‐ ‐‐ 33 <0.20 Jo 560 806 80

MW‐18 10/15/2012 160 <4.1 ‐‐ 160 ‐‐ 33 84 <0.05 Jo 28 <0.01 Jo 2.9 40 ‐‐ ‐‐ 31 <0.20 Jo 540 786 80

MW‐18 01/22/2013 160 <4.1 ‐‐ 160 ‐‐ 34 82 <0.05 28 <0.01 Jo 3.0 41 ‐‐ ‐‐ 32 <0.20 Jo 580 799 81

MW‐18 04/17/2013 160 <4.1 ‐‐ 160 ‐‐ 34 83 <0.05 28 <0.01 Jo 2.9 39 ‐‐ ‐‐ 34 0.21 540 769 84

MW‐18 07/17/2013 150 <4.1 ‐‐ 150 ‐‐ 39 80 <0.05 27 <0.01 Jo 2.9 38 ‐‐ ‐‐ 31 <0.20 550 783 71

MW‐18 10/21/2013 150 <4.1 ‐‐ 150 ‐‐ 39 79 <0.05 27 <0.01 2.8 38 ‐‐ ‐‐ 31 <0.20 Jo 490 814 75

Page 74 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐18 01/22/2014 150 <4.1 ‐‐ 150 ‐‐ 44 77 <0.05 Jo 26 <0.01 Jo 2.8 42 ‐‐ ‐‐ 28 <0.20 Jo 480 751 66

MW‐18 04/22/2014 160 <4.1 ‐‐ 160 ‐‐ 41 75 <0.05 25 <0.01 Jo 2.8 41 ‐‐ ‐‐ 28 <0.20 Jo 560 812 62

MW‐18 07/21/2014 150 <4.1 ‐‐ 150 ‐‐ 50 79 <0.05 26 <0.01 Jo 3.0 45 ‐‐ ‐‐ 28 <0.20 570 830 65

MW‐18 10/20/2014 150 <4.1 ‐‐ 150 ‐‐ 44 81 <0.05 27 0.014 3.0 46 ‐‐ ‐‐ 29 <0.20 Jo 460 794 55

MW‐18 01/21/2015 160 <4.1 ‐‐ 160 ‐‐ 50 72 <0.05 23 <0.01 Jo 2.7 39 ‐‐ ‐‐ 29 0.29 490 794 65

MW‐18 04/15/2015 160 <4.1 ‐‐ 160 ‐‐ 55 80 <0.05 27 0.024 3.0 47 ‐‐ ‐‐ 27 0.3 550 807 62

MW‐18 07/22/2015 160 <4.1 ‐‐ 160 ‐‐ 55 86 <0.05 27 0.02 3.3 51 ‐‐ ‐‐ 27 0.32 530 838 61

MW‐18 10/15/2015 150 <4.1 ‐‐ 150 ‐‐ 53 72 <0.05 24 <0.01 Jo 2.7 41 ‐‐ ‐‐ 28 <0.20 Jo 580 780 61

MW‐18 01/20/2016 150 <4.1 ‐‐ 150 ‐‐ 48 75 <0.05 25 <0.01 Jo 2.8 41 ‐‐ ‐‐ 28 <0.20 Jo 550 794 59

MW‐18 04/14/2016 160 <4.1 ‐‐ 160 ‐‐ 50 85 <0.05 27 <0.01 Jo 3.0 45 ‐‐ ‐‐ 28 0.53 540 791 59

MW‐18 07/18/2016 170 <4.1 ‐‐ 170 ‐‐ 52 77 <0.05 23 0.011 2.9 44 ‐‐ ‐‐ 27 0.25 560 822 53

MW‐18 10/12/2016 170 <4.1 ‐‐ 170 ‐‐ 58 85 <0.05 28 0.011 3.0 47 ‐‐ ‐‐ 26 0.25 550 797 61

MW‐19 01/20/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 10 ‐‐ ‐‐ ‐‐ ‐‐

MW‐19 02/09/1998 270 <1 <1 270 ‐‐ 91 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1.1 640 1100 58

MW‐19 03/19/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 110 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 1.1 830 1100 ‐‐

MW‐19 04/29/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 92 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 <1.1 770 1100 ‐‐

MW‐19 05/20/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 64 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 660 930 ‐‐

MW‐19 06/16/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 69 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 <1.1 650 940 ‐‐

MW‐19 07/28/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 80 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 1.1 670 1000 ‐‐

MW‐19 08/21/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 88 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 47 <1.1 770 1200 ‐‐

MW‐19 09/24/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 120 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 45 1.2 880 1400 ‐‐

MW‐19 10/22/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 82 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1.1 690 1000 ‐‐

MW‐19 11/25/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 74 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 1.1 700 990 ‐‐

MW‐19 12/15/1998 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 78 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 1.5 700 990 ‐‐

MW‐19 02/16/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 65 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 <1.1 590 890 ‐‐

MW‐19 05/23/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 100 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 <1.1 840 1200 ‐‐

MW‐19 08/23/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 88 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 <1.1 800 1200 ‐‐

MW‐19 11/22/1999 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 96 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 <1.1 800 1200 ‐‐

MW‐19 02/17/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 66 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 <1.1 660 990 ‐‐

MW‐19 05/02/2000 280 <1 <1 280 ‐‐ 81 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 750 1100 61

MW‐19 08/08/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 79 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1.1 770 1200 ‐‐

MW‐19 09/15/2000 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 86 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 44 <1.1 800 1200 ‐‐

MW‐19 11/22/2000 260 <1 <1 260 ‐‐ 92 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 2.4 820 1200 ‐‐

MW‐19 12/12/2000 280 <1 <1 280 ‐‐ 81 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 <1.1 780 1200 ‐‐

MW‐19 01/06/2001 280 <1 <1 280 ‐‐ 75 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 <1.1 770 1100 ‐‐

Page 75 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐19 02/06/2001 270 <1 <1 270 ‐‐ 76 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 ‐‐ 800 1100 73

MW‐19 03/25/2001 240 <1 <1 240 ‐‐ 53 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 650 980 59

MW‐19 04/16/2001 240 <1 <1 240 ‐‐ 60 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1.1 710 1000 61

MW‐19 05/23/2001 260 <1 <1 260 ‐‐ 57 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1.1 700 1000 63

MW‐19 06/25/2001 240 <1 <1 240 ‐‐ 53 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 1.8 660 950 58

MW‐19 07/19/2001 250 <1 <1 250 ‐‐ 52 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 <1.1 690 940 64

MW‐19 08/01/2001 220 <1 <1 220 ‐‐ 54 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 4.1 690 960 66

MW‐19 09/05/2001 250 <1 <1 250 ‐‐ 57 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1.1 740 1000 76

MW‐19 10/02/2001 260 <1 <1 260 ‐‐ 50 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 3 770 990 76

MW‐19 11/06/2001 260 <1 <1 260 ‐‐ 58 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 41 <1.1 740 1000 87

MW‐19 12/05/2001 250 <1 <1 250 ‐‐ 59 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 1.3 680 980 72

MW‐19 01/04/2002 220 <1 <1 220 ‐‐ 44 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1.1 670 960 69

MW‐19 02/05/2002 220 <1 <1 220 ‐‐ 48 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 640 970 71

MW‐19 03/05/2002 230 <1 <1 230 ‐‐ 43 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 <1.1 650 940 65

MW‐19 04/03/2002 240 <1 <1 240 ‐‐ 47 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1.1 690 990 74

MW‐19 05/08/2002 240 <1 <1 240 ‐‐ 44 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 34 <1.1 660 970 70

MW‐19 06/04/2002 250 <1 <1 250 ‐‐ 47 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 <1.1 680 1000 78

MW‐19 07/03/2002 230 <1 <1 230 ‐‐ 45 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1.1 680 970 72

MW‐19 08/08/2002 240 <1 <1 240 ‐‐ 48 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 <1.1 710 1000 80

MW‐19 09/05/2002 250 <1 <1 250 ‐‐ 46 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1.1 770 1000 81

MW‐19 10/09/2002 250 <1 <1 250 ‐‐ 48 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 39 <1.1 760 1000 86

MW‐19 11/06/2002 240 <1 <1 240 ‐‐ 45 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 38 <1.1 740 980 83

MW‐19 12/03/2002 250 <1 <1 250 ‐‐ 40 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 36 <1.1 730 1000 85

MW‐19 01/06/2003 220 <1 <1 220 ‐‐ 42 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 35 <1.1 820 960 79

MW‐19 02/04/2003 240 <1 <1 240 ‐‐ 39 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 <1.1 660 910 67

MW‐19 03/04/2003 240 <1 <1 240 ‐‐ 39 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 <1.1 730 910 68

MW‐19 04/01/2003 230 <1 <1 230 ‐‐ 41 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 33 <1.1 770 980 82

MW‐19 05/01/2003 240 <1 <1 240 ‐‐ 39 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 <1.1 680 920 69

MW‐19 06/03/2003 240 <1 <1 240 ‐‐ 30 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 23 <1.1 690 880 64

MW‐19 07/01/2003 230 <1 <1 230 ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 24 <1.1 620 820 52

MW‐19 08/12/2003 260 <1 <1 260 ‐‐ 39 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 28 <1.1 670 930 74

MW‐19 09/04/2003 250 <1 <1 250 ‐‐ 39 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 1.2 680 930 76

MW‐19 10/01/2003 240 <1 <1 240 ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 24 <1.1 580 790 52

MW‐19 11/04/2003 260 <1 <1 260 ‐‐ 40 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 4.5 780 940 80

MW‐19 12/02/2003 270 <1 <1 270 ‐‐ 38 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 <1.1 660 950 78

Page 76 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐19 01/13/2004 240 <1 <1 240 ‐‐ 36 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 <1.1 670 910 70

MW‐19 02/04/2004 250 <1 <1 250 ‐‐ 34 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 28 <1 610 880 62

MW‐19 03/02/2004 220 <1 <1 220 ‐‐ 34 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 28 <1 630 880 64

MW‐19 04/06/2004 270 <1 <1 270 ‐‐ 39 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 <1 760 930 74

MW‐19 05/11/2004 210 <1 <1 210 ‐‐ 39 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 <1 670 930 69

MW‐19 06/01/2004 240 <1 <1 240 ‐‐ 39 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 <1 680 970 77

MW‐19 07/06/2004 270 <1 <1 270 ‐‐ 36 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 <1 700 940 78

MW‐19 08/05/2004 280 <1 <1 280 ‐‐ 36 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 <1 690 940 77

MW‐19 09/02/2004 240 <1 <1 240 ‐‐ 38 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1 760 940 79

MW‐19 10/05/2004 220 <1 <1 220 ‐‐ 40 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1 800 980 84

MW‐19 11/02/2004 270 <1 <1 270 ‐‐ 37 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 <1 720 980 77

MW‐19 12/01/2004 250 <1 <1 250 ‐‐ 41 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1 780 990 80

MW‐19 01/12/2005 250 <1 <1 250 ‐‐ 43 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1 700 970 80

MW‐19 02/01/2005 220 <1 <1 220 ‐‐ 45 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1 690 970 80

MW‐19 03/08/2005 260 <1 <1 260 ‐‐ 43 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 <1 710 950 76

MW‐19 04/05/2005 260 <1 <1 260 ‐‐ 40 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 31 <1 770 970 78

MW‐19 05/04/2005 250 <1 <1 250 ‐‐ 42 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1 690 970 82

MW‐19 06/02/2005 210 <1 <1 210 ‐‐ 43 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 32 <1 710 970 82

MW‐19 07/20/2005 240 <1 <1 240 ‐‐ 39 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 <1 680 950 79

MW‐19 08/03/2005 240 <1 <1 240 ‐‐ 40 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 <1 740 960 78

MW‐19 09/07/2005 260 <1 <1 260 ‐‐ 38 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 <1 750 950 77

MW‐19 10/04/2005 250 <1 <1 250 ‐‐ 31 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 27 <1 630 890 71

MW‐19 11/09/2005 260 <1 <1 260 ‐‐ 35 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 29 <0.5 710 940 76

MW‐19 12/07/2005 250 <1 <1 250 ‐‐ 37 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 <1 700 940 77

MW‐19 01/04/2006 210 <1 <1 210 ‐‐ 36 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 28 <1 740 940 77

MW‐19 02/06/2006 260 <1 <1 260 ‐‐ 39 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 <1 640 940 77

MW‐19 03/15/2006 260 <1 <1 260 ‐‐ 38 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 30 <1 720 950 76

MW‐19 08/03/2006 270 <10 <10 270 ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.54 590 866 68

MW‐19 09/05/2006 230 27 <5.0 260 ‐‐ 25 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.36 580 835 66

MW‐19 10/09/2006 270 <5.0 <5.0 270 ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.52 610 834 67

MW‐19 11/06/2006 280 <5.0 <5.0 280 ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.44 640 827 68

MW‐19 12/11/2006 280 <5.0 <5.0 280 ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.20 630 887 71

MW‐19 01/03/2007 280 <5 <5 280 ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.49 620 877 67

MW‐19 02/05/2007 270 <5 <5 270 ‐‐ 30 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.28 590 851 67

MW‐19 03/05/2007 270 <5 <5 270 ‐‐ 30 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.38 620 836 62

Page 77 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐19 04/05/2007 270 <5 <5 270 ‐‐ 30 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.44 520 862 63

MW‐19 05/03/2007 270 <5 <5 270 ‐‐ 32 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.63 600 857 66

MW‐19 06/07/2007 270 <5 <5 270 ‐‐ 27 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.68 590 883 64

MW‐19 07/02/2007 260 <5 <5 260 ‐‐ 28 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.57 550 849 64

MW‐19 08/02/2007 270 <5 <5 270 ‐‐ 25 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.43 580 830 62

MW‐19 09/10/2007 270 <5 <5 270 ‐‐ 23 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.34 570 817 60

MW‐19 10/08/2007 260 <5 <5 260 ‐‐ 22 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.4 580 808 60

MW‐19 11/07/2007 270 <5 <5 270 ‐‐ 25 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.49 620 819 64

MW‐19 12/06/2007 270 <5 <5 270 ‐‐ 26 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.71 600 812 63

MW‐19 01/14/2008 270 <5 <5 270 ‐‐ 28 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ <0.2 Jo 600 808 63

MW‐19 02/07/2008 280 <5 <5 280 ‐‐ 28 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.51 600 884 61

MW‐19 03/04/2008 270 <5 <5 270 ‐‐ 30 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.35 580 873 62

MW‐19 04/10/2008 260 <5 <5 260 ‐‐ 30 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.29 670 849 61

MW‐19 05/05/2008 260 <5 <5 260 ‐‐ 29 100 <0.05 24 0.011 2.5 47 ‐‐ ‐‐ ‐‐ 0.49 570 852 60

MW‐19 06/03/2008 250 <5.0 <5.0 250 ‐‐ 28 96 <0.050 24 <0.010 Jo 2.4 46 ‐‐ ‐‐ ‐‐ 0.47 570 823 57

MW‐19 07/01/2008 260 <5.0 <5.0 260 ‐‐ 28 100 <0.050 25 <0.010 Jo 2.1 44 ‐‐ ‐‐ ‐‐ 0.46 580 858 60

MW‐19 08/04/2008 250 <5.0 <5.0 250 ‐‐ 27 93 <0.050 22 <0.010 Jo 2.0 38 ‐‐ ‐‐ ‐‐ 0.23 570 840 58

MW‐19 09/08/2008 250 <5.0 <5.0 250 ‐‐ 27 100 <0.050 25 <0.010 Jo 2.1 44 ‐‐ ‐‐ ‐‐ 0.52 580 853 60

MW‐19 10/09/2008 230 <5.0 <5.0 230 ‐‐ 25 86 <0.050 21 0.012 1.9 36 ‐‐ ‐‐ ‐‐ 0.52 530 818 55

MW‐19 11/04/2008 240 <5.0 <5.0 240 ‐‐ 23 93 <0.050 23 0.015 2.2 41 ‐‐ ‐‐ ‐‐ 0.55 570 813 54

MW‐19 12/03/2008 240 <2.5 <2.5 240 ‐‐ 25 93 <0.050 23 0.017 2.3 44 ‐‐ ‐‐ ‐‐ 0.45 570 812 61

MW‐19 01/13/2009 240 <4.1 <4.1 240 ‐‐ 24 92 <0.050 23 0.022 2.0 44 ‐‐ ‐‐ ‐‐ 0.56 610 804 60

MW‐19 02/04/2009 240 <4.1 <4.1 240 ‐‐ 24 97 <0.050 24 0.022 2.0 45 ‐‐ ‐‐ ‐‐ 0.48 550 809 58

MW‐19 03/04/2009 240 <4.1 <4.1 240 ‐‐ 28 94 <0.050 23 0.015 2.0 47 ‐‐ ‐‐ ‐‐ 0.46 570 819 62

MW‐19 04/13/2009 230 <4.1 <4.1 230 ‐‐ 26 95 <0.050 24 <0.010 Jo 2.1 45 ‐‐ ‐‐ ‐‐ 0.44 540 770 54

MW‐19 05/04/2009 320 <8.2 <8.2 320 ‐‐ 28 93 <0.050 23 <0.010 Jo 2.1 46 ‐‐ ‐‐ ‐‐ 0.63 580 1190 59

MW‐19 06/08/2009 230 <4.1 <4.1 230 ‐‐ 28 90 <0.05 22 <0.01 Jo 1.9 45 ‐‐ ‐‐ ‐‐ 0.46 560 793 60

MW‐19 07/13/2009 220 <4.1 <4.1 220 ‐‐ 27 89 <0.050 22 <0.010 Jo 2.2 44 ‐‐ ‐‐ ‐‐ 0.51 610 805 52

MW‐19 08/04/2009 220 <4.1 <4.1 220 ‐‐ 27 90 <0.05 22 <0.01 Jo 1.9 43 ‐‐ ‐‐ ‐‐ 0.51 570 782 52

MW‐19 09/08/2009 230 <8.2 <8.2 230 ‐‐ 28 100 <0.050 26 <0.010 Jo 2.3 49 ‐‐ ‐‐ ‐‐ 0.43 560 830 53

MW‐19 10/07/2009 230 <4.1 <4.1 230 ‐‐ 28 95 <0.050 24 0.016 2.0 42 ‐‐ ‐‐ ‐‐ 0.49 540 789 52

MW‐19 11/09/2009 230 <4.1 <4.1 230 ‐‐ 28 91 <0.050 23 0.015 2.1 40 ‐‐ ‐‐ ‐‐ 0.42 600 799 50

MW‐19 12/08/2009 230 <4.1 <4.1 230 ‐‐ 28 94 <0.050 24 0.015 2.1 41 ‐‐ ‐‐ ‐‐ 0.48 580 786 52

MW‐19 01/05/2010 220 <4.1 <4.1 220 ‐‐ 30 84 <0.050 21 0.014 2.1 44 ‐‐ ‐‐ ‐‐ 0.5 580 804 53

MW‐19 02/11/2010 230 <4.1 <4.1 230 ‐‐ 30 93 <0.050 23 0.016 1.9 43 ‐‐ ‐‐ ‐‐ 0.29 590 818 52

Page 78 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐19 03/08/2010 230 <4.1 <4.1 230 ‐‐ 34 94 <0.050 23 0.021 2.2 45 ‐‐ ‐‐ ‐‐ 0.38 610 815 57

MW‐19 04/15/2010 230 <4.1 ‐‐ 230 ‐‐ 33 99 <0.05 25 0.017 2.2 48 ‐‐ ‐‐ ‐‐ 0.24 540 791 55

MW‐19 07/08/2010 230 <4.1 ‐‐ 230 ‐‐ 34 94 <0.05 24 0.018 2.0 42 ‐‐ ‐‐ ‐‐ 0.46 550 838 52

MW‐19 10/27/2010 230 <4.1 ‐‐ 230 ‐‐ 41 97 <0.05 24 0.019 2.1 50 ‐‐ ‐‐ ‐‐ 0.53 620 864 54

MW‐19 01/19/2011 240 <4.1 ‐‐ 240 ‐‐ 43 96 <0.05 25 0.023 2.3 50 ‐‐ ‐‐ ‐‐ 0.46 620 898 58

MW‐19 04/04/2011 240 <4.1 ‐‐ 240 ‐‐ 45 100 <0.05 25 0.02 2.2 55 ‐‐ ‐‐ ‐‐ 0.32 610 902 57

MW‐19 07/07/2011 230 <4.1 ‐‐ 230 ‐‐ 43 99 <0.05 24 0.02 2.4 50 ‐‐ ‐‐ 25 0.58 570 863 50

MW‐19 10/04/2011 240 <4.1 ‐‐ 240 ‐‐ 51 100 <0.05 25 0.028 2.3 50 ‐‐ ‐‐ 27 0.34 600 883 56

MW‐19 01/18/2012 220 <4.1 ‐‐ 220 ‐‐ 57 98 <0.05 Jo 25 0.022 2.1 46 ‐‐ ‐‐ 25 0.55 610 883 51

MW‐19 04/04/2012 230 <4.1 ‐‐ 230 ‐‐ 56 100 <0.05 25 0.022 2.1 46 ‐‐ ‐‐ 25 0.44 600 884 56

MW‐19 07/23/2012 230 <4.1 ‐‐ 230 ‐‐ 60 97 <0.05 25 0.042 2.0 46 ‐‐ ‐‐ 25 0.46 570 890 50

MW‐19 10/16/2012 250 <4.1 ‐‐ 250 ‐‐ 67 110 <0.05 Jo 27 0.018 2.2 47 ‐‐ ‐‐ 19 0.52 600 882 51

MW‐19 01/22/2013 220 <4.1 ‐‐ 220 ‐‐ 58 98 <0.05 24 0.02 1.9 44 ‐‐ ‐‐ 23 0.4 550 829 44

MW‐19 04/18/2013 230 <4.1 ‐‐ 230 ‐‐ 65 100 <0.05 Jo 25 0.03 2.0 43 ‐‐ ‐‐ 22 0.5 560 822 51

MW‐19 07/17/2013 250 <4.1 ‐‐ 250 ‐‐ 67 100 <0.05 25 0.022 2.1 43 ‐‐ ‐‐ 15 0.58 550 844 46

MW‐19 10/21/2013 270 <4.1 ‐‐ 270 ‐‐ 70 98 <0.05 25 0.021 2.0 41 ‐‐ ‐‐ 9.9 0.42 570 882 48

MW‐19 01/22/2014 270 <4.1 ‐‐ 270 ‐‐ 66 100 <0.05 25 0.025 2.0 46 ‐‐ ‐‐ 11 0.53 500 810 46

MW‐19 04/22/2014 280 <4.1 ‐‐ 280 ‐‐ 66 96 <0.05 24 0.022 2.0 43 ‐‐ ‐‐ 8.1 0.45 560 891 47

MW‐19 07/21/2014 280 <4.1 ‐‐ 280 ‐‐ 70 110 <0.05 26 0.023 2.2 46 ‐‐ ‐‐ 7.2 0.41 580 913 47

MW‐19 10/20/2014 280 <4.1 ‐‐ 280 ‐‐ 76 110 <0.05 29 0.024 2.2 47 ‐‐ ‐‐ 7.0 0.69 510 886 46

MW‐19 01/21/2015 280 <4.1 ‐‐ 280 ‐‐ 74 95 <0.05 23 0.024 1.7 39 ‐‐ ‐‐ 7.4 0.5 560 888 46

MW‐19 04/15/2015 300 <4.1 ‐‐ 300 ‐‐ 76 110 <0.05 29 0.032 2.2 48 ‐‐ ‐‐ 7.1 0.5 580 899 46

MW‐19 07/22/2015 310 <8.2 ‐‐ 310 ‐‐ 90 120 <0.05 31 0.03 2.2 46 ‐‐ ‐‐ 5.8 0.52 580 1020 50

MW‐19 10/15/2015 310 <4.1 ‐‐ 310 ‐‐ 93 110 <0.05 28 0.023 2.0 41 ‐‐ ‐‐ 5.7 0.61 610 954 48

MW‐19 01/20/2016 310 <4.1 ‐‐ 310 ‐‐ 93 120 <0.05 29 0.031 2.1 44 ‐‐ ‐‐ 4.5 0.6 660 973 50

MW‐19 04/14/2016 320 <4.1 ‐‐ 320 ‐‐ 100 130 <0.05 32 0.032 2.5 51 ‐‐ ‐‐ 5.0 0.54 620 984 56

MW‐19 07/18/2016 330 <8.2 ‐‐ 330 ‐‐ 96 130 <0.05 30 0.031 2.2 50 ‐‐ ‐‐ 4.5 0.43 680 1030 50

MW‐19 10/12/2016 330 <8.2 ‐‐ 330 ‐‐ 97 130 <0.05 32 0.033 2.5 54 ‐‐ ‐‐ 4.6 0.44 680 1020 52

MW‐21 04/08/2008 42 <1.0 <1.0 42 ‐‐ 26 59 <0.050 15 ‐‐ 5.2 20 ‐‐ ‐‐ 34 <1.0 470 560 49

MW‐21 08/04/2008 28 <2.5 <2.5 28 ‐‐ 37 81 <0.050 Jo 20 <0.010 Jo 7.3 27 ‐‐ ‐‐ ‐‐ 0.33 740 835 84

MW‐21 09/08/2008 38 <2.5 <2.5 38 ‐‐ 37 84 <0.050 21 0.018 7.2 26 ‐‐ ‐‐ ‐‐ 0.53 760 777 78

MW‐21 10/09/2008 31 <2.5 <2.5 31 ‐‐ 45 89 <0.050 23 <0.010 Jo 7.4 25 ‐‐ ‐‐ ‐‐ 0.53 710 869 84

MW‐21 11/04/2008 31 <2.5 <2.5 31 ‐‐ 47 91 <0.050 23 0.011 7.8 25 ‐‐ ‐‐ ‐‐ 0.63 770 863 82

MW‐21 12/03/2008 39 <2.5 <2.5 39 ‐‐ 52 89 <0.050 23 <0.010 Jo 6.8 27 ‐‐ ‐‐ ‐‐ 0.44 730 830 90

MW‐21 01/13/2009 43 <4.1 <4.1 43 ‐‐ 48 86 <0.050 22 0.017 6.5 27 ‐‐ ‐‐ ‐‐ 0.28 780 796 77

Page 79 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐21 02/04/2009 39 <4.1 <4.1 39 ‐‐ 45 87 <0.050 22 0.019 6.5 27 ‐‐ ‐‐ ‐‐ 0.42 640 781 80

MW‐21 03/04/2009 47 <4.1 <4.1 47 ‐‐ 47 82 <0.050 21 <0.010 Jo 5.9 25 ‐‐ ‐‐ ‐‐ 0.39 660 721 73

MW‐21 04/14/2009 44 <4.1 <4.1 44 ‐‐ 39 84 <0.050 23 <0.010 Jo 6.3 25 ‐‐ ‐‐ ‐‐ 0.42 650 705 71

MW‐21 05/04/2009 34 <4.1 <4.1 34 ‐‐ 35 70 <0.050 18 0.012 5.4 23 ‐‐ ‐‐ ‐‐ 0.23 630 644 66

MW‐21 06/08/2009 35 <4.1 <4.1 35 ‐‐ 41 84 <0.05 21 <0.01 6 22 ‐‐ ‐‐ ‐‐ 0.43 670 758 82

MW‐21 07/13/2009 25 <4.1 <4.1 25 ‐‐ 12 32 0.32 8.2 0.019 3.6 12 ‐‐ ‐‐ ‐‐ 0.29 340 331 26

MW‐21 08/04/2009 24 <4.1 <4.1 24 ‐‐ 6.6 18 0.45 4.7 <0.01 Jo 2.4 8.2 ‐‐ ‐‐ ‐‐ 0.37 220 184 14

MW‐21 09/08/2009 54 <8.2 <8.2 54 ‐‐ 15 36 0.19 9.4 0.011 4.1 15 ‐‐ ‐‐ ‐‐ 0.38 300 361 30

MW‐21 11/09/2009 25 <4.1 <4.1 25 ‐‐ 34 72 <0.050 Jo 19 0.013 5.3 21 ‐‐ ‐‐ ‐‐ 0.54 660 652 62

MW‐21 12/08/2009 24 <4.1 <4.1 24 ‐‐ 34 66 0.37 16 0.01 5.0 19 ‐‐ ‐‐ ‐‐ 0.65 570 599 58

MW‐21 01/06/2010 27 <4.1 <4.1 27 ‐‐ 26 51 0.25 12 <0.010 Jo 4.1 19 ‐‐ ‐‐ ‐‐ 0.51 460 484 46

MW‐21 02/10/2010 31 <4.1 <4.1 31 ‐‐ 20 42 0.4 11 0.014 4.9 20 ‐‐ ‐‐ ‐‐ 0.31 420 422 35

MW‐21 03/08/2010 30 <4.1 <4.1 30 ‐‐ 17 35 0.37 8.8 0.01 3.5 17 ‐‐ ‐‐ ‐‐ 0.36 350 375 32

MW‐21 04/15/2010 28 <4.1 ‐‐ 28 ‐‐ 18 40 0.12 10 <0.01 Jo 3.6 19 ‐‐ ‐‐ ‐‐ 0.39 350 413 35

MW‐21 07/08/2010 23 <4.1 ‐‐ 23 ‐‐ 8.8 23 0.27 6.1 <0.01 Jo 3.0 13 ‐‐ ‐‐ ‐‐ 0.34 230 249 14

MW‐21 10/27/2010 32 <4.1 ‐‐ 32 ‐‐ 8.0 21 0.06 5.9 <0.01 Jo 2.8 12 <0.01 ‐‐ ‐‐ <0.20 Jo 210 241 12

MW‐21 01/19/2011 28 <4.1 ‐‐ 28 ‐‐ 6.6 17 <0.05 Jo 5.1 <0.01 2.4 9.9 ‐‐ ‐‐ ‐‐ 0.25 170 202 11

MW‐21 04/04/2011 27 <4.1 ‐‐ 27 ‐‐ 12 25 <0.05 Jo 7.0 <0.01 Jo 2.7 12 ‐‐ ‐‐ ‐‐ 0.34 240 266 15

MW‐21 07/07/2011 37 <4.1 ‐‐ 37 ‐‐ 14 26 <0.05 7.2 <0.01 Jo 3.1 17 ‐‐ ‐‐ 15 0.27 240 293 17

MW‐21 10/04/2011 33 <4.1 ‐‐ 33 ‐‐ 8.6 29 <0.05 Jo 6.9 <0.01 Jo 3.2 17 ‐‐ ‐‐ 20 0.24 280 320 22

MW‐21 11/09/2011 32.0 <5.0 ‐‐ 32.0 <0.20 12.3 37.3 J <0.20 8.54 J <0.015 <10 24.0 J <0.01 ‐‐ 25.8 J‐ <0.20 490 4100 42.5

MW‐21 01/19/2012 34 <4.1 ‐‐ 34 ‐‐ 14 35 0.097 8.7 <0.01 Jo 2.9 15 ‐‐ ‐‐ 24 0.65 200 367 21

MW‐21 04/04/2012 37 <4.1 ‐‐ 37 ‐‐ 19 38 <0.05 Jo 9.4 <0.01 2.9 12 ‐‐ ‐‐ 21 0.29 320 366 24

MW‐21 07/23/2012 31 <4.1 ‐‐ 31 ‐‐ 20 46 <0.05 Jo 12 0.013 4.4 16 ‐‐ ‐‐ 29 0.59 380 451 43

MW‐21 10/15/2012 29 <4.1 ‐‐ 29 ‐‐ 22 84 <0.05 Jo 20 0.014 7.1 27 ‐‐ ‐‐ 52 0.67 630 745 90

MW‐21 01/22/2013 27 <4.1 ‐‐ 27 ‐‐ 31 78 <0.05 17 <0.01 Jo 5.4 27 ‐‐ ‐‐ 50 0.88 680 705 65

MW‐21 04/17/2013 31 <4.1 ‐‐ 31 ‐‐ 46 100 0.052 24 0.011 6.9 28 ‐‐ ‐‐ 62 0.55 760 854 120

MW‐21 07/17/2013 21 <4.1 ‐‐ 21 ‐‐ 37 71 <0.05 19 <0.01 6.7 29 ‐‐ ‐‐ 50 <0.20 620 716 75

MW‐21 10/21/2013 24 <4.1 ‐‐ 24 ‐‐ 51 86 <0.05 24 <0.01 Jo 8.2 30 ‐‐ ‐‐ 63 0.72 730 892 71

MW‐21 01/22/2014 22 <4.1 ‐‐ 22 ‐‐ 59 93 0.069 25 <0.01 Jo 7.9 35 ‐‐ ‐‐ 61 0.69 700 880 90

MW‐21 04/22/2014 27 <4.1 ‐‐ 27 ‐‐ 43 84 <0.05 24 <0.01 7.7 33 ‐‐ ‐‐ 59 0.61 770 899 85

MW‐21 01/21/2015 18 <8.2 ‐‐ 18 ‐‐ 29 130 <0.05 36 <0.01 Jo 7.8 22 ‐‐ ‐‐ 130 0.48 770 1280 86

MW‐22 03/13/2008 190 <1.0 <1.0 190 ‐‐ 210 28 0.14 11 ‐‐ 6.0 220 ‐‐ ‐‐ 4.3 8.1 710 1300 120

MW‐22 08/04/2008 240 <5.0 <5.0 240 ‐‐ 98 29 <0.050 14 0.017 6.3 110 ‐‐ ‐‐ ‐‐ 0.43 510 800 29

MW‐22 09/08/2008 230 <5.0 <5.0 230 ‐‐ 57 32 <0.050 17 0.33 2.9 83 ‐‐ ‐‐ ‐‐ <0.20 Jo 370 633 14

Page 80 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐22 10/09/2008 230 <5.0 <5.0 230 ‐‐ 54 27 <0.050 14 0.28 2.7 76 ‐‐ ‐‐ ‐‐ <0.20 Jo 370 633 13

MW‐22 11/04/2008 230 <5.0 <5.0 230 ‐‐ 62 30 <0.050 15 <0.010 Jo 5.1 85 ‐‐ ‐‐ ‐‐ <0.20 Jo 380 649 14

MW‐22 12/03/2008 250 <2.5 <2.5 250 ‐‐ 53 33 <0.050 17 0.31 2.7 87 ‐‐ ‐‐ ‐‐ <0.20 Jo 420 661 13

MW‐22 01/13/2009 250 <4.1 <4.1 250 ‐‐ 51 36 <0.050 19 0.41 2.5 78 ‐‐ ‐‐ ‐‐ <0.20 Jo 430 649 13

MW‐22 02/04/2009 250 <4.1 <4.1 250 ‐‐ 50 38 <0.050 20 0.4 2.7 84 ‐‐ ‐‐ ‐‐ <0.20 Jo 390 634 12

MW‐22 03/04/2009 260 <4.1 <4.1 260 ‐‐ 52 39 <0.050 20 0.38 2.6 81 ‐‐ ‐‐ ‐‐ <0.20 410 690 12

MW‐22 04/14/2009 260 <4.1 <4.1 260 ‐‐ 47 39 <0.050 20 0.43 2.5 79 ‐‐ ‐‐ ‐‐ <0.20 Jo 420 646 12

MW‐22 05/04/2009 270 <4.1 <4.1 270 ‐‐ 52 40 <0.050 21 0.39 2.6 83 ‐‐ ‐‐ ‐‐ <0.20 Jo 440 681 12

MW‐22 06/09/2009 270 <4.1 <4.1 270 ‐‐ 47 38 <0.05 20 0.35 2.2 77 ‐‐ ‐‐ ‐‐ 0.24 430 645 12

MW‐22 07/14/2009 260 <4.1 <4.1 260 ‐‐ 50 35 <0.050 19 0.34 3.0 84 ‐‐ ‐‐ ‐‐ <0.20 Jo 410 655 11

MW‐22 08/04/2009 270 <4.1 <4.1 270 ‐‐ 49 34 <0.05 Jo 18 0.31 2.4 86 ‐‐ ‐‐ ‐‐ <0.2 Jo 420 670 11

MW‐22 09/08/2009 300 <8.2 <8.2 300 ‐‐ 51 38 <0.050 20 0.34 2.8 96 ‐‐ ‐‐ ‐‐ <0.20 450 721 11

MW‐22 10/07/2009 270 <4.1 <4.1 270 ‐‐ 43 36 <0.050 20 0.34 2.7 84 ‐‐ ‐‐ ‐‐ <0.20 410 658 11

MW‐22 11/10/2009 280 <4.1 <4.1 280 ‐‐ 46 40 <0.050 22 0.4 2.9 83 ‐‐ ‐‐ ‐‐ <0.20 430 681 10

MW‐22 12/08/2009 290 <4.1 <4.1 290 ‐‐ 46 40 <0.050 21 0.42 2.5 78 ‐‐ ‐‐ ‐‐ <0.20 Jo 420 697 11

MW‐22 01/05/2010 300 <4.1 <4.1 300 ‐‐ 56 46 <0.050 24 0.46 2.7 83 ‐‐ ‐‐ ‐‐ <0.20 490 771 11

MW‐22 02/10/2010 310 <4.1 <4.1 310 ‐‐ 54 46 <0.050 24 0.46 2.6 77 ‐‐ ‐‐ ‐‐ <0.20 480 765 11

MW‐22 03/08/2010 300 <4.1 <4.1 300 ‐‐ 61 48 <0.050 25 0.51 2.7 78 ‐‐ ‐‐ ‐‐ <0.20 470 770 13

MW‐22 04/15/2010 280 <4.1 ‐‐ 280 ‐‐ 61 49 <0.05 25 0.48 2.6 88 ‐‐ ‐‐ ‐‐ <0.20 450 737 12

MW‐22 07/08/2010 300 <4.1 ‐‐ 300 ‐‐ 77 49 <0.05 25 0.51 2.7 85 ‐‐ ‐‐ ‐‐ <0.20 500 818 15

MW‐22 10/28/2010 280 <4.1 ‐‐ 280 ‐‐ 72 51 <0.05 26 0.54 3.1 88 ‐‐ ‐‐ ‐‐ <0.20 520 779 14

MW‐22 01/19/2011 290 <4.1 ‐‐ 290 ‐‐ 65 50 <0.05 26 0.54 2.6 73 ‐‐ ‐‐ ‐‐ <0.20 500 788 15

MW‐22 04/04/2011 310 <4.1 ‐‐ 310 ‐‐ 72 58 <0.05 29 0.63 3.2 87 ‐‐ ‐‐ ‐‐ <0.20 510 839 16

MW‐22 07/07/2011 320 <4.1 ‐‐ 320 ‐‐ 72 54 <0.05 27 0.57 3.0 89 ‐‐ ‐‐ 1.3 <0.20 Jo 500 852 16

MW‐22 10/04/2011 310 <4.1 ‐‐ 310 ‐‐ 75 53 <0.05 27 0.56 3.0 87 ‐‐ ‐‐ 1.2 <0.20 Jo 500 820 17

MW‐22 01/18/2012 320 <4.1 ‐‐ 320 ‐‐ 76 58 <0.05 Jo 29 0.59 2.9 87 ‐‐ ‐‐ 0.79 <0.20 Jo 520 849 18

MW‐22 04/04/2012 320 <4.1 ‐‐ 320 ‐‐ 79 57 <0.05 29 0.56 2.6 80 ‐‐ ‐‐ 0.9 <0.20 480 833 18

MW‐22 07/23/2012 350 <4.1 ‐‐ 350 ‐‐ 90 57 <0.05 30 0.54 2.8 100 ‐‐ ‐‐ 0.61 <0.20 540 932 16

MW‐22 10/15/2012 380 <4.1 ‐‐ 380 ‐‐ 88 67 <0.05 Jo 34 0.68 3.0 100 ‐‐ ‐‐ <0.10 <0.20 590 966 16

MW‐22 01/22/2013 310 <4.1 ‐‐ 310 ‐‐ 93 48 <0.05 24 1.2 3.8 110 ‐‐ ‐‐ <0.10 <0.20 520 870 12

MW‐22 04/18/2013 390 <4.1 ‐‐ 390 ‐‐ 93 71 <0.05 35 0.76 3.1 96 ‐‐ ‐‐ <0.10 <0.20 560 921 18

MW‐22 07/17/2013 410 <8.2 ‐‐ 410 ‐‐ 99 78 <0.05 40 0.85 3.3 96 ‐‐ ‐‐ <0.10 <0.20 Jo 650 1050 16

MW‐22 10/21/2013 390 <8.2 ‐‐ 390 ‐‐ 110 62 <0.05 33 0.76 2.8 120 ‐‐ ‐‐ <0.10 <0.20 640 1000 15

MW‐22 01/22/2014 400 <4.1 ‐‐ 400 ‐‐ 94 74 0.053 38 0.91 3.1 100 ‐‐ ‐‐ <0.10 <0.20 Jo 600 978 17

MW‐22 04/22/2014 390 <8.2 ‐‐ 390 ‐‐ 96 71 <0.05 37 0.92 3.0 100 ‐‐ ‐‐ <0.10 <0.20 Jo 620 1070 16

Page 81 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐22 07/21/2014 390 <8.2 ‐‐ 390 ‐‐ 110 72 <0.05 37 0.88 3.2 120 ‐‐ ‐‐ <0.10 <0.20 650 1110 16

MW‐22 10/20/2014 370 <4.1 ‐‐ 370 ‐‐ 97 69 <0.05 35 0.92 3.1 110 ‐‐ ‐‐ <0.10 <0.20 510 989 16

MW‐22 01/21/2015 380 <4.1 ‐‐ 380 ‐‐ 89 66 <0.05 33 0.76 2.8 90 ‐‐ ‐‐ <0.10 Jo <0.20 Jo 610 994 17

MW‐22 04/15/2015 390 <8.2 ‐‐ 390 ‐‐ 100 71 <0.05 38 1 3.1 120 ‐‐ ‐‐ 0.18 <0.20 Jo 630 1030 15

MW‐22 07/22/2015 380 <8.2 ‐‐ 380 ‐‐ 100 66 <0.05 33 0.81 2.8 120 ‐‐ ‐‐ <0.10 Jo <0.20 590 1080 15

MW‐22 10/15/2015 360 <4.1 ‐‐ 360 ‐‐ 96 56 <0.05 31 0.75 2.6 99 ‐‐ ‐‐ <0.10 Jo <0.20 600 923 15

MW‐22 01/20/2016 380 <4.1 ‐‐ 380 ‐‐ 94 61 <0.05 Jo 33 0.88 2.9 94 ‐‐ ‐‐ <0.10 <0.20 660 983 15

MW‐22 04/14/2016 420 <8.2 ‐‐ 420 ‐‐ 95 72 <0.05 37 1 3.1 100 ‐‐ ‐‐ 0.38 <0.20 Jo 660 1070 13

MW‐22 07/18/2016 440 <8.2 ‐‐ 440 ‐‐ 100 73 <0.05 38 0.96 3.1 130 ‐‐ ‐‐ <0.10 <0.20 Jo 700 1130 13

MW‐22 10/12/2016 470 <8.2 ‐‐ 470 ‐‐ 100 92 <0.05 43 1 3.3 130 ‐‐ ‐‐ <0.10 Jo <0.20 680 1160 12

MW‐23 03/13/2008 <3.0 220 52 380 ‐‐ 250 2.7 <0.050 0.83 ‐‐ 150 260 ‐‐ ‐‐ <2.0 <1.0 960 2200 22

MW‐23 08/04/2008 <10 210 230 440 ‐‐ 150 5.0 <0.050 0.3 <0.010 140 250 ‐‐ ‐‐ ‐‐ 0.55 970 2310 7.5

MW‐23 09/08/2008 150 <2.5 <2.5 150 ‐‐ 280 30 <0.050 13 0.2 8.9 190 ‐‐ ‐‐ ‐‐ <0.20 Jo 680 1190 1.6

MW‐23 10/09/2008 150 <2.5 <2.5 150 ‐‐ 280 27 <0.050 Jo 12 0.19 7.7 170 ‐‐ ‐‐ ‐‐ <0.20 Jo 680 1190 1.9

MW‐23 11/04/2008 150 <2.5 <2.5 150 ‐‐ 280 31 <0.050 Jo 14 0.23 7.2 180 ‐‐ ‐‐ ‐‐ <0.20 Jo 620 1160 1.3

MW‐23 12/03/2008 160 <5.0 <5.0 160 ‐‐ 290 30 <0.050 13 0.2 7.2 180 ‐‐ ‐‐ ‐‐ <0.20 670 1160 2.1

MW‐23 01/13/2009 150 <8.2 <8.2 150 ‐‐ 280 31 <0.050 Jo 14 0.23 6.0 180 ‐‐ ‐‐ ‐‐ <0.20 640 1140 2.0

MW‐23 02/04/2009 140 <8.2 <8.2 140 ‐‐ 280 32 <0.050 14 0.21 5.3 190 ‐‐ ‐‐ ‐‐ <0.20 620 1120 1.8

MW‐23 03/04/2009 150 <8.2 <8.2 150 ‐‐ 290 31 <0.050 Jo 14 0.19 4.8 170 ‐‐ ‐‐ ‐‐ <0.20 640 1150 1.9

MW‐23 04/14/2009 150 <8.2 <8.2 150 ‐‐ 270 33 <0.050 15 0.23 6.0 190 ‐‐ ‐‐ ‐‐ <0.20 640 1100 1.4

MW‐23 05/04/2009 140 <8.2 <8.2 140 ‐‐ 270 31 <0.050 14 0.19 4.7 180 ‐‐ ‐‐ ‐‐ <0.20 680 1130 <1.0 Jo

MW‐23 06/09/2009 150 <8.2 <8.2 150 ‐‐ 300 32 <0.05 14 0.2 3.9 170 ‐‐ ‐‐ ‐‐ <0.2 650 1090 1.4

MW‐23 07/14/2009 150 <8.2 <8.2 150 ‐‐ 290 33 <0.050 Jo 15 0.21 4.4 180 ‐‐ ‐‐ ‐‐ <0.20 680 1130 <1.0 Jo

MW‐23 08/04/2009 150 <8.2 <8.2 150 ‐‐ 290 33 <0.05 15 0.2 3.6 170 ‐‐ ‐‐ ‐‐ <0.2 640 1130 <1 Jo

MW‐23 09/08/2009 150 <8.2 <8.2 150 ‐‐ 290 32 <0.050 15 0.19 4.0 170 ‐‐ ‐‐ ‐‐ <0.20 630 1130 <1.0 Jo

MW‐23 10/07/2009 150 <8.2 <8.2 150 ‐‐ 290 33 <0.050 15 0.22 3.5 170 ‐‐ ‐‐ ‐‐ <0.20 660 1110 <1.0 Jo

MW‐23 11/10/2009 140 <8.2 <8.2 140 ‐‐ 280 32 <0.050 Jo 15 0.21 4.2 170 ‐‐ ‐‐ ‐‐ <0.20 640 1140 <1.0 Jo

MW‐23 12/08/2009 140 <8.2 <8.2 140 ‐‐ 290 31 <0.050 14 0.21 3.8 170 ‐‐ ‐‐ ‐‐ <0.20 660 1100 <1.0 Jo

MW‐23 01/05/2010 140 <4.1 <4.1 140 ‐‐ 280 31 <0.050 14 0.2 4.0 170 ‐‐ ‐‐ ‐‐ <0.20 660 1140 <1.0 Jo

MW‐23 02/10/2010 150 <8.2 <8.2 18 ‐‐ 280 32 <0.050 Jo 15 0.2 4.0 170 ‐‐ ‐‐ ‐‐ <0.20 700 1160 <1.0 Jo

MW‐23 03/08/2010 140 <8.2 <8.2 140 ‐‐ 280 32 <0.050 Jo 15 0.22 4.0 170 ‐‐ ‐‐ ‐‐ <0.20 660 1130 <1.0 Jo

MW‐23 04/15/2010 140 <8.2 ‐‐ 140 ‐‐ 300 33 0.22 15 0.2 3.9 180 ‐‐ ‐‐ ‐‐ <0.20 680 1130 <1.0

MW‐23 07/08/2010 140 <8.2 ‐‐ 140 ‐‐ 290 30 <0.05 Jo 14 0.19 3.6 170 ‐‐ ‐‐ ‐‐ <1.0 640 1170 <1.0 Jo

MW‐23 10/28/2010 140 <8.2 ‐‐ 140 ‐‐ 300 34 <0.05 Jo 16 0.23 3.8 190 ‐‐ ‐‐ ‐‐ <0.20 710 1150 <1.0 Jo

MW‐23 01/19/2011 140 <8.2 ‐‐ 140 ‐‐ 280 30 <0.05 14 0.19 3.6 160 ‐‐ ‐‐ ‐‐ <0.20 740 1130 <1.0 Jo

Page 82 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐23 04/04/2011 140 <8.2 ‐‐ 140 ‐‐ 270 33 <0.05 Jo 16 0.21 4.0 180 ‐‐ ‐‐ ‐‐ <0.40 640 1150 <1.0 Jo

MW‐23 07/07/2011 140 <8.2 ‐‐ 140 ‐‐ 280 32 <0.05 15 0.24 3.4 180 ‐‐ ‐‐ <0.10 <0.20 620 1140 <1.0 Jo

MW‐23 10/04/2011 160 <8.2 ‐‐ 160 ‐‐ 290 33 <0.05 15 0.21 3.4 170 ‐‐ ‐‐ <0.10 <0.20 660 1160 <1.0 Jo

MW‐23 01/18/2012 140 <8.2 ‐‐ 140 ‐‐ 280 33 <0.05 Jo 15 0.21 3.5 190 ‐‐ ‐‐ <0.10 <0.20 680 1180 <1.0 Jo

MW‐23 04/04/2012 140 <8.2 ‐‐ 140 ‐‐ 280 32 <0.05 Jo 14 0.2 3.2 160 ‐‐ ‐‐ <0.10 <0.20 680 1110 <1.0 Jo

MW‐23 07/23/2012 140 <8.2 ‐‐ 140 ‐‐ 280 31 <0.05 Jo 16 0.2 3.1 170 ‐‐ ‐‐ 1.3 <0.20 620 1160 2.8

MW‐23 10/15/2012 140 <8.2 ‐‐ 140 ‐‐ 290 35 <0.05 Jo 16 0.22 3.2 180 ‐‐ ‐‐ <0.10 <0.20 670 1190 <1.0 Jo

MW‐23 01/22/2013 140 <8.2 ‐‐ 140 ‐‐ 290 32 <0.05 15 0.2 3.3 180 ‐‐ ‐‐ <0.10 <0.20 640 1150 <1.0 Jo

MW‐23 04/18/2013 140 <8.2 ‐‐ 140 ‐‐ 290 33 <0.05 Jo 15 0.2 3.2 180 ‐‐ ‐‐ <0.10 <0.20 640 1090 <1.0 Jo

MW‐23 07/17/2013 140 <8.2 ‐‐ 140 ‐‐ 290 33 <0.05 16 0.2 3.3 170 ‐‐ ‐‐ <0.10 <0.20 680 1140 <1.0 Jo

MW‐23 10/21/2013 130 <8.2 ‐‐ 130 ‐‐ 310 31 <0.05 16 0.14 3.8 180 ‐‐ ‐‐ <0.10 <0.20 700 1250 <1.0 Jo

MW‐23 01/22/2014 140 <8.2 ‐‐ 140 ‐‐ 280 33 0.077 16 0.2 3.4 180 ‐‐ ‐‐ 0.42 <0.20 650 1090 <2.0 Jo

MW‐23 04/22/2014 130 <8.2 ‐‐ 130 ‐‐ 290 33 <0.05 16 0.12 4.3 190 ‐‐ ‐‐ <0.10 <0.20 Jo 680 1250 <1.0 Jo

MW‐23 07/21/2014 140 <8.2 ‐‐ 140 ‐‐ 280 34 <0.05 15 0.21 3.2 190 ‐‐ ‐‐ <0.20 <0.20 660 1210 <2.0 Jo

MW‐23 10/20/2014 140 <8.2 ‐‐ 140 ‐‐ 300 36 <0.05 17 0.19 3.5 190 ‐‐ ‐‐ <0.20 <0.20 570 1200 <2.0 Jo

MW‐23 01/21/2015 160 <8.2 ‐‐ 160 ‐‐ 270 29 <0.05 14 0.17 2.7 160 ‐‐ ‐‐ <0.10 <0.20 Jo 700 1150 <1.0 Jo

MW‐23 04/15/2015 150 <8.2 ‐‐ 150 ‐‐ 270 32 <0.05 16 0.21 3.1 180 ‐‐ ‐‐ 1.2 <0.20 Jo 700 1120 <2.0 Jo

MW‐23 07/22/2015 140 <8.2 ‐‐ 140 ‐‐ 310 37 <0.05 18 0.18 3.4 200 ‐‐ ‐‐ <0.20 <0.20 Jo 720 1300 <2.0 Jo

MW‐23 10/15/2015 150 <8.2 ‐‐ 150 ‐‐ 290 34 <0.05 Jo 15 0.19 2.9 180 ‐‐ ‐‐ <0.20 <0.20 840 1150 <2.0 Jo

MW‐23 01/20/2016 140 <8.2 ‐‐ 140 ‐‐ 300 34 <0.05 16 0.16 3.3 180 ‐‐ ‐‐ <0.20 <0.20 830 1240 <2.0 Jo

MW‐23 04/14/2016 140 <8.2 ‐‐ 140 ‐‐ 280 32 <0.05 15 0.2 2.9 170 ‐‐ ‐‐ <0.20 <0.20 Jo 710 1190 <2.0

MW‐23 07/18/2016 150 <8.2 ‐‐ 150 ‐‐ 280 34 <0.05 15 0.21 2.8 180 ‐‐ ‐‐ 0.35 <0.20 720 1200 <2.0 Jo

MW‐23 10/12/2016 150 <8.2 ‐‐ 150 ‐‐ 290 38 <0.05 17 0.2 3.4 200 ‐‐ ‐‐ <0.20 <0.20 720 1200 <2.0 Jo

MW‐24 01/06/2010 360 ‐‐ ‐‐ 360 ‐‐ 88 210 <0.050 70 0.37 4.8 80 ‐‐ 480 110 1.3 1500 1670 83

MW‐24 04/15/2010 370 <8.2 <8.2 370 ‐‐ 120 230 <0.050 73 0.4 5.1 80 ‐‐ ‐‐ 120 J‐ 1.3 1300 1840 93

MW‐24 08/12/2010 360 <8.2 <8.2 360 ‐‐ 87 210 <0.050 69 0.35 5.1 73 0.14 J‐ ‐‐ 100 1.3 1400 1760 74

MW‐24 11/08/2010 360 <8.2 ‐‐ 360 ‐‐ 110 210 <0.050 67 0.33 4.9 77 ‐‐ ‐‐ 98 0.99 1400 1820 83

MW‐24 05/18/2011 380 ‐‐ ‐‐ 380 <1.0 99.5 197 <0.20 63.2 0.298 <10 73.3 0.12 ‐‐ 85.4 <0.20 1110 1800 78.9

MW‐24 07/08/2011 384 ‐‐ ‐‐ 384 <1.0 87.8 189 <0.20 61.5 0.307 <10 74.3 0.11 ‐‐ 76.3 <0.20 1230 1750 <73.7 U

MW‐24 10/05/2011 372 <5.0 ‐‐ 372 <2.0 94.0 200 <0.20 63.9 0.31 <10 74.4 0.11 ‐‐ 94.3 <0.20 1220 1690 77.2

MW‐24 01/05/2012 351 <5.0 ‐‐ 351 0.28 88 203 <0.20 65.5 0.313 <10 70.5 0.11 410 J 92 J <0.20 1120 1700 <69 U

MW‐24 04/04/2012 370 <5.0 ‐‐ 370 <2.0 95.2 216 <0.20 65.0 0.332 <10 87.2 0.12 ‐‐ 88.4 <0.26 1160 1690 79.5

MW‐24 07/24/2012 350 <5.0 ‐‐ 350 <1.0 92.1 189 <0.20 61.7 0.299 <10 78.8 0.25 ‐‐ 97.7 <0.20 1260 1570 89.2

MW‐24 10/16/2012 340 <5.0 ‐‐ 340 <4.0 86.9 201 J <0.20 62.7 J 0.309 J <10 82.4 J 0.12 ‐‐ 84.8 <0.20 1230 1780 70.3

MW‐24 01/23/2013 362 <5.0 ‐‐ 362 <0.50 92.9 198 <0.20 62.3 0.316 <10 74.0 0.17 ‐‐ 106 <0.20 1210 1950 78.6

Page 83 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐24 04/16/2013 374 <5.0 ‐‐ 374 <0.50 92.5 187 <0.20 58.9 0.309 <10 77.2 0.13 ‐‐ 98.8 <0.20 1270 1660 80.5

MW‐24 07/16/2013 348 <5.0 ‐‐ 348 <0.50 99.6 189 <0.20 60.6 0.302 <10 75.7 0.12 ‐‐ 93.3 <0.20 1130 1680 78.2

MW‐24 10/17/2013 368 <5.0 ‐‐ 368 ‐‐ 86.8 197 <0.20 62.5 0.354 <10 85.5 ‐‐ ‐‐ 81.5 <1.1 U 1160 1640 72.5

MW‐24 01/22/2014 334 <5.0 ‐‐ 334 ‐‐ 84.6 176 <0.20 55.5 0.277 <10 75.3 ‐‐ ‐‐ 81.0 <2.2 U 1200 1370 74.6

MW‐24 04/23/2014 180 <5.0 ‐‐ 180 ‐‐ 80.1 181 <0.20 58.6 0.308 <10 76.8 ‐‐ ‐‐ 70.5 <0.20 1100 1590 68.9

MW‐25 01/06/2010 140 ‐‐ ‐‐ 140 ‐‐ 39 37 <0.050 15 0.054 2.9 57 ‐‐ ‐‐ 13 0.2 380 550 45

MW‐25 04/15/2010 130 <4.1 <4.1 130 ‐‐ 32 35 <0.050 14 0.054 2.5 54 ‐‐ ‐‐ 9.5 <0.20 Jo 350 493 39

MW‐25 08/12/2010 130 <4.1 <4.1 130 ‐‐ 32 32 <0.050 12 0.062 2.5 52 0.084 ‐‐ 6.4 0.21 310 483 39

MW‐25 10/28/2010 130 <4.1 ‐‐ 130 ‐‐ 33 33 <0.050 13 0.066 2.4 53 ‐‐ ‐‐ 6.7 <0.20 350 478 39

MW‐25 05/18/2011 126 ‐‐ ‐‐ 126 <0.20 35.3 29.3 <0.20 11.5 0.0714 <10 50.4 0.089 ‐‐ 2.9 <0.20 290 495 39.3

MW‐25 07/08/2011 <128 U ‐‐ ‐‐ <128 U <0.20 32.8 <27.4 U <0.20 10.7 0.0831 <10 <51.6 U 0.076 ‐‐ 1.9 <0.20 <279 U <464 U <34.1 U

MW‐25 10/05/2011 130 <5.0 ‐‐ 130 <0.20 35.7 30.9 <0.20 12.0 0.105 <10 51.6 0.069 ‐‐ <4.5 U <0.20 293 454 34.9

MW‐25 01/05/2012 119 <5.0 ‐‐ 119 0.19 38 32.8 <0.20 13.0 0.122 <10 50.3 0.074 27 J 6.1 J <0.20 290 480 <34 U

MW‐25 04/04/2012 124 <5.0 ‐‐ 124 <0.20 37.7 37.3 <0.20 13.8 0.145 <10 59.7 0.091 ‐‐ 7.0 0.31 313 498 35.5

MW‐25 07/24/2012 126 <5.0 ‐‐ 126 <0.40 45.1 40.3 <0.20 14.0 0.136 <10 57.9 0.076 ‐‐ 8.5 <0.20 315 460 39.9

MW‐25 10/16/2012 130 <5.0 ‐‐ 130 <0.50 44.9 41.2 J <0.20 15.6 J 0.144 J <10 58.0 J 0.071 ‐‐ 10.4 <0.20 342 563 37.8

MW‐25 01/23/2013 144 <5.0 ‐‐ 144 <0.50 45.7 36.5 <0.20 13.9 0.127 <10 51.1 0.098 J ‐‐ 9.4 <0.20 313 569 41.0

MW‐25 04/16/2013 136 <5.0 ‐‐ 136 <0.50 45.9 34.8 <0.20 13.3 0.123 <10 53.6 0.074 ‐‐ 9.0 <0.24 U 336 512 38.5

MW‐25 07/16/2013 134 <5.0 ‐‐ 134 <0.50 41.1 37.1 <0.20 14.3 0.116 <10 52.7 0.071 ‐‐ 9.6 <0.20 340 539 40.6

MW‐25 10/17/2013 142 <5.0 ‐‐ 142 ‐‐ 50.5 44.3 <0.20 17.0 0.138 <10 55.6 ‐‐ ‐‐ 10.5 <0.56 U 375 589 38.3

MW‐25 01/22/2014 150 <5.0 ‐‐ 150 ‐‐ 54.9 42.0 <0.20 16.1 0.112 <10 53.9 ‐‐ ‐‐ 11.6 <0.65 U 387 492 40.7

MW‐25 04/23/2014 150 <5.0 ‐‐ 150 ‐‐ 48.7 48.0 <0.20 18.6 0.118 <10 56.5 ‐‐ ‐‐ 12.6 <0.43 U 401 642 40.2

MW‐25 10/20/2014 157 <5.0 ‐‐ 157 ‐‐ 48.6 44.2 <0.20 17.7 0.0954 <10 54.9 ‐‐ ‐‐ 12.7 <0.20 393 625 39.9

MW‐25 04/15/2015 153 <5.0 ‐‐ 153 ‐‐ 51.4 47.6 J <0.20 18.3 J 0.141 J <10 58.1 J ‐‐ ‐‐ 10.2 <0.20 393 622 39.9

MW‐25 10/15/2015 157 <5.0 ‐‐ 157 ‐‐ 111 49.9 <0.20 19.0 0.141 J <10 56.9 ‐‐ ‐‐ 11.7 <0.20 430 666 79.9

MW‐25 04/14/2016 154 <5.0 ‐‐ 154 ‐‐ 47.9 43.4 <0.20 16.6 0.120 J <10 51.5 J ‐‐ ‐‐ 10.6 <0.20 385 641 39.9

MW‐25 10/12/2016 139 <5.0 ‐‐ 141 ‐‐ 50 46.9 <0.3 17.9 0.0861 <10 J 57 ‐‐ ‐‐ 13 <0.53 R 396 557 41

MW‐26 01/06/2010 140 ‐‐ ‐‐ 140 ‐‐ 510 58 <0.050 25 0.47 4.1 280 ‐‐ ‐‐ 0.11 <0.20 1100 1760 59

MW‐26 04/15/2010 150 <8.2 <8.2 150 ‐‐ 380 38 0.1 16 0.5 3.5 250 ‐‐ ‐‐ <0.10 <0.20 940 1430 20

MW‐26 08/12/2010 150 <8.2 <8.2 150 ‐‐ 390 40 <0.050 17 0.49 3.4 230 0.38 ‐‐ <0.10 <0.20 830 1420 5.5

MW‐26 10/28/2010 160 <8.2 ‐‐ 160 ‐‐ 370 38 <0.050 16 0.46 2.9 220 ‐‐ ‐‐ <0.10 <0.20 850 1400 5.9

MW‐26 05/18/2011 148 ‐‐ ‐‐ 148 1.5 342 52.5 0.261 21.7 0.662 <10 230 0.46 ‐‐ <0.10 <0.20 832 1630 2.5

MW‐26 07/07/2011 <146 U ‐‐ ‐‐ <146 U 1.5 377 46.7 0.242 19.5 0.614 <10 210 0.39 ‐‐ <0.10 <0.20 901 1610 <2.3 U

MW‐26 10/05/2011 188 <5.0 ‐‐ 188 0.94 243 37.7 <0.20 14.9 0.499 <10 192 0.25 ‐‐ <0.42 U <0.20 652 1190 9.7

MW‐26 01/05/2012 173 <5.0 ‐‐ 173 1.1 300 41.7 <0.20 16.7 0.603 <10 183 0.33 <0.45 <0.1 <0.20 671 1280 <9.4 U

Page 84 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐26 04/04/2012 160 <5.0 ‐‐ 160 1.2 313 52.4 0.232 19.8 0.745 <10 235 0.43 ‐‐ <0.50 0.49 811 1490 5.0

MW‐26 07/24/2012 230 <5.0 ‐‐ 230 0.87 202 45.0 <0.20 16.0 0.474 <10 182 0.23 ‐‐ <0.20 <0.20 592 997 25.1

MW‐26 10/16/2012 194 <5.0 ‐‐ 194 1.3 271 48.1 J 0.225 19.1 J 0.493 J <10 196 J 0.32 ‐‐ <0.25 <0.20 702 1340 15.1

MW‐26 01/23/2013 172 <5.0 ‐‐ 172 1.8 409 51.6 0.276 20.7 0.586 <10 208 0.36 ‐‐ <0.25 0.26 904 1700 6.9

MW‐26 04/16/2013 162 <5.0 ‐‐ 162 1.5 357 45.9 0.274 18.6 0.535 <10 215 0.47 ‐‐ <0.25 <0.31 U 847 1450 6.5

MW‐26 07/16/2013 201 <5.0 ‐‐ 201 1.0 238 37.8 0.228 15.8 0.39 <10 176 0.24 ‐‐ <0.25 0.2 628 1950 15.6

MW‐26 10/17/2013 176 <5.0 ‐‐ 176 ‐‐ 331 50.6 0.299 21.1 0.479 <10 204 ‐‐ ‐‐ <0.25 <0.99 U 773 1390 9.6

MW‐26 01/22/2014 182 <5.0 ‐‐ 182 ‐‐ 333 45.9 0.257 19.1 0.434 <10 200 ‐‐ ‐‐ <0.25 <0.62 U 802 1190 8.5

MW‐26 04/23/2014 204 <5.0 ‐‐ 204 ‐‐ 240 40.1 0.259 17.1 0.391 <10 189 ‐‐ ‐‐ <0.25 <0.53 U 637 1260 13.3

MW‐27 01/06/2010 130 ‐‐ ‐‐ 130 ‐‐ 570 66 <0.050 24 0.37 5.2 260 ‐‐ ‐‐ <0.10 <0.20 1100 1810 2.6

MW‐27 04/15/2010 130 <8.2 <8.2 130 ‐‐ 590 70 0.13 25 0.41 5.5 280 ‐‐ ‐‐ <0.10 <0.20 1200 1810 2.7

MW‐27 08/12/2010 130 <8.2 <8.2 130 ‐‐ 570 69 <0.050 25 0.56 5.4 230 0.55 ‐‐ <0.10 <0.20 1300 J‐ 1870 3.6

MW‐27 10/28/2010 130 <8.2 ‐‐ 130 ‐‐ 550 67 <0.050 24 0.53 4.8 290 ‐‐ ‐‐ <0.10 <0.20 1300 1900 1.7

MW‐27 05/18/2011 134 ‐‐ ‐‐ 134 2.0 474 67.8 0.366 23.5 0.579 <10 248 0.6 ‐‐ <0.10 <0.20 1080 2010 1.0

MW‐27 07/07/2011 <138 U ‐‐ ‐‐ <138 U 2.0 510 65.9 0.367 23.1 0.611 <10 242 0.5 ‐‐ <0.10 <0.20 1180 1950 <0.82 U

MW‐27 10/05/2011 136 <5.0 ‐‐ 136 2.0 466 69.1 0.346 24.0 0.634 <10 260 0.54 ‐‐ <0.10 0.26 1110 1890 1.8

MW‐27 01/04/2012 131 <5.0 ‐‐ 131 2.1 540 68.5 0.381 24.0 0.644 <10 254 0.58 <0.45 UJ <0.1 UJ <0.20 1080 1900 <2.4 U

MW‐27 04/04/2012 136 <5.0 ‐‐ 136 <2.0 491 74.2 0.357 24.6 0.63 <10 276 0.56 ‐‐ <1.0 0.46 1110 1830 <5.0

MW‐27 07/24/2012 126 <5.0 ‐‐ 126 2.5 490 78.5 0.352 25.9 0.6 <10 298 0.66 ‐‐ <0.25 <0.20 1140 1810 3.8

MW‐27 10/16/2012 128 <5.0 ‐‐ 128 2.4 563 79.8 J 0.385 26.1 J 0.634 J <10 299 J 0.58 ‐‐ <0.25 <0.20 1260 2140 <1.3

MW‐27 01/23/2013 130 <5.0 ‐‐ 130 2.4 570 71.6 0.377 24.3 0.572 <10 267 0.57 ‐‐ <0.25 0.24 1200 2150 <1.3

MW‐27 04/16/2013 140 <5.0 ‐‐ 140 2.2 530 65.9 0.34 22.2 0.514 <10 267 0.57 ‐‐ <0.25 <0.38 U 1150 1840 <1.3

MW‐27 07/16/2013 132 <5.0 ‐‐ 132 2.2 536 71.9 0.305 24.3 0.452 <10 266 0.59 ‐‐ <0.25 0.32 1180 1940 <1.3

MW‐27 10/17/2013 136 <5.0 ‐‐ 136 ‐‐ 547 79.3 0.3 25.1 0.466 <10 272 ‐‐ ‐‐ <0.25 <0.7 U 1190 1990 <1.3

MW‐27 01/22/2014 130 <5.0 ‐‐ 130 ‐‐ 533 68.5 <0.20 20.1 0.342 <10 255 ‐‐ ‐‐ <0.25 <0.73 U 1180 1580 <1.3

MW‐27 04/23/2014 135 <5.0 ‐‐ 135 ‐‐ 527 75.0 <0.20 24.0 0.386 <10 281 ‐‐ ‐‐ <0.25 2.8 J+ 1190 1860 <1.3

MW‐28 01/07/2010 140 ‐‐ ‐‐ 140 ‐‐ 500 70 J‐ <0.050 UJ‐ 18 J‐ 0.21 J‐ 5.7 J‐ 260 J‐ ‐‐ ‐‐ 0.21 <0.20 1100 1700 8.1

MW‐28 04/15/2010 140 <8.2 <8.2 140 ‐‐ 510 70 <0.050 17 0.33 5.7 250 ‐‐ ‐‐ <0.10 <0.20 1100 1670 4.4

MW‐28 08/12/2010 140 <8.2 <8.2 140 ‐‐ 510 68 <0.050 17 0.41 6.3 240 0.51 ‐‐ <0.10 <0.20 1100 1700 2.4

MW‐28 11/08/2010 150 <8.2 ‐‐ 150 ‐‐ 500 68 <0.050 17 0.58 5.7 260 ‐‐ ‐‐ <0.10 <0.20 1100 1730 1.0

MW‐28 05/17/2011 134 ‐‐ ‐‐ 134 1.7 392 55.0 <0.20 16.1 0.799 15.2 222 0.53 ‐‐ <0.10 <0.20 924 1800 3.6

MW‐28 07/07/2011 <88.0 U ‐‐ ‐‐ <88.0 U 1.7 492 68.1 0.355 17.0 0.83 <10 218 0.43 ‐‐ <0.10 <0.20 1040 1780 <0.65 U

MW‐28 10/05/2011 143 <5.0 ‐‐ 143 1.9 412 70.3 0.367 17.4 0.908 <10 244 0.44 ‐‐ <0.20 U <0.20 1020 1670 1.1

MW‐28 01/04/2012 154 <5.0 ‐‐ 154 1.9 460 J 72.2 0.416 17.9 0.865 <10 230 0.49 <0.45 <0.1 <0.20 987 1700 <1.7 U

MW‐28 04/04/2012 142 <5.0 ‐‐ 142 <2.0 456 78.8 0.449 18.1 0.923 <10 258 0.57 ‐‐ <1.0 0.35 1020 1710 <5.0

Page 85 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐28 07/24/2012 124 <5.0 ‐‐ 124 2.1 433 76.8 0.3 18.6 0.943 <10 262 0.56 ‐‐ <0.25 <0.20 1080 1600 <1.3

MW‐28 10/15/2012 142 <5.0 ‐‐ 142 2.0 485 73.6 0.354 17.5 0.74 <10 251 0.46 ‐‐ <0.25 0.59 1080 1820 <1.3

MW‐28 01/23/2013 158 <5.0 ‐‐ 158 2.2 481 69.3 0.329 16.4 0.687 <10 237 0.48 ‐‐ <0.25 0.26 934 1890 <1.3

MW‐28 04/15/2013 144 <5.0 ‐‐ 144 2.0 452 67.9 0.352 16.0 0.582 <10 249 0.5 ‐‐ <0.25 <0.29 U 1040 1670 <1.3

MW‐28 07/16/2013 139 <5.0 ‐‐ 139 2.1 441 70.5 0.341 17.1 0.578 <10 239 0.49 ‐‐ <0.25 0.26 1010 1710 <1.3

MW‐28 10/17/2013 144 <5.0 ‐‐ 144 ‐‐ 462 76.3 0.356 18.1 0.642 <10 252 ‐‐ ‐‐ <0.25 <0.38 U 1060 1750 <1.3

MW‐28 01/22/2014 158 <5.0 ‐‐ 158 ‐‐ 469 70.1 0.319 16.4 0.532 <10 241 ‐‐ ‐‐ <0.25 <0.57 U 1110 1440 <1.3

MW‐28 04/23/2014 143 <5.0 ‐‐ 143 ‐‐ 464 77.3 0.354 18.6 0.576 <10 261 ‐‐ ‐‐ <0.25 <1.6 U 1090 1780 <1.3

MW‐29 01/07/2010 150 ‐‐ ‐‐ 150 ‐‐ 40 39 J‐ <0.050 UJ‐ 14 J‐ 0.083 J‐ 3.4 J‐ 68 J‐ ‐‐ ‐‐ 14 <0.20 410 598 60

MW‐29 04/15/2010 120 <4.1 <4.1 120 ‐‐ 26 33 <0.050 10 0.049 2.7 48 ‐‐ ‐‐ 6.1 <0.20 Jo 320 474 48

MW‐29 08/12/2010 130 <4.1 <4.1 130 ‐‐ 25 38 <0.050 12 0.04 2.1 57 0.06 ‐‐ 11 0.26 340 529 50

MW‐29 11/08/2010 110 <4.1 ‐‐ 110 ‐‐ 26 32 <0.050 10 0.034 2.7 49 ‐‐ ‐‐ 4.6 <0.20 290 447 45

MW‐29 05/17/2011 130 ‐‐ ‐‐ 130 0.26 27.8 39.2 <0.20 11.9 0.0311 <10 49.6 0.063 ‐‐ 8.6 <0.20 302 552 52.1

MW‐29 07/07/2011 <143 U ‐‐ ‐‐ <143 U 0.35 24.4 41.4 <0.20 13.0 0.0354 <10 62.3 0.056 ‐‐ 12.3 <0.20 <370 U 597 52.5

MW‐29 10/05/2011 121 <5.0 ‐‐ 121 0.25 26.9 37.9 <0.20 11.7 0.0343 <10 48.9 0.056 ‐‐ 6.2 <0.20 279 467 46.8

MW‐29 01/04/2012 109 <5.0 ‐‐ 109 0.23 33 33.9 <0.20 9.91 0.0337 <10 39.1 0.058 0.85 J 0.19 J 0.21 230 428 <41 U

MW‐29 04/04/2012 118 <5.0 ‐‐ 118 <0.20 28.8 37.8 <0.20 10.4 0.0482 <10 48.6 0.064 ‐‐ 0.52 0.39 256 426 43.8

MW‐29 07/24/2012 134 <5.0 ‐‐ 134 0.5 28.6 51.9 <0.20 16.1 0.0525 <10 68.3 0.071 ‐‐ 20.3 <0.20 407 578 65.3

MW‐29 10/16/2012 158 <5.0 ‐‐ 158 <0.50 25.9 48.5 J <0.20 15.0 J 0.0496 J <10 62.9 J 0.061 ‐‐ 19.9 <0.20 420 652 60.1

MW‐29 01/23/2013 126 <5.0 ‐‐ 126 <0.50 40.6 34.7 <0.20 10.3 0.0312 <10 40.3 0.058 ‐‐ <0.25 0.27 254 464 51.7

MW‐29 04/16/2013 142 <5.0 ‐‐ 142 <0.50 36.9 39.8 <0.20 11.7 0.0423 <10 49.3 0.065 ‐‐ 5.4 <0.27 U 306 481 54.1

MW‐29 07/16/2013 161 <5.0 ‐‐ 161 <0.50 23.8 46.9 <0.20 14.8 0.0502 <10 61.4 0.067 ‐‐ 17.9 <0.20 412 615 54.7

MW‐29 10/17/2013 160 <5.0 ‐‐ 160 ‐‐ 23.4 50.7 <0.20 15.9 0.0572 <10 65.8 ‐‐ ‐‐ 18.7 <0.46 U 414 630 57.1

MW‐29 01/22/2014 134 <5.0 ‐‐ 134 ‐‐ 24.9 45.0 <0.20 13.4 0.0483 <10 62.1 ‐‐ ‐‐ 18.4 <0.33 U 408 511 58.4

MW‐29 04/23/2014 160 <5.0 ‐‐ 160 ‐‐ 24.8 50.3 <0.20 15.9 0.0604 <10 64.5 ‐‐ ‐‐ 18.6 <0.28 U 420 657 51.3

MW‐38 12/14/2010 190 <3.0 <3.0 190 ‐‐ 530 68 3.7 34 1.2 3.2 260 ‐‐ ‐‐ <1.1 <1.0 1100 2000 <10

MW‐38 01/26/2011 190 <3.0 <3.0 190 2.1 520 71 3.8 36 1.3 3.6 270 0.57 ‐‐ <1.1 <1.0 1100 2000 <10

MW‐38 05/17/2011 196 ‐‐ ‐‐ 196 2.7 660 129 0.389 34.1 0.551 <10 290 0.87 ‐‐ <0.10 <0.20 1470 2700 <0.50

MW‐38 07/07/2011 <212 U ‐‐ ‐‐ <212 U 2.1 564 96.3 0.524 27.8 0.524 <10 272 0.57 ‐‐ <0.10 <0.20 1210 2040 <0.50

MW‐38 10/05/2011 208 <5.0 ‐‐ 208 1.9 442 77.4 2.35 33.8 1.01 <10 262 0.49 ‐‐ <0.10 <0.20 1140 1980 <0.50

MW‐38 01/04/2012 204 <5.0 ‐‐ 204 2.1 530 J 80.4 3.54 37.4 1.19 <10 258 0.59 <0.45 <0.1 <0.20 1150 1970 <1.2 U

MW‐38 04/04/2012 202 <5.0 ‐‐ 202 <2.0 502 73.2 3.41 34.4 1.15 <10 243 0.58 ‐‐ <1.0 0.51 1140 1970 <5.0

MW‐38 07/23/2012 208 <5.0 ‐‐ 208 2.3 581 88.3 1.03 37.9 1.12 <10 293 0.65 ‐‐ <0.10 <0.43 U <1200 U 2070 <0.50

MW‐38 10/15/2012 218 <5.0 ‐‐ 218 2.1 513 73.3 2.83 35.8 1.22 <10 269 0.59 ‐‐ <0.25 4.9 1140 2030 <1.3

MW‐38 01/22/2013 210 <5.0 ‐‐ 210 2.1 539 75.7 4.04 38.4 1.31 <10 254 0.54 ‐‐ <0.25 <0.20 1040 1660 <1.3

Page 86 of 87

ATTACHMENT 5




Hilmar, California

Sample


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)


as CaC

O3 (mg/L)

Alkalinity, Total

as CaC

O3 (mg/L)

Bromide

(mg/L)

Chloride

(mg/L)

Dissolved Calcium

(mg/L)

Dissolved Iron

(mg/L)

Dissolved M

agnesium

(mg/L)

Dissolved M

anganese

(mg/L)

Dissolved Potassium

(mg/L)

Dissolved Sodium

(mg/L)

Iodide

(mg/L)

Nitrate (as NO3)

(mg/L)

Nitrate‐Nitrogen

(mg/L)


l

(mg/L)


(mg/L)


(µmhos/cm

)

Sulfate

(mg/L)

MW‐38 04/15/2013 216 <5.0 ‐‐ 216 2.0 505 78.4 4.13 38.6 1.43 <10 288 0.53 ‐‐ <0.25 <0.36 U 1070 1970 <1.3

MW‐38 07/16/2013 209 <5.0 ‐‐ 209 2.1 513 72.8 1.69 34.9 1.08 <10 269 0.59 ‐‐ <0.25 0.25 1050 1900 <1.3

MW‐38 10/17/2013 204 <5.0 ‐‐ 204 ‐‐ 474 71.9 3.67 36.2 1.29 <10 262 ‐‐ ‐‐ <0.25 <0.43 U 1080 1920 <1.3

MW‐38 01/21/2014 224 <5.0 ‐‐ 224 ‐‐ 482 71.0 4.29 36.1 1.25 <10 260 ‐‐ ‐‐ <0.25 <1.5 U 1100 1850 <1.3

MW‐38 04/23/2014 221 <5.0 ‐‐ 221 ‐‐ 503 74.7 4.24 38.7 1.33 <10 277 ‐‐ ‐‐ <0.25 <1.5 U 1110 1940 <1.3

MW‐40 12/14/2010 190 <3.0 <3.0 190 ‐‐ 370 56 1.1 18 0.76 3.8 210 ‐‐ ‐‐ <1.1 <1.0 850 1600 <10

MW‐40 01/26/2011 190 <3.0 <3.0 190 1.6 360 59 1.1 19 0.8 3.9 220 0.4 ‐‐ <1.1 <1.0 850 1600 <10

MW‐40 05/17/2011 204 ‐‐ ‐‐ 204 1.7 402 73.0 0.375 23.1 0.611 <10 227 0.54 ‐‐ <0.10 <0.20 979 1890 1.1

MW‐40 07/07/2011 <206 U ‐‐ ‐‐ <206 U 1.8 477 79.0 0.366 25.0 0.68 <10 236 0.48 ‐‐ <0.10 <0.20 1100 1980 <1.3 U

MW‐40 10/05/2011 204 <5.0 ‐‐ 204 1.6 366 71.6 0.347 21.9 0.575 <10 244 0.43 ‐‐ <0.10 <0.20 1010 1740 1.4

MW‐40 01/04/2012 196 <5.0 ‐‐ 196 1.5 390 J 67.5 0.492 20.9 0.639 <10 214 0.44 <0.45 <0.1 <0.20 876 1560 <1 U

MW‐40 04/04/2012 210 <5.0 ‐‐ 210 <2.0 435 90.0 0.594 25.4 0.71 <10 278 0.56 ‐‐ <1.0 0.39 1070 1890 <5.0

MW‐40 07/23/2012 206 <5.0 ‐‐ 206 2.4 623 99.7 0.539 29.5 0.703 <10 294 0.6 ‐‐ <0.10 <0.21 U <1220 U 2160 <0.50

MW‐40 10/15/2012 224 <5.0 ‐‐ 224 2.3 557 95.9 0.514 28.1 0.664 <10 290 0.55 ‐‐ <0.25 0.94 1270 2190 <1.3

MW‐40 01/22/2013 220 <5.0 ‐‐ 220 1.6 403 70.6 0.426 20.9 0.545 <10 222 0.42 ‐‐ <0.25 <0.20 804 1320 <1.3

MW‐40 04/15/2013 208 <5.0 ‐‐ 208 2.0 491 86.9 0.499 24.9 0.65 <10 279 0.5 ‐‐ <0.25 <0.37 U 1070 1960 <1.3

MW‐40 07/16/2013 194 <5.0 ‐‐ 194 2.1 520 90.4 0.476 26.7 0.636 <10 280 0.63 ‐‐ <0.25 0.21 1340 2050 <1.3

MW‐40 10/17/2013 204 <5.0 ‐‐ 204 ‐‐ 464 84.8 0.456 24.8 0.591 <10 265 ‐‐ ‐‐ <0.25 <0.5 U 1060 1900 <1.3

MW‐40 01/21/2014 212 <5.0 ‐‐ 212 ‐‐ 520 93.9 <0.543 U 28.1 0.66 <10 281 ‐‐ ‐‐ <0.25 <2.3 U 1250 1970 <1.3

MW‐40 04/23/2014 231 <5.0 ‐‐ 231 ‐‐ 529 94.7 0.549 28.4 0.674 <10 294 ‐‐ ‐‐ <0.25 <1.5 U 1190 1970 <1.3

Notes:

Monitoring wells MW‐2, MW‐10, MW‐14, MW‐20, MW‐24, MW‐26, MW‐27, MW‐28, MW‐29, MW‐32, MW‐38, and MW‐40 were destroyed during 2014.



NO₃ = nitrate

μg/L = microgram per liter


< = less than



See Attachment 10 for data qualifier definitions.

Page 87 of 87

ATTACHMENT 6

CONCENTRATIONS OF COCS OVER TIME

ATTACHMENT 6

CHLORIDE ‐ UPPER AQUIFER SHALLOW ZONE (1 OF 2)



Hilmar, California

Notes:

Laboratory reported non‐detect results plotted as half of the reporting limit and shown with an open symbol.

RAO = Remedial Action Objective

0

200

400

600

800

1000

Chloride

(milligram

per liter [m

g/L])

MW‐03 MW‐04 MW‐05 MW‐06

MW‐07 MW‐08 MW‐09 MW‐13

MW‐15 RAO Shallow Zone (239 mg/L)

ATTACHMENT 6

CHLORIDE ‐ UPPER AQUIFER SHALLOW ZONE (2 OF 2)



Hilmar, California

Notes:

Laboratory reported non‐detect results plotted as half of the reporting limit and show with an open symbol.


0

200

400

600

800

1000

Chloride

(milligram

per liter [m

g/L])

MW‐01 MW‐11 MW‐12 MW‐16 MW‐17 MW‐21 RAO Shallow Zone (239 mg/L)

ATTACHMENT 6

CHLORIDE ‐ LOWER AQUIFER ZONE



Hilmar, California

0

200

400

600

800

1000

Chloride

(milligram

per liter)

MW‐23

ATTACHMENT 6

DISSOLVED IRON ‐ UPPER AQUIFER SHALLOW ZONE (1 OF 2)



Hilmar, California

Notes:

Redevelopments and sanitization occured in wells MW‐03, MW‐05, and MW‐07.


0

2

4

6

8

10

12

Iron

(milligram

per liter [m

g/L])

MW‐03 MW‐05 MW‐06 MW‐07 RAO Shallow Zone (0.3 mg/L)

Red

evelop

Red

evelop

Sanitize

ATTACHMENT 6

DISSOLVED IRON ‐ UPPER AQUIFER SHALLOW ZONE (2 OF 2)



Hilmar, California

Notes:



0

2

4

6

8

10

12

Iron

(milligram

per liter [m

g/L])

MW‐01 MW‐04 MW‐08 MW‐09

MW‐11 MW‐12 MW‐13 MW‐15

MW‐16 MW‐17 MW‐21 RAO Shallow Zone (0.3 mg/L)

ATTACHMENT 6

DISSOLVED IRON ‐ UPPER AQUIFER SUPPLY ZONE



Hilmar, California

Notes:



0

2

4

6

8

10

12

Iron

(milligram

per liter [m

g/L])

MW‐18 MW‐19 MW‐22 MW‐25 RAO Supply Zone (0.3 mg/L)

ATTACHMENT 6

DISSOLVED MANGANESE ‐ UPPER AQUIFER SHALLOW ZONE (1 OF 2)



Hilmar, California

Note:


0

1

2

3

4

5

6

7

8

9

10

Man

ganese

(milligram

per liter [m

g/L])

MW‐03 MW‐04 MW‐06 MW‐07 MW‐09 MW‐17 RAO Shallow Zone (0.34 mg/L)

ATTACHMENT 6

DISSOLVED MANGANESE ‐ UPPER AQUIFER SHALLOW ZONE (2 OF 2)



Hilmar, California

Notes:



0

1

2

3

4

5

6

7

8

9

10

Man

ganese

(milligram

per liter [m

g/L])

MW‐01 MW‐05 MW‐08 MW‐11

MW‐12 MW‐13 MW‐15 MW‐16

MW‐21 RAO Shallow Zone (0.34 mg/L)

ATTACHMENT 6

DISSOLVED MANGANESE ‐ UPPER AQUIFER SUPPLY ZONE



Hilmar, California

Notes:

Laboratory reported non‐detect results plotted as half of the reporting limit and show with an open symbol.


0

0.2

0.4

0.6

0.8

1

1.2

1.4

Man

ganese

(milligram

per liter [m

g/L])

MW‐18 MW‐19 MW‐22 MW‐25 RAO Supply Zone (0.05 mg/L)

ATTACHMENT 6

NITRATE AS NITROGEN ‐ UPPER AQUIFER SHALLOW ZONE (1 OF 2)



Hilmar, California

Note:


0

20

40

60

80

100

120

140

160

180

Nitrate as Nitrogen

(milligram

per liter [m

g/L])

MW‐01 MW‐11 MW‐13 MW‐15 MW‐16 MW‐17 MW‐21 RAO Shallow Zone (52 mg/L)

ATTACHMENT 6

NITRATE AS NITROGEN ‐ UPPER AQUIFER SHALLOW ZONE (2 OF 2)



Hilmar, California

Notes:



0

20

40

60

80

100

120

140

160

180

Nitrate as Nitrogen

(milligram

per liter [m

g/L])

MW‐03 MW‐04 MW‐05

MW‐06 MW‐07 MW‐08

MW‐09 MW‐12 RAO Shallow Zone (52 mg/L)

ATTACHMENT 6

NITRATE AS NITROGEN ‐ UPPER AQUIFER SUPPLY ZONE



Hilmar, California

Notes:



0

20

40

60

80

100

120

140

160

180

Nitrate as Nitrogen

(milligram

per liter [m

g/L])

MW‐18 MW‐19 MW‐22 MW‐25 RAO Supply Zone (34 mg/L)

ATTACHMENT 6

DISSOLVED SODIUM ‐ UPPER AQUIFER SHALLOW ZONE (1 OF 2)



Hilmar, California

Note:


0

100

200

300

400

500

600

700

800

900

1000

Sodium

(milligram

per liter [m

g/L])

MW‐01 MW‐03 MW‐05MW‐06 MW‐07 MW‐08MW‐09 MW‐13 MW‐15RAO Shallow Zone (346 mg/L)

ATTACHMENT 6

DISSOLVED SODIUM ‐ UPPER AQUIFER SHALLOW ZONE (2 OF 2)



Hilmar, California

Note:


0

100

200

300

400

500

600

700

800

900

1000

Sodium

(milligram

per liter [m

g/L])


ATTACHMENT 6

DISSOLVED SODIUM ‐ UPPER AQUIFER SUPPLY ZONE



Hilmar, California

Note:


0

100

200

300

400

500

600

700

800

900

1000

Sodium

(milligram

per liter [m

g/L])


ATTACHMENT 6

DISSOLVED SODIUM ‐ LOWER AQUIFER ZONE



Hilmar, California

0

200

400

600

800

1000

Sodium

(milligram

per liter)

MW‐23

ATTACHMENT 6

SULFATE ‐ UPPER AQUIFER SHALLOW ZONE (1 OF 2)



Hilmar, California

Notes:



0

50

100

150

200

250

300

350

400

Sulfate

(milligram

per liter [m

g/L])


ATTACHMENT 6

SULFATE ‐ UPPER AQUIFER SHALLOW ZONE (2 OF 2)



Hilmar, California

Notes:



0

50

100

150

200

250

300

350

400

Sulfate

(milligram

per liter [m

g/L])

MW‐01 MW‐04 MW‐08

MW‐11 MW‐15 MW‐16


ATTACHMENT 6

SULFATE ‐ UPPER AQUIFER SUPPLY ZONE



Hilmar, California

Note:


0

50

100

150

200

250

300

350

400

Sulfate

(milligram

per liter [m

g/L])


ATTACHMENT 6

TOTAL DISSOLVED SOLIDS ‐ UPPER AQUIFER SHALLOW ZONE (1 OF 2)



Hilmar, California

Note:


0

500

1000

1500

2000

2500

3000

3500

4000

Total D

issolved Solids

(milligram

per liter [m

g/L])

MW‐01 MW‐03 MW‐05MW‐06 MW‐07 MW‐08MW‐09 MW‐13 MW‐15

RAO Shallow Zone (912 mg/L)

ATTACHMENT 6

TOTAL DISSOLVED SOLIDS ‐ UPPER AQUIFER SHALLOW ZONE (2 OF 2)



Hilmar, California

Note:


0

500

1000

1500

2000

2500

3000

3500

4000

Total D

issolved Solids

(milligram

per liter [m

g/L])


ATTACHMENT 6

TOTAL DISSOLVED SOLIDS ‐ UPPER AQUIFER SUPPLY ZONE



Hilmar, California

Note:


0

500

1000

1500

2000

2500

3000

3500

4000

Total D

issolved Solids

(milligram

per liter [m

g/L])


ATTACHMENT 6

TOTAL DISSOLVED SOLIDS ‐ LOWER AQUIFER ZONE



Hilmar, California

0

500

1000

1500

2000

2500

3000

3500

4000

Total D

issolved Solids

(milligram

per liter)

MW‐23

ATTACHMENT 7

HISTORICAL FORMER PRIMARY LAND REUSE AREA APPLICATION TIMELINE

(JANUARY 2011‐DECEMBER 2015)

01.HCC.2012 DPG11/13/13 TJ

HILMAR CHEESE COMPANYHILMAR, CALIFORNIA FORMER PRIMARY LAND

REUSE AREA APPLICATION TIMELINE JANUARY 2011-DECEMBER 2012

ATTACHMENT 7a

TOTAL DISSOLVED


CHLORIDE AND SODIUM


REUSE WATER


HISTORY

Flow

for T

ID F

resh

wat

er, H

CC

Reu

se

Wat

er a

nd T

otal

App

licat

ion

(mg/

d)C

hlor

ide

(mg/

L)TD

S fo

r HC

C R

euse

Wat

er a

nd

TID

Fre

shw

ater

(mg/

L)

Jan 2011 Feb 2011 Mar 2011 Apr 2011 May 2011 Jun 2011 Jul 2011 Aug 2011 Sep 2011 Oct 2011 Nov 2011 Dec 2011 Jan 2012 Feb 2012 Mar 2012 Apr 2012 May 2012 Jun 2012

Hilmar Cheese Company (HCC) Reuse Water and Turlock Irrigation District (TID) Freshwater Application AreaTID Freshwater Application AreaHCC Reuse Water and Dairy Waste Water Application Area

1. Chloride and Sodium concentrations are not reported for TID water or Dairy Waste Water.2. Application data and history for Reuse Areas within the extent of the former Primary Lands; data not available for former Primary lands not owned by HCC or not receiving HCC Reuse water.3. Source: Hilmar Cheese Company Quarterly Monitoring Report dated January 27, 2012, April 19, 2012, July 19, 2012 and January 30, 2012.4. TID water may have been applied to the former Primary Lands identified as S-63, S-64 and S-65 prior to April 2011; however, HCC was not required to report for this period.

LEGEND

Flow

for D

airy

Was

te W

ater

(mg/

d)So

dium

(mg/

L)TD

S fo

r Dai

ry W

aste

Wat

er (m

g/L)

NOTES

Jun 2012May 2012Apr 2012Mar 2012Feb 2012Jan 2012Oct-Dec 2011Sep 2011Aug 2011Jul 2011Jun 2011May 2011Apr 2011Mar 2011Jan-Feb 2011

HCC Reuse Water, TID Freshwater and Dairy Waste Water Application Areamg/L = mg/d =milligrams per liter million gallons per day

2,3,4

Jul 2012 Aug 2012 Sep 2012

Jul 2012 Aug-Oct 2012

1

Oct 2012 Nov 2012 Dec 2012

Nov-Dec 2012

01.HCC.2014 DPG05/27/15 TJ


TOTAL DISSOLVED


CHLORIDE AND SODIUM


REUSE WATER


HISTORY

Flow

for T

ID F

resh

wat

er a

nd T

otal

Ap

plic

atio

n (m

g/d)

Chl

orid

e (m

g/L)

TDS

for H

CC

Reu

se W

ater

and

TI

D F

resh

wat

er (m

g/L)

Jan 2013 Feb 2013

Hilmar Cheese Company (HCC) Reuse Water and Turlock Irrigation District (TID) Freshwater Application AreaTID Freshwater Application AreaHCC Reuse Water and Dairy Wastewater Application Area

1. Chloride and Sodium concentrations are not reported for TID water or Dairy Wastewater.2. Application data and history for Reuse Areas within the extent of the former Primary Lands; data not available for former Primary lands not owned by HCC or not receiving HCC Reuse water.3. Source: Hilmar Cheese Company Quarterly Monitoring Report dated April 30, 2013, July 24, 2013, October 22, 2013, January 27, 2014, April 15, 2014, and July 16, 2014.4. TID water may have been applied to the former Primary Lands identified as S-63, S-64 and S-65 prior to April 2011; however, HCC was not required to report for this period.

LEGEND

Flow

for D

airy

Was

tew

ater

(mg/

d) a

nd

HC

C R

euse

Wat

erSo

dium

(mg/

L)TD

S fo

r Dai

ry W

aste

wat

er (m

g/L)

NOTES

Mar 2013Feb 2013Jan 2013


mg/L = mg/d =milligrams per liter million gallons per day

2,3,4

1

Mar 2013

HCC Reuse Water

Apr 2013 May 2013 June 2013

Apr, May 2013 June 2013

July 2013

July 2013

Aug 2013

Aug 2013

Sept 2013

Sept 2013

Oct 2013 Nov 2013 Dec 2013

Oct 2013 Nov 2013

Jan 2014

Jan 2014

Feb 2014

Feb, Mar 2014

Mar 2014 Apr 2014 May 2014 June 2014

Apr 2014 May 2014 June 2014 July 2014 Aug 2014 Sep 2014 Oct 2014 Nov 2014 Dec 2014

Dec 2013

July 2014 Aug 2014 Sept 2014 Oct 2014 Nov 2014 Dec 2014

FORMER PRIMARY LAND REUSE AREA APPLICATION TIMELINE

JANUARY 2013-DECEMBER 2014

ATTACHMENT 7b

HCC.2016 AIG6/2/2016 TJ

HILMAR CHEESE COMPANYHILMAR, CALIFORNIA FORMER PRIMARY LAND REUSE AREA

APPLICATION TIMELINE, 2015

ATTACHMENT 7c

TOTAL DISSOLVED


CHLORIDE AND SODIUM


REUSE WATER


HISTORY

Flow

for T

ID F

resh

wat

er a

nd T

otal

Ap

plic

atio

n (m

g/d)

Chl

orid

e (m

g/L)

TDS

for H

CC

Reu

se W

ater

and

TI

D F

resh

wat

er (m

g/L)

Jan 2015

TID Freshwater Application AreaHCC Reuse Water and Dairy Wastewater Application AreaAPPLICATION

COLOR CODES

Flow

for D

airy

Was

tew

ater

(mg/

d)

and

HC

C R

euse

Wat

erTD

S fo

r Dai

ry W

aste

wat

er (m

g/L)

NOTES


mg/L =mg/d =

milligrams per litermillion gallons per day

2,3,4

1

HCC Reuse Water

Feb 2015 Mar 2015 Apr 2015 May 2015 Jun 2015

Jan 2015 Feb 2015 Apr 2015 May 2015 June 2015Mar 2015

Hilmar Cheese Company (HCC) Reuse Water and Turlock Irrigation District (TID) Freshwater Application Area

1. Chloride and Sodium concentrations are not reported for TID water or Dairy Wastewater.

2. Application data and history for Reuse Areas within the extent of the former Primary Lands; data not available for former Primary lands not owned by HCC or not receiving HCC Reuse water.

3. Source: Hilmar Cheese Company Quarterly Monitoring Report dated April 7, July 16, October 14, 2015 and February 1, 2016.

4. TID water may have been applied to the former Primary Lands identified as S-63, S-64 and S-65 prior to April 2011; however, HCC was not required to report for this period.

0

1,000

2,000

3,000

4,000

5,000

6,000

0

100

200

300

400

500

600

700

800

900

1000TID Freshwater

HCC Reuse Water

Dairy Wastewater

0.4600.507

0.426

0.266 0.261

0.326

0.228

0.303

0.239

0.038

0.000

0.100

0.200

0.300

0.400

0.500

0.600

0.00

0.20

0.40

0.60

0.80

1.00

1.20TID Freshwater

HCC Reuse Water

Dairy Wastewater

Total Application (mg/d)

70

85

100

115

130

145

160

30

40

50

60

70

80

90

Chloride

Sodium

Sodi

um (m

g/L)

Jan 2015 Feb 2015 Mar 2015 Apr 2015 May 2015 Jun 2015 Jul 2015 Aug 2015 Sep 2015 Oct 2015 Nov 2015 Dec 2015

July 2015 Aug 2015 Sep 2015 Oct 2015 Nov 2015 Dec 2015

0.137

0.063 0.070 0.051 0.032

0.137

ATTACHMENT 8

2‐YEAR MOVING AVERAGE OF COCS IN MONITORING WELLS

ATTACHMENT 8

2‐YEAR MOVING AVERAGE IN MONITORING WELLS: CHLORIDE ‐ UPPER AQUIFER SHALLOW ZONE



Hilmar, California

Notes:


0

100

200

300

400

500

600

Chloride(m

illigram per liter [m

g/L])

MW‐07 RAO Shallow Zone (239 mg/L)

ATTACHMENT 8

2‐YEAR MOVING AVERAGE IN MONITORING WELLS: CHLORIDE ‐ UPPER AQUIFER SUPPLY ZONE



Hilmar, California

Notes:


0.0

100.0

200.0

300.0

400.0

500.0

600.0

Chloride (milligram per liter [m

g/L])

MW‐25 RAO Supply Zone (106 mg/L)

ATTACHMENT 8

2‐YEAR MOVING AVERAGE IN MONITORING WELLS: DISSOLVED IRON ‐ UPPER AQUIFER SHALLOW ZONE



Hilmar, California

Note:


0

1

2

3

4

5

6

7

8

9

10

Iron (milligram per liter [m

g/L])

MW‐03 MW‐05 MW‐07 MW‐15 RAO Shallow Zone (0.3 mg/L)

ATTACHMENT 8

2‐YEAR MOVING AVERAGE IN MONITORING WELLS: DISSOLVED MANGANESE ‐ UPPER AQUIFER SHALLOW ZONE (1 OF 2)



Hilmar, California

Notes:


0

1

2

3

4

5

6

7

8

Man

ganese (milligram per liter [m

g/L])

MW‐01 MW‐03 MW‐04 MW‐05 MW‐06 MW‐07 RAO Shallow Zone (0.34 mg/L)

ATTACHMENT 8

2‐YEAR MOVING AVERAGE IN MONITORING WELLS: DISSOLVED MANGANESE ‐ UPPER AQUIFER SHALLOW ZONE (2 OF 2)



Hilmar, California

Note:


0

1

2

3

4

5

6

7

8

Man


g/L])

MW‐08 MW‐09 MW‐11 MW‐16 MW‐17 RAO Shallow Zone (0.34 mg/L)

ATTACHMENT 8

2‐YEAR MOVING AVERAGE IN MONITORING WELLS: DISSOLVED MANGANESE ‐ UPPER AQUIFER SUPPLY ZONE



Hilmar, California

Note:


0

1

2

3

4

5

6

7

8

Man


g/L])

MW‐22 MW‐25 RAO Supply Zone (0.05 mg/L)

ATTACHMENT 8

2‐YEAR MOVING AVERAGE IN MONITORING WELLS: NITRATE AS NITROGEN ‐ UPPER AQUIFER SHALLOW ZONE



Hilmar, California

Note:


0

20

40

60

80

100

120

Nitrate as Nitrogen (milligram per liter [m

g/L])


ATTACHMENT 8

2‐YEAR MOVING AVERAGE IN MONITORING WELLS: DISSOLVED SODIUM ‐ UPPER AQUIFER SHALLOW ZONE



Hilmar, California

Note:


0

100

200

300

400

500

600

700

800

900

Sodium (milligram per liter [m

g/L])

MW‐06 MW‐07 MW‐09 MW‐13 RAO Shallow Zone (346 mg/L)

ATTACHMENT 8

2‐YEAR MOVING AVERAGE IN MONITORING WELLS: SULFATE ‐ UPPER AQUIFER SHALLOW ZONE



Hilmar, California

Notes:


0

50

100

150

200

250

300

350

Sulfate (milligram per liter [m

g/])


ATTACHMENT 8

2‐YEAR MOVING AVERAGE IN MONITORING WELLS: TOTAL DISSOLVED SOLIDS ‐ UPPER AQUIFER SHALLOW ZONE (1 OF 2)



Hilmar, California

Note:


0

500

1000

1500

2000

2500

3000

3500

Total D

issolved Solid

s (m


g/L])

MW‐01 MW‐06 MW‐07 MW‐09 MW‐12 RAO Shallow Zone (912 mg/L)

ATTACHMENT 8

2‐YEAR MOVING AVERAGE IN MONITORING WELLS: TOTAL DISSOLVED SOLIDS ‐ UPPER AQUIFER SHALLOW ZONE (2 OF 2)



Hilmar, California

Note:


0

500

1000

1500

2000

2500

3000

3500

Total D

issolved Solid

s (m


g/L])

MW‐13 MW‐15 MW‐16 MW‐17 RAO Shallow Zone (912 mg/L)

ATTACHMENT 9

HISTORICAL TREND CHARTS

ATTACHMENT 9

HISTORICAL TREND CHARTS: MW‐01 ‐ UPPER AQUIFER SHALLOW ZONE



Hilmar, California

Note:


0

50

100

150

200

250

0

200

400

600

800

1000

1200

1400

Chloride, M

anganese, N

itrate‐Nitrogen, Sodium, Sulfate (milligram per liter)

Total D

issolved Solid

s (m

illigram per liter)

Total Dissolved Solids Chloride Dissolved Manganese Nitrate‐Nitrogen Dissolved Sodium Sulfate

ATTACHMENT 9




Hilmar, California

Note:


0

50

100

150

200

250

300

350

400

0

200

400

600

800

1000

1200

1400

1600

Chloride, M

anganese, N


Total D

issolved Solid

s (milligram per liter)


ATTACHMENT 9




Hilmar, California

Note:


0

50

100

150

200

250

300

350

0

200

400

600

800

1000

1200

Chloride, M

anganese, N


Total D

issolved Solid

s (m

illigram per liter)


ATTACHMENT 9




Hilmar, California

Note:


0

50

100

150

200

250

300

350

400

450

0

200

400

600

800

1000

1200

1400

1600

1800

Chloride, M

anganese, N


Total D

issolved Solid

s (m

illigram per liter)


ATTACHMENT 9




Hilmar, California

Note:


0

100

200

300

400

500

600

700

0

500

1000

1500

2000

2500

Chloride, M

anganese, N


Total D

issolved Solid

s (m

illigram per liter)


ATTACHMENT 9




Hilmar, California

Note:


0

50

100

150

200

250

300

350

400

450

500

0

200

400

600

800

1000

1200

1400

1600

1800

2000

Chloride, M

anganese, N


Total D

issolved Solid



ATTACHMENT 9




Hilmar, California

0

20

40

60

80

100

120

140

160

180

200

0

100

200

300

400

500

600

700

800

900

1000

Chloride, M

anganese, N


Total D

issolved Solid



ATTACHMENT 9




Hilmar, California

Note:


0

100

200

300

400

500

600

700

800

900

0

500

1000

1500

2000

2500

3000

3500

Chloride, M

anganese, N


Total D

issolved Solid



ATTACHMENT 9




Hilmar, California

0

20

40

60

80

100

120

140

0

100

200

300

400

500

600

700

800

900

1000

Chloride, M

anganese, N


Total D

issolved Solid



ATTACHMENT 9




Hilmar, California

Note:


0

20

40

60

80

100

120

140

160

180

0

200

400

600

800

1000

1200

Chloride, M

anganese, N


Total D

issolved Solid



ATTACHMENT 9




Hilmar, California

Note:


0

100

200

300

400

500

600

700

800

900

1000

0

500

1000

1500

2000

2500

3000

3500

4000

Chloride, M

anganese, N


Total D

issolved Solid



ATTACHMENT 9




Hilmar, California

Note:


0

50

100

150

200

250

300

350

400

0

500

1000

1500

2000

2500

3000

3500

Chloride, M

anganese, N


Total D

issolved Solid

s (m

illigram per liter)


ATTACHMENT 9


2016 Second Semi‐Annual Upper Aquifer Performace Monitoring Report


Hilmar, California

0

20

40

60

80

100

120

140

160

180

0

200

400

600

800

1000

1200

1400

1600

Chloride, M

anganese, N


Total D

issolved Solid



ATTACHMENT 9




Hilmar, California

0

20

40

60

80

100

120

140

160

180

0

200

400

600

800

1000

1200

1400

1600

1800

Chloride, M

anganese, N


Total D

issolved Solid



ATTACHMENT 9

HISTORICAL TREND CHARTS: MW‐18 ‐ UPPER AQUIFER SUPPLY ZONE



Hilmar, California

Note:


0

10

20

30

40

50

60

70

80

90

100

0

100

200

300

400

500

600

700

Chloride, M

anganese, N


Total D

issolved Solid



ATTACHMENT 9




Hilmar, California

0

20

40

60

80

100

120

0

100

200

300

400

500

600

700

800

Chloride, M

anganese, N


Total D

issolved Solid



ATTACHMENT 9




Hilmar, California

Note:


Well MW‐21 has frequently been dry during sampling events, therefore, there is no analytical data to report from those events.

0

20

40

60

80

100

120

140

0

100

200

300

400

500

600

700

800

900

Chloride, M

anganese, N


Total D

issolved Solid



ATTACHMENT 9




Hilmar, California

Note:


0

20

40

60

80

100

120

140

0

100

200

300

400

500

600

700

800

Chloride, M

anganese, N


Total D

issolved Solid



ATTACHMENT 9

HISTORICAL TREND CHARTS: MW‐23 ‐ LOWER AQUIFER C‐ZONE



Hilmar, California

Note:


0

50

100

150

200

250

300

350

0

100

200

300

400

500

600

700

800

900

Chloride, M

anganese, N


Total D

issolved Solid



ATTACHMENT 9




Hilmar, California

Note:


‐10

10

30

50

70

90

110

130

150

0

50

100

150

200

250

300

350

400

450

500

Chloride, M

anganese, N


Total D

issolved Solid



ATTACHMENT 10

DATA VALIDATION REPORT

(ELECTRONIC FORMAT)

Data Validation Report: Fourth Quarter 2016 Sampling Event Hilmar Cheese Company, Hilmar, California January 9, 2017 Page ii

Hilmar Cheese Company ‐ 4Q2016 DV Report ‐ 1‐10‐17 Final.docx

TABLE OF CONTENTS PAGE TABLE ............................................................................................................................................. iii APPENDIX ........................................................................................................................................ iii STANDARD ACRONYMS AND ABBREVIATIONS .............................................................................. iv

SUMMARY OF DATA VALIDATION FINDINGS ...............................................................................S‐1

1.0 QUALITY ASSURANCE REVIEW ......................................................................................... 1‐1

2.0 DATA VALIDATION DETAILS ............................................................................................. 2‐1 2.1 Data Completeness .................................................................................................................. 2‐1 2.2 Analytical Holding Times and Sample Preservation ............................................................... 2‐1 2.3 Blank Samples ........................................................................................................................... 2‐1 2.4 Surrogate Recoveries ............................................................................................................... 2‐2 2.5 Laboratory Control Samples/Laboratory Control Sample Duplicates ................................... 2‐2 2.6 Laboratory Duplicate Samples ................................................................................................. 2‐2 2.7 Matrix Spike/Matrix Spike Duplicate Samples........................................................................ 2‐3 2.8 ICP Serial Dilution Results ........................................................................................................ 2‐3 2.9 Comparison of Field Duplicate Sample Results ...................................................................... 2‐4 2.10 Compound Identification and Quantification ......................................................................... 2‐4 2.11 Verification of Electronic Data Deliverable/Database............................................................ 2‐4

3.0 REFERENCE ....................................................................................................................... 3‐1

Data Validation Report: Fourth Quarter 2016 Sampling Event Hilmar Cheese Company, Hilmar, California January 9, 2017 Page iii


TABLE

Table 1 Samples Included in this Quality Assurance Review

APPENDIX

Appendix A Data Qualifier Definitions

Data Validation Report: Fourth Quarter 2016 Sampling Event Hilmar Cheese Company, Hilmar, California January 9, 2017 Page iv


ACRONYMS AND ABBREVIATIONS

COC chain‐of‐custody record

EDD electronic data deliverable

FD field duplicate

ICP Inductively Coupled Plasma

LCS laboratory control sample

LCSD laboratory control sample duplicate

MDL Method Detection Limit

MS/MSD matrix spike/matrix spike duplicate

QA quality assurance

QC quality control

RPD relative percent difference

SM Standard Methods

USEPA U.S. Environmental Protection Agency

µmhos/cm microhmos per centimeter

% Percent

Data Validation Report: Fourth Quarter 2016 Sampling Event Hilmar Cheese Company, Hilmar, California January 9, 2017 Page S‐1


SUMMARY OF DATA VALIDATION FINDINGS

This quality assurance (QA) review has identified aspects of the analytical data that required qualification

due to laboratory duplicate results, matrix spike results, Inductively Coupled Plasma (ICP) serial dilution

results, and results which were quantitated outside the calibration range of the instrument; a portion of the

total Kjeldahl nitrogen data were rejected due to a very low average matrix spike recovery. To confidently

use any of the analytical data within this sample set, the data user should understand the qualifications and

limitations of the results.

Data Validation Report: Fourth Quarter 2016 Sampling Event Hilmar Cheese Company, Hilmar, California January 9, 2017 Page 1‐1


1.0 QUALITY ASSURANCE REVIEW

This report summarizes the findings of the Level 2 data validation performed on the data for the 11 aqueous

samples sets (including two equipment blanks, one field blank, and one field duplicate [FD] set) specified in

Table 1. The samples were collected and submitted as part of the Fourth Quarter 2016 sampling activities

at the Hilmar Cheese Company in Hilmar, California. The samples were collected on October 12, 2016.

The samples were submitted to SGS Accutest Laboratories Northern California in San Jose, California.

The samples were collectively analyzed for alkalinity (total alkalinity, bicarbonate, and carbonate) by

Standard Methods (SM) 2320 B; chloride, nitrate, and sulfate by U.S. Environmental Protection Agency

(USEPA) Methods 300.1; dissolved metals (calcium, iron, potassium, magnesium, manganese, and sodium)

by USEPA Method 200.7; specific conductivity by USEPA Method SM 2540 C; total dissolved solids by

SM 2540 C; and total Kjeldahl nitrogen by USEPA Method 351.2. The analyses for chloride, nitrate, and

sulfate were subcontracted to and analyzed by McCampbell Analytical, Inc. in Pittsburg, California. All other

analyses were transferred to and performed by SGS Accutest Laboratories Southeast in Orlando, Florida.

The parameters for the analyses of each sample are specified in Table 1.

This review has been performed in accordance with the National Functional Guidelines for Inorganic Data

Review (USEPA, 2014) and guidance from the appropriate Region 9 Data Quality Indicator Tables1.

In addition, the Level 2 data deliverables were examined to determine the usability of the analytical results

and compliance relative to requirements specified by the reported methodology. Qualifier codes have been

placed into the database, where necessary, so that the data user can quickly assess the qualitative and/or

quantitative reliability of any result based on the criteria evaluated. Each analytical method was reviewed

for completeness, accuracy, and precision in the following areas to determine any impact to data quality

and usability:

data completeness;

analytical holding times and sample preservation;

blank samples;

laboratory control samples/laboratory control sample duplicates (LCS/LCSD);

surrogate recoveries;

laboratory duplicate sample results;

matrix spike/matrix spike duplicate (MS/MSD) samples;

Inductively Coupled Plasma (ICP) serial dilution results;

comparison of FD samples results;

compound identification and quantification; and,

verification of electronic data deliverable (EDD)/database.

1 https://www.epa.gov/quality/data‐quality‐indicator‐tables‐region‐9



This critical quality assurance (QA) review identifies data quality issues for specific samples and specific

evaluation criteria. The data qualifications allow the data end‐user to best understand the usability of the

analytical results. Data that have not been qualified in this report should be considered valid based on the

quality control (QC) criteria that have been applied.



2.0 DATA VALIDATION DETAILS

This section presents results of the data validation of the samples with respect to each of the areas of data

review listed above. Where appropriate, data have been qualified. Data qualifier flags (Appendix A) that

are applied to data may indicate a bias in the reported data and should be considered during all

project evaluations.

2.1 Data Completeness

All sample analyses were performed as requested on the chain‐of‐custody records (COC) as revised by

Jacobson James & Associates, Inc. personnel via e‐mail. Issues observed during the data validation process

are noted below.

The changes made to the COCs in the field were not properly lined out, initialed, and dated.

In the subcontracted data package and the associated EDD, McCampbell Analytical, Inc.

identified samples W‐MW‐05‐A and FB‐MW‐05‐A as W‐MW‐5‐A and FB‐MW‐5‐A, respectively.

These discrepancies were noted in the annotated data package and corrected in the database.

Field blank, FB‐MW‐05‐A, was analyzed for chloride, nitrate, specific conductivity, sulfate, total

dissolved solids even though it was placed on hold.

On the SGS Accutest COCs for the subcontracted samples, the date of sample collection was

reported as 10/13/16. The actual date of collection was 10/12/16.

The TDS analyses were performed by SGS Accutest Southeast. However, upon the time of

analysis SGS Accutest Southeast had applied for but not received their certification

from California.

2.2 Analytical Holding Times and Sample Preservation

The samples submitted to the laboratory for analysis were properly preserved according to guidelines

established by the USEPA. All samples were analyzed within the recommended holding times.

2.3 Blank Samples

Laboratory method blanks were analyzed for all methods with each batch of samples. In addition, two

equipment blank sets were collected and submitted as part of this sampling event. The equipment blanks

were collectively analyzed for all target analytes. The results of blank samples were used to evaluate the

impact of blank contamination on the sample data. All laboratory method blanks were free of

contamination at levels at or above the Method Detection Limits (MDL). All equipment blanks were free of

contamination at or above the reporting limits for all analytes except specific conductivity.



Equipment/Field Blank Analyte Concentration

FB‐MW‐05‐A Specific Conductivity 2.2 micromhos per centimeter

[µmhos/cm]

EB‐101216‐A Specific Conductivity 1.7 µmhos/cm

EB‐MW‐25‐A Specific Conductivity 1.5 µmhos/cm

All of the reported positive results for specific conductivity in the associated samples were greater than

5‐times the blank level. Consequently, qualification of the associated data was not warranted.

2.4 Surrogate Recoveries

For the chloride, nitrate, and sulfate analyses by EPA Methods 300.1, all surrogate (formate) recoveries met

laboratory QC criteria except the surrogate in sample W‐MW‐15‐A (100‐times dilution). The surrogate in

sample W‐MW‐15‐A was diluted out.

2.5 Laboratory Control Samples/Laboratory Control Sample Duplicates

LCS or LCS/LCSD were prepared and analyzed with each batch of samples for all appropriate methods.

The LCS/LCSD results (average recoveries and/or relative percent differences [RPD]) were within acceptance

criteria for accuracy and/or precision established by the laboratory and the appropriate

guidance documents.

2.6 Laboratory Duplicate Samples

The laboratory performed laboratory duplicate analyses on project and non‐project samples in association

with samples collected during this sampling event. Acceptable precision was demonstrated by all

laboratory duplicate analyses performed on project samples except as noted below.

A high RPD was reported for potassium (22.1 percent [%]) in the laboratory duplicate analyses

of samples W‐MW‐15‐AF (Batch MP30988) which is associated with samples W‐MW‐01‐AF,

W‐MW‐03‐AF, W‐MW‐07‐AF, W‐MW‐07‐BF, W‐MW‐13‐AF, W‐MW‐15‐AF and W‐MW‐25‐AF.

Consequently, the reported positive results for potassium in samples W‐MW‐01‐AF,

W‐MW‐03‐AF, W‐MW‐07‐AF, W‐MW‐07‐BF, W‐MW‐13‐AF, and W‐MW‐15‐AF are

estimated (J).

An equipment blank (EB‐MW‐25‐A) was selected by the laboratory for the specific conductivity laboratory

duplicate analyses. Although acceptable precision was demonstrated, this blank matrix may not

representative of the project‐specific sample matrix and the results were not directly used in the

assessment of precision for the respective test methods. Instead, the assessment of precision was

performed using the LCD/LCSD results (see Section 2.5).



In the cases where the laboratory selected non‐project samples for laboratory duplicate purposes, the

results were not used in the assessment of precision for the respective test methods. The assessment of

precision was performed using the LCD/LCSD results (see Section 2.5).

2.7 Matrix Spike/Matrix Spike Duplicate Samples

The laboratory performed MS/MSD analyses on project samples in association with samples collected

during this sampling event. As requested on the associated COCs, samples W‐MW‐07‐A and W‐MW‐07‐AF

were used for the MS/MSD analyses.

In the samples listed below, the source results for the following analytes exceeded 4‐times the spike level;

consequently, the recoveries for these analytes in the associated MS/MSD analyses were not evaluated.

Sample Analyte

W‐MW‐15‐AF (Batch MP30988)

Dissolved Potassium, Dissolved Sodium

Acceptable precision and accuracy were demonstrated by all other project samples used for the MS/MSD

analyses except as noted below.

A very low average percent recovery (0.0%) was reported for total Kjeldahl nitrogen in the MS/MSD

analyses of sample W‐MW‐15‐A (Batch GP28674). Consequently, the reported not‐detected results for

total Kjeldahl nitrogen in samples W‐MW‐01‐A, W‐MW‐05‐A, W‐MW‐13‐A, and W‐MW‐25‐A have been

rejected (R) and the reported positive results for total Kjeldahl nitrogen in samples W‐MW‐03‐A,

W‐MW‐07‐A, W‐MW‐07‐B, and W‐MW‐15‐A may be biased low (J‐).

In the cases where the laboratory selected non‐project samples for MS/MSD purposes, the results were not

used in the assessment of precision and accuracy for the respective test methods. The assessment of

precision and accuracy was performed using the LCS results (see Section 2.5).

2.8 ICP Serial Dilution Results

The laboratory performed ICP serial dilution analyses on the following project samples associated with

samples in this sampling event.

Analytes Batch Sample

Dissolved Calcium, Dissolved Iron, Dissolved Magnesium, Dissolved Manganese,

Dissolved Potassium, Dissolved Sodium MP30988 W‐MW‐15‐AF

In the ICP serial dilution of sample W‐MW‐15‐AF (Batch MP30988), a high percent difference (12.5%) was

reported for dissolved potassium. Consequently, the reported positive results for dissolved potassium in

samples W‐MW‐01‐AF, W‐MW‐03‐AF, W‐MW‐07‐AF, W‐MW‐07‐BF, W‐MW‐13‐AF, and W‐MW‐15‐AF are

estimated (J).



In the cases where the laboratory selected non‐project samples for the ICP serial dilution, the results were

not used in the assessment of the data for the respective test method.

2.9 Comparison of Field Duplicate Sample Results

One (1) blind FD set (as specified in Table 1) were submitted as part of this data set. The FD samples were

collected and submitted for sample point MW‐07. The FD samples represent 14.3% of the primary

samples collected.

Primary Sample Identification Field Duplicate Identification

W‐MW‐07‐A W‐MW‐07‐B

W‐MW‐07‐AF W‐MW‐07‐BF

Acceptable precision and sample representativeness were demonstrated by the correlation observed

between the results in the FD sets (± Method Reporting Limit MRL or RPD ≤ 20%).

2.10 Compound Identification and Quantification

The project‐required reporting limits were achieved for all target analytes which did not warrant dilution.

The analyses for all samples which required dilution were properly diluted to quantitate the elevated levels

of the target analytes except for potassium in sample W‐MW‐15‐A. The potassium result reported in this

sample was quantitated outside the calibration range of the instrument.

2.11 Verification of Electronic Data Deliverable/Database

The sample data in the final electronic file (XLS) provided by the client matched the sample data reported in

the hardcopy laboratory report.



3.0 REFERENCE

U.S. Environmental Protection Agency (USEPA), 2014. National Functional Guidelines for Inorganic Data Review. August.

TABLE

TABLE 1 SAMPLES INCLUDED IN THIS QUALITY ASSURANCE REVIEW Data Validation Report: Fourth Quarter 2016 Sampling Event

Hilmar Cheese Company Hilmar, California

Page 1 of 2

Sample Identification

Laboratory


Date

Sampled

Parameter(s)

Examined

FA37765

W‐MW‐13‐A FA37765‐1 10/12/2016 ALK, ANIONS, SC, TDS, TKN

W‐MW‐13‐AF FA37765‐2F 10/12/2016 MD


W‐MW‐15‐AF FA37765‐4F 10/12/2016 MD


W‐MW‐05‐AF FA37765‐6F 10/12/2016 MD

FB‐MW‐05‐A (Field Blank)

FA37765‐7 10/12/2016 ANIONS, SC, TDS


W‐MW‐25‐AF FA37765‐10F 10/12/2016 MD

EB‐101216‐A (Equipment Blank)

FA37765‐11 10/12/2016 ALK, ANIONS, SC, TDS, TKN

EB‐101216‐AF (Equipment Blank)

FA37765‐12F 10/12/2016 MD


W‐MW‐07‐AF FA37765‐14F 10/12/2016 MD

W‐MW‐07‐B (Field Duplicate of W‐MW‐07‐A)


W‐MW‐07‐BF (Field Duplicate of W‐MW‐07‐AF)

FA37765‐16F 10/12/2016 MD


W‐MW‐03‐AF FA37765‐18F 10/12/2016 MD

TABLE 1 SAMPLES INCLUDED IN THIS QUALITY ASSURANCE REVIEW Data Validation Report: Fourth Quarter 2016 Sampling Event

Hilmar Cheese Company Hilmar, California

Page 2 of 2


Laboratory


Date

Sampled

Parameter(s)

Examined


W‐MW‐01‐AF FA37765‐20F 10/12/2016 MD

EB‐MW‐25‐A (Equipment Blank)


EB‐MW‐25‐AF (Equipment Blank)

FA37765‐22F 10/12/2016 MD

Notes: ALK = alkalinity (total alkalinity, bicarbonate, and carbonate) by Standard Methods (SM) 2320 B ANIONS = chloride, nitrate, and sulfate by U.S. Environmental Protection Agency (USEPA) Methods 300.0/9056A MD = dissolved metals (calcium, iron, potassium, magnesium, manganese, and sodium) by USEPA Method 200.7 SC = specific conductivity by SM 2510 B TDS = total dissolved solids by SM 2540 C TKN = total Kjeldahl nitrogen by USEPA Method 351.2

APPENDIX A

DATA QUALIFIER DEFINITIONS

Appendix A: Data Qualifier Definitions Data Validation Report

DATA QUALIFIER DEFINITIONS

DNR Do Not Report in the final data set. The data were included in the hardcopy report for

completeness only as the sample analyses were associated with laboratory Batch QC

quality control analyses. These results should not be used as part of the

decision‐making process nor reported as part of the final data set.

J The analyte was positively identified but the associated numerical value may not

represent the actual concentration of the analyte in the sample due to an analytical

bias in precision or accuracy, or because the resulting concentration has been reported

at a confidence level of less than 99%.

Jo A subset of the “J” flag described above. The analyte was positively identified but the

associated estimated numerical value reported by the laboratory was less than the

sample‐specific reporting limit for this analyte. Consequently, there is a lower

confidence in the accuracy in the result.

N The analysis indicates the presence of an analyte for which there is presumptive

evidence to make a tentative identification.

NA not analyzed

R The sample results are rejected due to serious deficiencies in the ability to analyze the

sample and meet quality control criteria. The presence or absence of the analyte

cannot be verified and data are not usable.

U The analyte was detected above the laboratory‐reported sample quantitation limit.

However, due to contamination from an outside source such as laboratory or field

equipment, the analyte should be considered “not detected” at or above the adjusted

sample quantitation limit.

UJ The analyte was not detected above the reported sample quantitation limit. However,

the reported quantitation limit is approximate and may or may not represent the

actual limit of quantitation necessary to accurately and precisely measure the analyte

in the sample.

+ The result is biased high.

‐ The result is biased low.

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