Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the...

108
1 Blue, Karen To: Kilburn, Dianna Subject: RE: Response to ADEQ review of Second Half 2018 Groundwater Monitoring Report and Notice of Statistically Significant Results, Eco-Vista, Class 1 Landfill, Permit No. 0290-S1-R3 From: Dana Derrington [mailto:[email protected]] Sent: Thursday, January 24, 2019 11:47 AM To: Kilburn, Dianna Cc: 'Jodi Reynolds-Coffelt'; Cramer, Robert; 'Adrienne Maull' Subject: Response to ADEQ review of Second Half 2018 Groundwater Monitoring Report and Notice of Statistically Significant Results, Eco-Vista, Class 1 Landfill, Permit No. 0290-S1-R3 Hello Dianna, On behalf of Waste Management of Arkansas, FTN is submitting the attached letter in response to the January 7, 2019 letter from ADEQ (DIN 75256) regarding the groundwater program at the EcoͲVista Landfill. Please contact me at (314) 786Ͳ5855 or Jodi ReynoldsͲCoffelt (479) 968Ͳ2305 if you have any questions. Regards, Dana Dana Derrington, PE * , PG * FTN Associates, Ltd. 13990 Olive Blvd., Suite 203 Chesterfield, MO 63017 Office: (314) 786Ͳ5855 Cell: (501) 920Ͳ9642 * Missouri and Arkansas Rec’d Digitally AFIN:_________________________ PMT#:_________________________ S W DOC ID#:______________________ M D TO:___________________________ By Karen Blue at 12:55 pm, Jan 24, 2019 72-00144 0290-S1-R3 75357 DK>FILE <KMB

Transcript of Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the...

Page 1: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

1

Blue, Karen

To: Kilburn, DiannaSubject: RE: Response to ADEQ review of Second Half 2018 Groundwater Monitoring Report

and Notice of Statistically Significant Results, Eco-Vista, Class 1 Landfill, Permit No. 0290-S1-R3

From: Dana Derrington [mailto:[email protected]]Sent: Thursday, January 24, 2019 11:47 AM To: Kilburn, Dianna Cc: 'Jodi Reynolds-Coffelt'; Cramer, Robert; 'Adrienne Maull' Subject: Response to ADEQ review of Second Half 2018 Groundwater Monitoring Report and Notice of Statistically Significant Results, Eco-Vista, Class 1 Landfill, Permit No. 0290-S1-R3

Hello Dianna,

On behalf of Waste Management of Arkansas, FTN is submitting the attached letter in response to the January 7, 2019letter from ADEQ (DIN 75256) regarding the groundwater program at the Eco Vista Landfill. Please contact me at (314)786 5855 or Jodi Reynolds Coffelt (479) 968 2305 if you have any questions.

Regards,Dana

Dana Derrington, PE*, PG*

FTN Associates, Ltd.13990 Olive Blvd., Suite 203Chesterfield, MO 63017Office: (314) 786 5855Cell: (501) 920 9642*Missouri and Arkansas

Rec’d Digitally

AFIN:_________________________

PMT#:_________________________ SW

DOC ID#:______________________ MD

TO:___________________________

By Karen Blue at 12:55 pm, Jan 24, 2019

72-00144

0290-S1-R3

75357

DK>FILE <KMB

Page 2: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Regional Offices: Fayetteville, Arkansas; Baton Rouge, Louisiana • www.ftn-assoc.com • [email protected]

January 24, 2019

[email protected]

Ms. Dianna Kilburn, PG

Groundwater Branch Manager

Office of Land Resources

Arkansas Department of Environmental Quality

5301 Northshore Drive

North Little Rock, AR 72118-5317

RE: Response to ADEQ Review of Second Half 2018 Groundwater Monitoring Report and

Notice of Statistically Significant Results, Second Half 2018 Groundwater Monitoring

Eco-Vista, Class 1 Landfill, Tontitown, AR

Permit No. 0290-S1-R3; AFIN: 72-00144

FTN No. R06820-0100-004

Dear Ms. Kilburn:

On behalf of the Waste Management of Arkansas Inc. (WM) Eco-Vista Class 1 Landfill (the landfill),

FTN Associates, Ltd. (FTN) is submitting this response to the letter sent to Ms. Jodi Reynolds-Coffelt

of WM from the Arkansas Department of Environmental Quality (ADEQ) dated January 7, 2019

(ADEQ Document Identification Number [DIN] 75256).

The ADEQ comments and WM’s responses to each are presented below:

ADEQ Comment 1: In Appendix E Statistical Evaluation, July 2018 Event under Summary of

Statistical Limit Exceedances during the Third Quarter Monitoring Period in 2018 states that “The

resample sulfate concentration at MW-15 (11.0 mg/L) confirms the initial exceedance at LGW-15.”

MW-15 cannot confirm an exceedance at another well. LGW-15 was not even resampled. Please

explain this inconsistency.

WM Response: The inconsistency noted above was a typographical error. The report should

have stated “The resample sulfate concentration at MW-15 (11.0 mg/L) confirms the initial

exceedance at MW-15.” A revised Appendix E correcting the error is included as

Attachment 1 to this letter.

ADEQ Comment 2: Also, in Appendix E, Attachments A through E are not included in the report.

Please resubmit Appendix E with all attachments.

Page 3: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Ms. Dianna Kilburn, PG

Eco-Vista Landfill, LLC

January 24, 2019

Page 2

WM Response: A revised Appendix E that includes Attachments A through E is included as

Attachment 1 to this letter.

ADEQ Comment 3: Document ID 74554 states that FTN Associates, Ltd. would submit a NEI work

plan by October 19, 2018. ADEQ has not received this work plan. Please submit a NEI work plan.

WM Response: As FTN discussed with Robert Cramer with ADEQ via telephone on January

18, 2019, the NEI work plan is in progress and WM expects to submit the NEI work plan to

ADEQ in February 2019. WM anticipates submittal of the work plan no later than February

28, 2019.

ADEQ Comment 4: In Section 6.0 Corrective Action Monitoring the report states that “wells NE-6

through NE-13 are not currently required to be sampled as part of the monitoring program.” In

Document ID 74217 ADEQ requested the wells NE-6 through NE-13 to be sampled during semi-

annual groundwater sampling events. It was acknowledged in Document ID 74554 that the facility

would sample the wells as requested. Please amend the text and provide an explanation and correction

for the oversight.

WM Response: Wells NE-6 through NE-13 will be sampled on a semiannual basis beginning

in the first half of 2019. The second half of 2018 sampling event, performed during July 2018,

had already been completed (July 10 to July 18, 2018) when WM committed to semiannual

sampling in Document ID 74554 (September 13, 2018). As requested, page 6 of the report was

revised to reflect this upcoming change and is attached to this letter.

If you have any questions regarding this submittal, please contact me at (314) 786-5855 or

Jodi Reynolds-Coffelt at (479) 968-2305.

Respectfully Submitted,

FTN ASSOCIATES, LTD.

Dana Derrington, PE, PG

Project Manager

DLD/kae

Attachment

CC: Jodi Reynolds-Coffelt, Waste Management of Arkansas, Inc., Environmental Protection

Manager – Arkansas

Robert Cramer, Geologist, ADEQ

R:\WP_FILES\06820-0100-004\CORRESPONDENCE\2019-01-24 L-D KILBURN 2H2018 GWMR RESPONSE\2019-01-24 L-D KILBURN.DOCX

Page 4: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Attachment 1 — Revised Appendix E, Second Half of 2018 Groundwater

Monitoring Report

Page 5: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Results of the Ground Water Statistics

for Eco-Vista Sanitary Landfill

Third Quarter Monitoring Event in 2018

Prepared for: Waste Management

2210 Waste Management Drive Springdale, Arkansas 72762

Prepared by:

Jeffrey A. Holmgren Otter Creek Environmental Services, L.L.C.

40W565 Foxwick Court Elgin, IL 60124 (847) 464-1355

December 14, 2018

Page 6: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Ground Water Statistics for Eco-Vista Sanitary Landfill Third Quarter Monitoring Event In 2018

C:\Otter Creek Environmental\Arkansas\Eco-Vista\ecovistaq318RRRR.doc December 14, 2018

- 1 -

Introduction This report contains the results of the statistical analyses used to evaluate the ground water data obtained during the third quarter monitoring event in 2018 at Eco Vista Sanitary Landfill. The ground water monitoring well network at Eco Vista Sanitary Landfill includes MW-1N, MW-2N, MW-3N, MW-7N, MW-8N, MW-10N, MW-11N, MW-15, MW-16, MW-17, MW-19, MW-20, MW-21, LGW-2, LGW-3R, LGW-4, LGW-5, LGW-6, LGW-7, LGW-8R, LGW-9, LGW-10, and LGW-14R. These monitoring wells were sampled during July 10-17, 2018 and analyzed for the parameters required by permit. The statistical plan is designed to detect a release from the facility at the earliest indication so that it is protective of human health and the environment. An intrawell methodology is described and then applied to the Eco Vista Sanitary Landfill data. The statistical plan conforms with USEPA Guidance document (“Statistical Analysis of Ground-Water Monitoring Data at RCRA Facilities, Unified Guidance”, March 2009), and the American Society for Testing and Materials (ASTM) standard D6312-98, Developing Appropriate Statistical Approaches for Ground-Water Detection Monitoring Programs. Ground Water Monitoring Program The groundwater monitoring network for Eco Vista Sanitary Landfill includes the twenty-three wells designated above. Each of the groundwater monitoring wells is to be sampled and analyzed for the detection monitoring parameters listed below. Acetone trans-1,4-Dichloro-2-butene Iodomethane Acrylonitrile 1,1-Dichloroethane 4-Methyl-2-pentanone Benzene 1,2-Dichloroethane Styrene Bromochloromethane 1,1-Dichloroethene 1,1,1,2-Tetrachloroethane Bromodichloromethane cis-1,2-Dichloroethene 1,1,2,2-Tetrachloroethane Bromoform trans-1,2-Dichloroethene Tetrachloroethene Carbon disulfide 1,2-Dichloropropane Toluene Carbon tetrachloride cis-1,3-Dichloropropene 1,1,1-Trichloroethane Chlorobenzene trans-1,3-Dichloropropene 1,1,2-Trichloroethane Chloroethane Ethylbenzene Trichloroethene Chloroform 2-Hexanone Trichlorofluoromethane Dibromochloromethane Bromomethane 1,2,3-Trichloropropane 1,2-Dibromo-3-chloropropane Chloromethane Vinyl acetate 1,2-Dibromoethane Dibromomethane Vinyl chloride 1,2-Dichlorobenzene Methylene chloride Xylenes (Total) 1,4-Dichlorobenzene 2-Butanone Antimony, Total Chromium, Total Selenium, Total Arsenic, Total Cobalt, Total Silver, Total Barium, Total Copper, Total Thallium, Total Beryllium, Total Lead, Total Vanadium, Total Cadmium, Total Nickel, Total Zinc, Total Chloride Sulfate pH Iron Total Dissolved Solids (TDS) Specific Conductance Manganese Total Organic Carbon (TOC)

Page 7: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Ground Water Statistics for Eco-Vista Sanitary Landfill Third Quarter Monitoring Event In 2018

C:\Otter Creek Environmental\Arkansas\Eco-Vista\ecovistaq318RRRR.doc December 14, 2018

- 2 -

The ground water data obtained during the third quarter monitoring event in 2018 are summarized in Attachment A. STATISTICAL METHODOLOGIES FOR DETECTION MONITORING The statistical guidance provides several options for statistically evaluating the ground water data at those wells that monitor the open cells or contiguous MSWLF units. The preferred methods for comparing inorganic ground water data are using either prediction limits or using control charts. Both of these methods were initially applied to the Eco Vista Sanitary Landfill data using the DUMPStat® statistical program. DUMPStat® is a program for the statistical analysis of groundwater monitoring data using methods described in “Statistical Methods for Groundwater Monitoring” by Dr. Robert D. Gibbons. The DUMPStat program is completely consistent with all USEPA regulations and guidance and the ASTM D6312-98 guidance. It was previously determined that an intrawell control chart method is the more appropriate statistic for Eco Vista Sanitary Landfill. Ground water statistics are to be done on the inorganic constituents listed. The organic constituents are compared to practical quantitation limits (PQLs), in lieu of statistical comparisons to historical concentrations. Volatile Organic Compounds Volatile Organic Compounds (VOCs) are generally man-made compounds not present in ambient ground water. If VOCs are initially detected above their statistical limit (i.e., the laboratory PQL or reporting limit), a verification resample will be conducted at the next scheduled sampling event. A statistical exceedance will be indicated if the VOC detection is confirmed by the subsequent monitoring. VOCs detected in the ground water at Eco Vista Sanitary Landfill during the third quarter monitoring event in 2018 are summarized in the table below. Acetone was detected at wells LGW-14R, LGW-2, LGW-3R, LGW-8R, MW-10N, MW-11N, and MW-1N, however acetone was also detected in the associated equipment blank and trip blank at similar concentrations. The current acetone detections are likely artifacts of the sampling or analyses. Historical detections are summarized in Attachment B.

VOCs detected at Eco Vista Sanitary Landfill during the third quarter monitoring event in 2018

Detection Wells

Well VOC Detected Result, μg/L

Reporting Limit, μg/L

Verified/ Awaiting Verification

LGW-2 Vinyl chloride 1.7 1 Awaiting Verification Monitoring well LGW-2 was resampled on October 2, 2018 and analyzed for vinyl chloride. The resample vinyl chloride concentration (2.1 μg/L) confirms the initial detection at LGW-2, therefore it is statistically significant.

Page 8: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Ground Water Statistics for Eco-Vista Sanitary Landfill Third Quarter Monitoring Event In 2018

C:\Otter Creek Environmental\Arkansas\Eco-Vista\ecovistaq318RRRR.doc December 14, 2018

- 3 -

Intrawell statistics Intrawell statistics are appropriate for facilities where the upgradient wells do not accurately characterize the natural ground water conditions downgradient from the facility. This may be due to different hydrogeological conditions where the wells are screened, having too few upgradient wells to account for the spatial variability, or the site exhibiting no definable hydraulic gradient. Intrawell statistics compare new measurements to the historical data at each ground water monitoring well independently. It is recommended that at least eight background samples be obtained prior to performing the statistics. The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because it will detect releases both in terms of the constituent concentration and cumulative increases. This method is also extremely sensitive to sudden and gradual releases. A requirement for constructing these control charts is that the parameter is detected at a frequency greater than or equal to 25%, otherwise the data variance is not properly defined. The combined Shewhart-CUSUM control chart assumes that the data are independent and normally distributed with a fixed mean and a constant variance. Independent data is much more critical than the normality assumption. To achieve independence, it is recommended that data are collected no more frequently than quarterly to account for seasonal variation. The combined Shewhart-CUSUM control chart is extremely robust to deviations from normality. Because the control charts do not use a specific multiplier based on a normal distribution, it is more conservative to assume normality. It is recommended that at least eight rounds of data be available to provide a reliable estimate of the mean and standard deviation of the parameter concentration, although the control charts will be generated with as few as four data points. Having only four data points may produce greater uncertainty in the mean and standard deviation of the background data, leading to higher control limits, thus having a potentially high false negative rate. Many groundwater monitoring parameters are not detected at a frequency great enough to generate the combined Shewhart-CUSUM control charts. For constituents that are detected less than 25% of the time at a particular well, the data should be plotted as a time series until a sufficient number of data points are available to provide a 99% confidence nonparametric prediction limit. Thirteen independent measurements (with 1 resample) are necessary to achieve a 99% confidence (1% false positive rate) nonparametric prediction limit. Eight independent measurements (for pass 1 of 2 resamples) are necessary to achieve a 99% confidence nonparametric prediction limit. The nonparametric prediction limit is the largest determination out of the data set collected for that well and parameter. If the detection frequency is 0% after thirteen samples have been collected, the practical quantitation limit (PQL) becomes the nonparametric prediction limit. In developing the statistical background, the historical data must be thoroughly screened for anomalous data due to sampling error, analytical error, or simply by chance alone. An erroneous data point, if not removed prior to the mean and variance computations, would yield a larger control limit thus increasing the false negative rate. The DUMPStat® program screens for outliers using the Dixon test. If the Dixon test indicates an outlier, the value is compared to three times the median value for intrawell analyses. If the value fails both criteria of the two-stage screening, the value is considered a statistical outlier and will

Page 9: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Ground Water Statistics for Eco-Vista Sanitary Landfill Third Quarter Monitoring Event In 2018

C:\Otter Creek Environmental\Arkansas\Eco-Vista\ecovistaq318RRRR.doc December 14, 2018

- 4 -

not be used in the mean and variance determinations. Anomalous data will still be plotted on the graphs (with a unique symbol) but will not be included in the calculations. The verification resample plan is an integral function of the statistical plan to reduce the probability that anomalous data obtained after the background has been established, is indicative of a landfill release. The background data for each well and constituent is tested for existing trends using Sen's nonparametric estimate of trend. If contamination exists prior to completing the background, the control limits could be potentially high and this control chart method would not be able to detect an increasing trend unless the increase is severe. Results of the Intrawell Statistics for Detection Monitoring The trace metals and inorganic indicator data from wells MW-1N, MW-10N, MW-11N, MW-15, MW-16, MW-17, MW-19, MW-20, LGW-2, LGW-3R, LGW-4, LGW-8R, and LGW-14R were evaluated using the combined Shewhart-CUSUM control chart method. Assessment statistics were performed on the remaining wells due to previous control limit/prediction limit exceedances or VOC detections. The background used to determine control limits includes data obtained from January 2006 through 2012 for well MW-1N; January 2006 through 2014 for wells MW-10N, MW-11N, LGW-2, LGW-4; June 2015 through October 2106 for wells MW-15, MW-16, MW-17, MW-19, and MW-20; and February 2009 through 2014 for wells LGW-8R and LGW-14R. LGW-3R is a replacement well for LGW-3 and is in background monitoring. Upon completion of eight rounds of background, LGW-3R will be statistically evaluated. A summary of the intrawell statistics is included in Attachment C, Table 1 “Summary Statistics and Intermediate Computations for Combined Shewhart-CUSUM Control Charts.” The control charts or prediction limit graphs follow the summary table. Outliers identified on the control charts are summarized in the table below.

Summary of Statistical Outliers Identified During Background on the Control Chart Graphs

Well Parameter Result Date Chromium, μg/L 43.0 2/6/2009

Iron, μg/L 1300 2/6/2009 Manganese, μg/L 120 2/6/2009

Nickel, μg/L 42.0 2/6/2009 LGW-14R

Zinc, μg/L 24.0 2/6/2009 LGW-2 Lead, μg/L 12.0 1/25/2006

Iron, μg/L 1400 10/26/2006 LGW-4 Zinc, μg/L <20 10/26/2006

Manganese, μg/L 8.7 7/10/2007 MW-10N Zinc, μg/L <20 7/10/2007

MW-11N Lead, μg/L 16.0 1/19/2006 Iron, μg/L 1200 8/5/2015 MW-15 Zinc, μg/L 23.0 8/5/2015

Chloride, mg/L 19.0 1/7/2016 MW-20 Sulfate, mg/L 57.0 1/7/2016

Page 10: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Ground Water Statistics for Eco-Vista Sanitary Landfill Third Quarter Monitoring Event In 2018

C:\Otter Creek Environmental\Arkansas\Eco-Vista\ecovistaq318RRRR.doc December 14, 2018

- 5 -

For the parameters evaluated, the statistical limit exceedances identified are summarized in the table below.

Summary of statistical limit exceedances during the third quarter monitoring period in 2018.

Well Parameter Result CUSUM Value

Control limit

Control Limit Type

Verified/Awaiting Verification

TDS, mg/L 230 276.6753 256.1775 Normal Awaiting Verification LGW-14R Zinc, μg/L 60.0 -- 5.4000 Nonparametric Awaiting Verification

Arsenic, μg/L 10.0 -- 5.0000 Nonparametric Verified Iron, μg/L 17000 16722.0707 2707.4704 Normal Verified TDS, mg/L 560 610.9469 478.3983 Normal Verified

LGW-2

TOC, mg/L 1.7 -- 1.0000 Nonparametric Verified LGW-8R TDS, mg/L 350 400.1549 369.4059 Normal Verified MW-15 Sulfate, mg/L 12.0 17.7220 13.5608 Normal Awaiting Verification MW-1N Zinc, μg/L 47.0 154.2612 144.0072 Normal Awaiting Verification

A control chart factor was selected to provide a balance of the site-wide false positive and false negative rates. A statistical power curve indicates the expected false assessments for the site as a whole. The site-wide false positive rate is 6% and the test becomes sensitive to 4 standard deviation units over background. Increasing trends detected in the background data include sulfate at MW-16, sulfate at MW-17, sulfate at MW-1N, and zinc at MW-1N. Monitoring well LGW-14R was resampled on October 2, 2018 and analyzed for TDS and zinc. The resample TDS concentration at LGW-14R (230 mg/L) confirms the initial exceedance at LGW-14R. The resample zinc concentration at LGW-14R (<5 μg/L) does not confirm the initial exceedance, therefore it is not statistically significant. Monitoring well MW-15 was resampled on October 2, 2018 and analyzed for sulfate. The resample sulfate concentration at MW-15 (11.0 mg/L) confirms the initial exceedance at MW-15. Monitoring well MW-1N was resampled on October 3, 2018 and analyzed for zinc. The resample zinc concentration at MW-1N (47.0 μg/L) confirms the initial exceedance at MW-1N.

Summary of resample statistics.

Well Parameter Result CUSUM Value

Control limit

Control Limit Type

Verified/Awaiting Verification

TDS, mg/L 230 276.6753 256.1775 Normal Awaiting Verification LGW-14R Zinc, μg/L <5 -- 5.4000 Nonparametric Exceed not Verified

MW-15 Sulfate, mg/L 11.0 16.7220 13.5608 Normal Awaiting Verification MW-1N Zinc, μg/L 47.0 154.2612 144.0072 Normal Awaiting Verification

Page 11: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Ground Water Statistics for Eco-Vista Sanitary Landfill Third Quarter Monitoring Event In 2018

C:\Otter Creek Environmental\Arkansas\Eco-Vista\ecovistaq318RRRR.doc December 14, 2018

- 6 -

STATISTICAL METHODOLOGIES FOR ASSESSMENT MONITORING Wells currently in assessment monitoring for past statistical exceedances or verified VOC detections include LGW-5, LGW-6, LGW-7, LGW-9, LGW-10, MW-2N, MW-3N, MW-7N, MW-8N, and MW-21. Volatile Organic Compounds VOCs detected in the ground water at Eco Vista Sanitary Landfill during the third quarter monitoring event in 2018 are summarized in the table below. Acetone was detected at wells LGW-10, LGW-7, LGW-9, MW-21, MW-2N, MW-7N, and MW-8N, however acetone was also detected in the associated equipment blank and trip blank at similar concentrations. The current acetone detections are likely artifacts of the sampling or analyses. Historical detections are summarized in Attachment B.

VOCs detected at Eco Vista Sanitary Landfill during the third quarter monitoring event in 2018 Assessment Wells

Well VOC Detected Result, μg/L

Reporting Limit, μg/L

Verified/ Awaiting Verification GWPS, μg/L

1,1-Dichloroethane 1.6 1 Verified 2.4 1,4-Dichlorobenzene 3.7 1 Verified 75

Benzene 1.9 1 Verified 5 LGW-10

cis-1,2-Dichloroethene 1.7 1 Verified 70 MW-21 1,4-Dichlorobenzene 1.3 1 Verified 75

GWPS – Groundwater Protection Standard. Proposed in Document No. 65838 and approved in Document No. 65893. The current verified VOC detections were evaluated against the ground water protection standards (GWPS) using confidence limits (Attachment D). The 95% lower confidence limit (LCL) for the mean of the data was used to evaluate whether the regulated unit is in compliance with the approved ground-water protection standards (e.g. whether the verified constituent is detected at a significant level above the GWPS). An exceedance is verified if the LCL is above the Regulatory GWPS. The calculated LCLs for historically detected VOCs are below the respective GWPS. Trace Metals and Inorganic Compounds The current verified control limit/prediction limit exceedances and GWPS exceedances were evaluated against the approved GWPS using confidence limits (Attachment E). The 95% lower confidence limit (LCL) for the mean of the data was used to evaluate whether the regulated unit is in compliance with the groundwater protection standards (e.g. whether the verified constituent is detected at a significant level above the GWPS). An exceedance is verified if the LCL is above the GWPS. The 95% LCL for cobalt at LGW-10 (44.196 μg/L) exceeds the GWPS of 11 μg/L. The 95% LCL for cadmium at LGW-6 (57.541 μg/L) exceeds the GWPS of 5 μg/L. The 95% LCL for cadmium at LGW-7 (25.049 μg/L) exceeds the GWPS of 5 μg/L. The 95% LCL for cadmium at LGW-9 (34.045 μg/L) exceeds the GWPS of 5 μg/L. The 95% LCL for cobalt at MW-21 (14.467 μg/L) exceeds the GWPS of 11 μg/L.

Page 12: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Ground Water Statistics for Eco-Vista Sanitary Landfill Third Quarter Monitoring Event In 2018

C:\Otter Creek Environmental\Arkansas\Eco-Vista\ecovistaq318RRRR.doc December 14, 2018

- 7 -

The 95% LCL for cadmium at MW-3N (17.069 μg/L) exceeds the GWPS of 5 μg/L. The 95% LCL for cadmium at MW-8N (14.986 μg/L) exceeds the GWPS of 5 μg/L. The remainder of the calculated 95% LCLs are below the respective GWPS. CONCLUSIONS This document describes a comprehensive statistical plan designated for the Eco Vista Sanitary Landfill. The groundwater monitoring network for Eco Vista Sanitary Landfill includes wells MW-1N, MW-2N, MW-3N, MW-7N, MW-8N, MW-10N, MW-11N, MW-15, MW-16, MW-17, MW-19, MW-20, MW-21, LGW-2, LGW-3R, LGW-4, LGW-5, LGW-6, LGW-7, LGW-8R, LGW-9, LGW-10, and LGW-14R. These wells were sampled during July 10-17, 2018 and analyzed for the parameters required by permit. There are verified detections of 1,1-dichloroethane, 1,4-dichlorobenzene, benzene, and cis-1,2-dichloroethene at LGW-10, 1,4-dichlorobenzene at MW-21, and vinyl chloride at LGW-2. None of the VOCs exceeded GWPS. The trace metals and inorganic indicator data were statistically compared to background using control charts/prediction limits. For the most current data, there are verified statistical limit exceedances for TDS at LGW-14R, arsenic, iron, TDS, and TOC at LGW-2 and TDS at LGW-8R. Due to verified statistical limit exceedances, GWPS exceedances, and confirmed VOCs, select wells and parameters were evaluated using assessment statistics. The 95% LCL exceeded the GWPS for cobalt at LGW-10, cadmium at LGW-6, cadmium at LGW-7, cadmium at LGW-9, cobalt at MW-21, cadmium at MW-3N, and cadmium at MW-8N.

Page 13: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Ground Water Statistics for Eco-Vista Sanitary Landfill Third Quarter Monitoring Event In 2018

C:\Otter Creek Environmental\Arkansas\Eco-Vista\ecovistaq318RRRR.doc December 14, 2018

Attachment A

Ground Water Data obtained during the Third Quarter Monitoring Event in 2018

Page 14: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Analytical Data Summary for 7/10/2018 to 7/18/2018Constituents Units LGW-10 LGW-14R LGW-2 LGW-3R LGW-4 LGW-5 LGW-6 LGW-7 LGW-8R LGW-9 MW-10N

0,0,0-triethylphosphorothioate ug/L <48.0000 <51.0000 <49.0000 <50.0000 <50.0000 <50.0000 <49.0000 <51.0000 <49.0000 <47.0000 <48.00001,1,1,2-tetrachloroethane ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,1,1-trichloroethane ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,1,2,2-tetrachloroethane ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,1,2-trichloroethane ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,1-dichloroethane ug/L 1.6000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,1-dichloroethene ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,1-dichloropropene ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,2,3-trichloropropane ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,2,4,5-tetrachlorobenzene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.70001,2,4-trichlorobenzene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.70001,2-dibromo-3-chloropropane (dbcp) ug/L <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.00001,2-dibromoethane (edb) ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,2-dichlorobenzene ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,2-dichloroethane ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,2-dichloropropane ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,3-dichlorobenzene ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,3-dichloropropane ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,4-dichlorobenzene ug/L 3.7000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,4-naphthoquinone ug/L <48.0000 <51.0000 <49.0000 <50.0000 <50.0000 <50.0000 <49.0000 <51.0000 <49.0000 <47.0000 <48.00001-naphthylamine ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.70002,2'-oxybis(1-chloropropane) ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.70002,2-dichloropropane ug/L <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.00002,3,4,6-tetrachlorophenol ug/L <48.0000 <51.0000 <49.0000 <50.0000 <50.0000 <50.0000 <49.0000 <51.0000 <49.0000 <47.0000 <48.00002,4,5-t ug/L <.9600 <1.0000 <1.1000 <1.0000 <.9800 <1.0000 <1.0000 <.9500 <.9800 <.9600 <1.00002,4,5-tp (silvex) ug/L <.9600 <1.0000 <1.1000 <1.0000 <.9800 <1.0000 <1.0000 <.9500 <.9800 <.9600 <1.00002,4,5-trichlorophenol ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.70002,4,6-trichlorophenol ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.70002,4-d ug/L <3.8000 <4.1000 <4.4000 <4.1000 <3.9000 <4.1000 <4.0000 <3.8000 <3.9000 <3.8000 <4.00002,4-dichlorophenol ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.70002,4-dimethylphenol ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.70002,4-dinitrophenol ug/L <48.0000 <51.0000 <49.0000 <50.0000 <50.0000 <50.0000 <49.0000 <51.0000 <49.0000 <47.0000 <48.00002,4-dinitrotoluene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.70002,6-dichlorophenol ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.70002,6-dinitrotoluene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.70002-acetylaminofluorene ug/L <95.0000 <100.0000 <97.0000 <100.0000 <99.0000 <100.0000 <99.0000 <100.0000 <98.0000 <95.0000 <97.00002-chloronaphthalene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.70002-chlorophenol ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.70002-hexanone ug/L <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.00002-methylnaphthalene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.70002-naphthylamine ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.70002-nitroaniline ug/L <48.0000 <51.0000 <49.0000 <50.0000 <50.0000 <50.0000 <49.0000 <51.0000 <49.0000 <47.0000 <48.00002-nitrophenol ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.70003,3'-dichlorobenzidine ug/L <48.0000 <51.0000 <49.0000 <50.0000 <50.0000 <50.0000 <49.0000 <51.0000 <49.0000 <47.0000 <48.00003,3'-dimethylbenzidine ug/L <19.0000 <20.0000 <19.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <19.0000 <19.00003-chloropropene ug/L <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.00003-methylcholanthrene ug/L <19.0000 <20.0000 <19.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <19.0000 <19.00003-nitroaniline ug/L <48.0000 <51.0000 <49.0000 <50.0000 <50.0000 <50.0000 <49.0000 <51.0000 <49.0000 <47.0000 <48.00004,4'-ddd ug/L <.0480 <.0540 <.0500 <.0520 <.0500 <.0530 <.0530 <.0480 <.0480 <.0500 <.05104,4'-dde ug/L <.0480 <.0540 <.0500 <.0520 <.0500 <.0530 <.0530 <.0480 <.0480 <.0500 <.05104,4'-ddt ug/L <.0480 <.0540 <.0500 <.0520 <.0500 <.0530 <.0530 <.0480 <.0480 <.0500 <.05104-aminobiphenyl ug/L <48.0000 <51.0000 <49.0000 <50.0000 <50.0000 <50.0000 <49.0000 <51.0000 <49.0000 <47.0000 <48.00004-bromophenyl phenyl ether ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.70004-chloroaniline ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.70004-chlorophenyl phenyl ether ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 15: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Analytical Data Summary for 7/10/2018 to 7/18/2018Constituents MW-11N MW-15 MW-16 MW-17 MW-19 MW-1N MW-20 MW-21 MW-2N MW-3N MW-7N MW-8N

0,0,0-triethylphosphorothioate <50.0000 <51.0000 <48.0000 <47.0000 <48.0000 <49.0000 <47.0000 <48.0000 <51.0000 <47.0000 <52.0000 <49.00001,1,1,2-tetrachloroethane <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,1,1-trichloroethane <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,1,2,2-tetrachloroethane <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,1,2-trichloroethane <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,1-dichloroethane <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,1-dichloroethene <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,1-dichloropropene <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,2,3-trichloropropane <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,2,4,5-tetrachlorobenzene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.80001,2,4-trichlorobenzene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.80001,2-dibromo-3-chloropropane (dbcp) <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.00001,2-dibromoethane (edb) <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,2-dichlorobenzene <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,2-dichloroethane <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,2-dichloropropane <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,3-dichlorobenzene <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,3-dichloropropane <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.00001,4-dichlorobenzene <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 1.3000 <1.0000 <1.0000 <1.0000 <1.00001,4-naphthoquinone <50.0000 <51.0000 <48.0000 <47.0000 <48.0000 <49.0000 <47.0000 <48.0000 <51.0000 <47.0000 <52.0000 <49.00001-naphthylamine <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.80002,2'-oxybis(1-chloropropane) <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.80002,2-dichloropropane <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.00002,3,4,6-tetrachlorophenol <50.0000 <51.0000 <48.0000 <47.0000 <48.0000 <49.0000 <47.0000 <48.0000 <51.0000 <47.0000 <52.0000 <49.00002,4,5-t <1.0000 <1.0000 <1.0000 <.9500 <1.0000 <.9700 <.9600 <.9500 <1.0000 <.9500 <1.0000 <.95002,4,5-tp (silvex) <1.0000 <1.0000 <1.0000 <.9500 <1.0000 <.9700 <.9600 <.9500 <1.0000 <.9500 <1.0000 <.95002,4,5-trichlorophenol <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.80002,4,6-trichlorophenol <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.80002,4-d <4.0000 <4.1000 <4.2000 <3.8000 <4.1000 <3.9000 <3.8000 <3.8000 <4.1000 <3.8000 <4.1000 <3.80002,4-dichlorophenol <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.80002,4-dimethylphenol <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.80002,4-dinitrophenol <50.0000 <51.0000 <48.0000 <47.0000 <48.0000 <49.0000 <47.0000 <48.0000 <51.0000 <47.0000 <52.0000 <49.00002,4-dinitrotoluene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.80002,6-dichlorophenol <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.80002,6-dinitrotoluene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.80002-acetylaminofluorene <100.0000 <100.0000 <95.0000 <95.0000 <96.0000 <99.0000 <95.0000 <95.0000 <100.0000 <95.0000 <100.0000 <98.00002-chloronaphthalene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.80002-chlorophenol <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.80002-hexanone <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.00002-methylnaphthalene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.80002-naphthylamine <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.80002-nitroaniline <50.0000 <51.0000 <48.0000 <47.0000 <48.0000 <49.0000 <47.0000 <48.0000 <51.0000 <47.0000 <52.0000 <49.00002-nitrophenol <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.80003,3'-dichlorobenzidine <50.0000 <51.0000 <48.0000 <47.0000 <48.0000 <49.0000 <47.0000 <48.0000 <51.0000 <47.0000 <52.0000 <49.00003,3'-dimethylbenzidine <20.0000 <20.0000 <19.0000 <19.0000 <19.0000 <20.0000 <19.0000 <19.0000 <20.0000 <19.0000 <21.0000 <20.00003-chloropropene <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.00003-methylcholanthrene <20.0000 <20.0000 <19.0000 <19.0000 <19.0000 <20.0000 <19.0000 <19.0000 <20.0000 <19.0000 <21.0000 <20.00003-nitroaniline <50.0000 <51.0000 <48.0000 <47.0000 <48.0000 <49.0000 <47.0000 <48.0000 <51.0000 <47.0000 <52.0000 <49.00004,4'-ddd <.0520 <.0510 <.0490 <.0480 <.0510 <.0480 <.0490 <.0480 <.0490 <.0470 <.0480 <.04804,4'-dde <.0520 <.0510 <.0490 <.0480 <.0510 <.0480 <.0490 <.0480 <.0490 <.0470 <.0480 <.04804,4'-ddt <.0520 <.0510 <.0490 <.0480 <.0510 <.0480 <.0490 <.0480 <.0490 <.0470 <.0480 <.04804-aminobiphenyl <50.0000 <51.0000 <48.0000 <47.0000 <48.0000 <49.0000 <47.0000 <48.0000 <51.0000 <47.0000 <52.0000 <49.00004-bromophenyl phenyl ether <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.80004-chloroaniline <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.80004-chlorophenyl phenyl ether <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 16: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Analytical Data Summary for 7/10/2018 to 7/18/2018Constituents Units LGW-10 LGW-14R LGW-2 LGW-3R LGW-4 LGW-5 LGW-6 LGW-7 LGW-8R LGW-9 MW-10N

4-nitroaniline ug/L <48.0000 <51.0000 <49.0000 <50.0000 <50.0000 <50.0000 <49.0000 <51.0000 <49.0000 <47.0000 <48.00004-nitrophenol ug/L <48.0000 <51.0000 <49.0000 <50.0000 <50.0000 <50.0000 <49.0000 <51.0000 <49.0000 <47.0000 <48.00005-nitro-o-toluidine ug/L <19.0000 <20.0000 <19.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <19.0000 <19.00007,12-dimethylbenz(a)anthracene ug/L <19.0000 <20.0000 <19.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <19.0000 <19.0000Acenaphthene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Acenaphthylene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Acetone ug/L 6.9000 29.0000 17.0000 6.2000 <5.0000 <5.0000 <5.0000 7.6000 6.0000 7.7000 5.6000Acetonitrile ug/L <30.0000 <30.0000 <30.0000 <30.0000 <30.0000 <30.0000 <30.0000 <30.0000 <30.0000 <30.0000 <30.0000Acetophenone ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Acrolein ug/L <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000Acrylonitrile ug/L <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000Aldrin ug/L <.0480 <.0540 <.0500 <.0520 <.0500 <.0530 <.0530 <.0480 <.0480 <.0500 <.0510Alkalinity, bicarbonate (as caco3) mg/L 470.0000* 190.0000* 530.0000* 280.0000* 250.0000* 280.0000* 340.0000* 290.0000* 290.0000* 360.0000* 260.0000*Alkalinity, carbonate (as caco3) mg/L <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000Alpha-bhc ug/L <.0480 <.0540 <.0500 <.0520 <.0500 <.0530 <.0530 <.0480 <.0480 <.0500 <.0510Ammonia (as n) mg/L .2200 <.1000 .2200 <.1000 <.1000 <.1000 <.1000 <.1000 <.1000 <.1000 <.1000Anthracene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Antimony, total ug/L <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000Arsenic, total ug/L <5.0000 <5.0000 10.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000Barium, total ug/L 83.0000 30.0000 98.0000 47.0000 59.0000 71.0000 110.0000 26.0000 68.0000 180.0000 25.0000Benzene ug/L 1.9000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Benzo(a)anthracene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Benzo(a)pyrene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Benzo(b)fluoranthene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Benzo(ghi)perylene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Benzo(k)fluoranthene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Benzyl alcohol ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Beryllium, total ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Beta-bhc ug/L <.0480 <.0540 <.0500 <.0520 <.0500 <.0530 <.0530 <.0480 <.0480 <.0500 <.0510Bis(2-chloroethoxy) methane ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Bis(2-chloroethyl) ether ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Bis(2-ethylhexyl) phthalate ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Bromochloromethane ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Bromoform ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Bromomethane ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Butyl benzyl phthalate ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Cadmium, total ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 2.8000 55.0000 24.0000 <1.0000 42.0000 <1.0000Calcium, total mg/L 150.0000 74.0000 190.0000 100.0000 100.0000 110.0000 110.0000 93.0000 110.0000 110.0000 33.0000Carbon disulfide ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Carbon tetrachloride ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Chlordane ug/L <.4800 <.5400 <.5000 <.5200 <.5000 <.5300 <.5300 <.4800 <.4800 <.5000 <.5100Chloride mg/L 14.0000 4.2000 8.7000 18.0000 15.0000 15.0000 14.0000 14.0000 14.0000 66.0000 5.4000Chlorobenzene ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Chlorobenzilate ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Chloroethane ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Chloroform ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Chloromethane ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Chloroprene ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Chromium, total ug/L <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000Chrysene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Cis-1,2-dichloroethene ug/L 1.7000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Cis-1,3-dichloropropene ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Cobalt, total ug/L 65.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 5.9000 <3.0000Copper, total ug/L <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000Cresol, 4,6-dinitro-o- ug/L <48.0000 <51.0000 <49.0000 <50.0000 <50.0000 <50.0000 <49.0000 <51.0000 <49.0000 <47.0000 <48.0000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 17: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Analytical Data Summary for 7/10/2018 to 7/18/2018Constituents MW-11N MW-15 MW-16 MW-17 MW-19 MW-1N MW-20 MW-21 MW-2N MW-3N MW-7N MW-8N

4-nitroaniline <50.0000 <51.0000 <48.0000 <47.0000 <48.0000 <49.0000 <47.0000 <48.0000 <51.0000 <47.0000 <52.0000 <49.00004-nitrophenol <50.0000 <51.0000 <48.0000 <47.0000 <48.0000 <49.0000 <47.0000 <48.0000 <51.0000 <47.0000 <52.0000 <49.00005-nitro-o-toluidine <20.0000 <20.0000 <19.0000 <19.0000 <19.0000 <20.0000 <19.0000 <19.0000 <20.0000 <19.0000 <21.0000 <20.00007,12-dimethylbenz(a)anthracene <20.0000 <20.0000 <19.0000 <19.0000 <19.0000 <20.0000 <19.0000 <19.0000 <20.0000 <19.0000 <21.0000 <20.0000Acenaphthene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Acenaphthylene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Acetone 8.9000 <5.0000 <5.0000 <5.0000 <5.0000 26.0000 <5.0000 24.0000 39.0000 <5.0000 7.3000 6.8000Acetonitrile <30.0000 <30.0000 <30.0000 <30.0000 <30.0000 <30.0000 <30.0000 <30.0000 <30.0000 <30.0000 <30.0000 <30.0000Acetophenone <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Acrolein <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000Acrylonitrile <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000Aldrin <.0520 <.0510 <.0490 <.0480 <.0510 <.0480 <.0490 <.0480 <.0490 <.0470 <.0480 <.0480Alkalinity, bicarbonate (as caco3) 180.0000* 180.0000* 180.0000* 170.0000* 130.0000* 200.0000* 270.0000* 170.0000* 150.0000* 290.0000* 200.0000* 200.0000*Alkalinity, carbonate (as caco3) <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000Alpha-bhc <.0520 <.0510 <.0490 <.0480 <.0510 <.0480 <.0490 <.0480 <.0490 <.0470 <.0480 <.0480Ammonia (as n) <.1000 <.1000 <.1000 <.1000 <.1000 <.1000 <.1000 .3800 <.1000 <.1000 <.1000 <.1000Anthracene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Antimony, total <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000Arsenic, total <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000Barium, total 64.0000 21.0000 35.0000 53.0000 25.0000 40.0000 79.0000 280.0000 51.0000 120.0000 110.0000 180.0000Benzene <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Benzo(a)anthracene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Benzo(a)pyrene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Benzo(b)fluoranthene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Benzo(ghi)perylene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Benzo(k)fluoranthene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Benzyl alcohol <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Beryllium, total <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Beta-bhc <.0520 <.0510 <.0490 <.0480 <.0510 <.0480 <.0490 <.0480 <.0490 <.0470 <.0480 <.0480Bis(2-chloroethoxy) methane <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Bis(2-chloroethyl) ether <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Bis(2-ethylhexyl) phthalate <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Bromochloromethane <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Bromoform <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Bromomethane <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Butyl benzyl phthalate <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Cadmium, total <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 1.4000 <1.0000 25.0000 1.4000 16.0000Calcium, total 68.0000 73.0000 66.0000 65.0000 48.0000 72.0000 98.0000 42.0000 54.0000 110.0000 78.0000 63.0000Carbon disulfide <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Carbon tetrachloride <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Chlordane <.5200 <.5100 <.4900 <.4800 <.5100 <.4800 <.4900 <.4800 <.4900 <.4700 <.4800 <.4800Chloride <3.0000 51.0000 5.3000 32.0000 12.0000 3.8000 4.7000 21.0000 7.6000 4.5000 43.0000 43.0000Chlorobenzene <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Chlorobenzilate <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Chloroethane <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Chloroform <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Chloromethane <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Chloroprene <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Chromium, total <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000Chrysene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Cis-1,2-dichloroethene <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Cis-1,3-dichloropropene <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Cobalt, total <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 21.0000 <3.0000 <3.0000 <3.0000 <3.0000Copper, total <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000Cresol, 4,6-dinitro-o- <50.0000 <51.0000 <48.0000 <47.0000 <48.0000 <49.0000 <47.0000 <48.0000 <51.0000 <47.0000 <52.0000 <49.0000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 18: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Analytical Data Summary for 7/10/2018 to 7/18/2018Constituents Units LGW-10 LGW-14R LGW-2 LGW-3R LGW-4 LGW-5 LGW-6 LGW-7 LGW-8R LGW-9 MW-10N

Cresol, o- ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Cresol, p-chloro-m- ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Cyanide, total mg/L <.0100 <.0100 <.0100 <.0100 <.0100 <.0100 <.0100 <.0100 <.0100 <.0100 <.0100Delta-bhc ug/L <.0480 <.0540 <.0500 <.0520 <.0500 <.0530 <.0530 <.0480 <.0480 <.0500 <.0510Di-n-butyl phthalate ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Di-n-octyl phthalate ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Diallate ug/L <19.0000 <20.0000 <19.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <19.0000 <19.0000Dibenzo(a,h)anthracene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Dibenzofuran ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Dibromochloromethane ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Dibromomethane ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Dichlorobromomethane ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Dichlorodifluoromethane ug/L <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000Dieldrin ug/L <.0480 <.0540 <.0500 <.0520 <.0500 <.0530 <.0530 <.0480 <.0480 <.0500 <.0510Diethyl phthalate ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Dimethoate ug/L <19.0000 <20.0000 <19.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <19.0000 <19.0000Dimethyl phthalate ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Dinoseb ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Diphenylamine ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Disulfoton ug/L <48.0000 <51.0000 <49.0000 <50.0000 <50.0000 <50.0000 <49.0000 <51.0000 <49.0000 <47.0000 <48.0000Do (field) mg/L .9700 5.0000 .9400 3.9500 3.0800 .5900 3.5700 1.6400 .5000 .3900 .6600Endosulfan i ug/L <.0480 <.0540 <.0500 <.0520 <.0500 <.0530 <.0530 <.0480 <.0480 <.0500 <.0510Endosulfan ii ug/L <.0480 <.0540 <.0500 <.0520 <.0500 <.0530 <.0530 <.0480 <.0480 <.0500 <.0510Endosulfan sulfate ug/L <.0480 <.0540 <.0500 <.0520 <.0500 <.0530 <.0530 <.0480 <.0480 <.0500 <.0510Endrin ug/L <.0480 <.0540 <.0500 <.0520 <.0500 <.0530 <.0530 <.0480 <.0480 <.0500 <.0510Endrin aldehyde ug/L <.0480 <.0540 <.0500 <.0520 <.0500 <.0530 <.0530 <.0480 <.0480 <.0500 <.0510Ethyl methacrylate ug/L <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000Ethyl methane sulfonate ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Ethylbenzene ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Famphur ug/L <190.0000 <200.0000 <190.0000 <200.0000 <200.0000 <200.0000 <200.0000 <200.0000 <200.0000 <190.0000 <190.0000Fluoranthene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Fluorene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Gamma-bhc (lindane) ug/L <.0480 <.0540 <.0500 <.0520 <.0500 <.0530 <.0530 <.0480 <.0480 <.0500 <.0510Heptachlor ug/L <.0480 <.0540 <.0500 <.0520 <.0500 <.0530 <.0530 <.0480 <.0480 <.0500 <.0510Heptachlor epoxide ug/L <.0480 <.0540 <.0500 <.0520 <.0500 <.0530 <.0530 <.0480 <.0480 <.0500 <.0510Hexachlorobenzene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Hexachlorobutadiene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Hexachlorocyclopentadiene ug/L <48.0000 <51.0000 <49.0000 <50.0000 <50.0000 <50.0000 <49.0000 <51.0000 <49.0000 <47.0000 <48.0000Hexachloroethane ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Hexachloropropene ug/L <95.0000 <100.0000 <97.0000 <100.0000 <99.0000 <100.0000 <99.0000 <100.0000 <98.0000 <95.0000 <97.0000Indeno(1,2,3-cd)pyrene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Iodomethane ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Iron, total ug/L 7600.0000 <60.0000 17000.0000 <60.0000 <60.0000 <60.0000 <60.0000 <60.0000 <60.0000 <60.0000 240.0000Isobutanol ug/L <110.0000 <110.0000 <110.0000 <110.0000 <110.0000 <110.0000 <110.0000 <110.0000 <110.0000 <110.0000 <110.0000Isodrin ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Isophorone ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Isosafrole ug/L <19.0000 <20.0000 <19.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <19.0000 <19.0000Kepone ug/L <.9600 <1.1000 <1.0000 <1.0000 <.9900 <1.1000 <1.1000 <.9600 <.9600 <1.0000 <1.0000Lead, total ug/L <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000M-dinitrobenzene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Magnesium, total mg/L 3.0000 .8900 1.8000 2.1000 2.0000 2.5000 3.4000 3.4000 2.4000 9.1000 11.0000Manganese, total ug/L 6900.0000 <3.0000 200.0000 <3.0000 38.0000 1100.0000 18000.0000 14000.0000 <3.0000 11000.0000 25.0000Mercury, total ug/L <.3300 <.3300 <.3300 <.3300 <.3300 <.3300 <.3300 <.3300 <.3300 <.3300 <.3300Meta + para-cresol ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Methacrylonitrile ug/L <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 19: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Analytical Data Summary for 7/10/2018 to 7/18/2018Constituents MW-11N MW-15 MW-16 MW-17 MW-19 MW-1N MW-20 MW-21 MW-2N MW-3N MW-7N MW-8N

Cresol, o- <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Cresol, p-chloro-m- <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Cyanide, total <.0100 <.0100 <.0100 <.0100 <.0100 <.0100 <.0100 <.0200 <.0100 <.0100 <.0100 <.0100Delta-bhc <.0520 <.0510 <.0490 <.0480 <.0510 <.0480 <.0490 <.0480 <.0490 <.0470 <.0480 <.0480Di-n-butyl phthalate <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Di-n-octyl phthalate <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Diallate <20.0000 <20.0000 <19.0000 <19.0000 <19.0000 <20.0000 <19.0000 <19.0000 <20.0000 <19.0000 <21.0000 <20.0000Dibenzo(a,h)anthracene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Dibenzofuran <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Dibromochloromethane <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Dibromomethane <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Dichlorobromomethane <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Dichlorodifluoromethane <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000 <2.0000Dieldrin <.0520 <.0510 <.0490 <.0480 <.0510 <.0480 <.0490 <.0480 <.0490 <.0470 <.0480 <.0480Diethyl phthalate <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Dimethoate <20.0000 <20.0000 <19.0000 <19.0000 <19.0000 <20.0000 <19.0000 <19.0000 <20.0000 <19.0000 <21.0000 <20.0000Dimethyl phthalate <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Dinoseb <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Diphenylamine <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Disulfoton <50.0000 <51.0000 <48.0000 <47.0000 <48.0000 <49.0000 <47.0000 <48.0000 <51.0000 <47.0000 <52.0000 <49.0000Do (field) 4.3100 2.6800 3.0300 3.2700 5.6700 1.7100 1.2400 .1300 5.3000 .2400 2.2400 .4200Endosulfan i <.0520 <.0510 <.0490 <.0480 <.0510 <.0480 <.0490 <.0480 <.0490 <.0470 <.0480 <.0480Endosulfan ii <.0520 <.0510 <.0490 <.0480 <.0510 <.0480 <.0490 <.0480 <.0490 <.0470 <.0480 <.0480Endosulfan sulfate <.0520 <.0510 <.0490 <.0480 <.0510 <.0480 <.0490 <.0480 <.0490 <.0470 <.0480 <.0480Endrin <.0520 <.0510 <.0490 <.0480 <.0510 <.0480 <.0490 <.0480 <.0490 <.0470 <.0480 <.0480Endrin aldehyde <.0520 <.0510 <.0490 <.0480 <.0510 <.0480 <.0490 <.0480 <.0490 <.0470 <.0480 <.0480Ethyl methacrylate <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000Ethyl methane sulfonate <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Ethylbenzene <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Famphur <200.0000 <200.0000 <190.0000 <190.0000 <190.0000 <200.0000 <190.0000 <190.0000 <200.0000 <190.0000 <210.0000 <200.0000Fluoranthene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Fluorene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Gamma-bhc (lindane) <.0520 <.0510 <.0490 <.0480 <.0510 <.0480 <.0490 <.0480 <.0490 <.0470 <.0480 <.0480Heptachlor <.0520 <.0510 <.0490 <.0480 <.0510 <.0480 <.0490 <.0480 <.0490 <.0470 <.0480 <.0480Heptachlor epoxide <.0520 <.0510 <.0490 <.0480 <.0510 <.0480 <.0490 <.0480 <.0490 <.0470 <.0480 <.0480Hexachlorobenzene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Hexachlorobutadiene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Hexachlorocyclopentadiene <50.0000 <51.0000 <48.0000 <47.0000 <48.0000 <49.0000 <47.0000 <48.0000 <51.0000 <47.0000 <52.0000 <49.0000Hexachloroethane <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Hexachloropropene <100.0000 <100.0000 <95.0000 <95.0000 <96.0000 <99.0000 <95.0000 <95.0000 <100.0000 <95.0000 <100.0000 <98.0000Indeno(1,2,3-cd)pyrene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Iodomethane <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Iron, total <60.0000 <60.0000 <60.0000 <60.0000 <60.0000 <60.0000 <60.0000 7600.0000 <60.0000 <60.0000 320.0000 <60.0000Isobutanol <110.0000 <110.0000 <110.0000 <110.0000 <110.0000 <110.0000 <110.0000 <110.0000 <110.0000 <110.0000 <110.0000 <110.0000Isodrin <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Isophorone <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Isosafrole <20.0000 <20.0000 <19.0000 <19.0000 <19.0000 <20.0000 <19.0000 <19.0000 <20.0000 <19.0000 <21.0000 <20.0000Kepone <1.0000 <1.0000 <.9800 <.9600 <1.0000 <.9500 <.9900 <.9600 <.9700 <.9500 <.9500 <.9500Lead, total <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000M-dinitrobenzene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Magnesium, total .6600 2.1000 1.4000 2.5000 1.5000 3.0000 2.3000 8.7000 .8000 3.6000 5.7000 7.0000Manganese, total <3.0000 <3.0000 <3.0000 <3.0000 4.6000 <3.0000 56.0000 13000.0000 <3.0000 1500.0000 1200.0000 6800.0000Mercury, total <.3300 <.3300 <.3300 <.3300 <.3300 <.3300 <.3300 <.3300 <.3300 <.3300 <.3300 <.3300Meta + para-cresol <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Methacrylonitrile <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 20: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Analytical Data Summary for 7/10/2018 to 7/18/2018Constituents Units LGW-10 LGW-14R LGW-2 LGW-3R LGW-4 LGW-5 LGW-6 LGW-7 LGW-8R LGW-9 MW-10N

Methapyrilene ug/L <48.0000 <51.0000 <49.0000 <50.0000 <50.0000 <50.0000 <49.0000 <51.0000 <49.0000 <47.0000 <48.0000Methoxychlor ug/L <.0960 <.1100 <.1000 <.1000 <.0990 <.1100 <.1100 <.0960 <.0960 <.1000 <.1000Methyl ethyl ketone ug/L <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000Methyl isobutyl ketone ug/L <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000Methyl methacrylate ug/L <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000Methyl methanesulfonate ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Methyl parathion ug/L <48.0000 <51.0000 <49.0000 <50.0000 <50.0000 <50.0000 <49.0000 <51.0000 <49.0000 <47.0000 <48.0000Methylene chloride ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000N-nitroso-di-n-propylamine ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000N-nitrosodi-n-butylamine ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000N-nitrosodiethylamine ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000N-nitrosodimethylamine ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000N-nitrosodiphenylamine ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000N-nitrosomethylethylamine ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000N-nitrosopiperidine ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000N-nitrosopyrrolidine ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Naphthalene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Nickel, total ug/L 180.0000 <4.0000 <4.0000 <4.0000 <4.0000 12.0000 140.0000 70.0000 <4.0000 53.0000 <4.0000Nitrobenzene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000O-toluidine ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000P-dimethylaminoazobenzene ug/L <19.0000 <20.0000 <19.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <19.0000 <19.0000P-phenylenediamine ug/L <95.0000 <100.0000 <97.0000 <100.0000 <99.0000 <100.0000 <99.0000 <100.0000 <98.0000 <95.0000 <97.0000Parathion ug/L <48.0000 <51.0000 <49.0000 <50.0000 <50.0000 <50.0000 <49.0000 <51.0000 <49.0000 <47.0000 <48.0000Pcb 1016 ug/L <.9600 <1.1000 <1.0000 <1.0000 <.9900 <1.1000 <1.1000 <.9600 <.9600 <1.0000 <1.0000Pcb 1221 ug/L <.9600 <1.1000 <1.0000 <1.0000 <.9900 <1.1000 <1.1000 <.9600 <.9600 <1.0000 <1.0000Pcb 1232 ug/L <.9600 <1.1000 <1.0000 <1.0000 <.9900 <1.1000 <1.1000 <.9600 <.9600 <1.0000 <1.0000Pcb 1242 ug/L <.9600 <1.1000 <1.0000 <1.0000 <.9900 <1.1000 <1.1000 <.9600 <.9600 <1.0000 <1.0000Pcb 1248 ug/L <.9600 <1.1000 <1.0000 <1.0000 <.9900 <1.1000 <1.1000 <.9600 <.9600 <1.0000 <1.0000Pcb 1254 ug/L <.9600 <1.1000 <1.0000 <1.0000 <.9900 <1.1000 <1.1000 <.9600 <.9600 <1.0000 <1.0000Pcb 1260 ug/L <.9600 <1.1000 <1.0000 <1.0000 <.9900 <1.1000 <1.1000 <.9600 <.9600 <1.0000 <1.0000Pentachlorobenzene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Pentachloronitrobenzene ug/L <48.0000 <51.0000 <49.0000 <50.0000 <50.0000 <50.0000 <49.0000 <51.0000 <49.0000 <47.0000 <48.0000Pentachlorophenol ug/L <48.0000 <51.0000 <49.0000 <50.0000 <50.0000 <50.0000 <49.0000 <51.0000 <49.0000 <47.0000 <48.0000pH (Field) S.U. 6.6000 7.4000 6.5100 6.6500 6.5100 6.2300 6.5700 6.6500 6.5200 6.4400 7.4000Phenacetin ug/L <19.0000 <20.0000 <19.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <19.0000 <19.0000Phenanthrene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Phenol ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Phorate ug/L <48.0000 <51.0000 <49.0000 <50.0000 <50.0000 <50.0000 <49.0000 <51.0000 <49.0000 <47.0000 <48.0000Potassium, total mg/L <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000Pronamide ug/L <19.0000 <20.0000 <19.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <19.0000 <19.0000Propionitrile ug/L <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000Pyrene ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Safrole ug/L <48.0000 <51.0000 <49.0000 <50.0000 <50.0000 <50.0000 <49.0000 <51.0000 <49.0000 <47.0000 <48.0000Selenium, total ug/L <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <20.0000 <10.0000 <10.0000 <10.0000 <10.0000Silver, total ug/L <50.0000 <50.0000 <50.0000 <50.0000 <50.0000 <50.0000 <50.0000 <50.0000 <50.0000 <50.0000 <50.0000Sodium, total mg/L 7.9000 16.0000 12.0000 15.0000 12.0000 12.0000 9.5000 7.8000 8.4000 54.0000 56.0000Specific conductance (field) umhos/cm 911.0000 394.0000 943.0000 559.0000 572.9000 604.0000 631.0000 554.0000 612.0000 861.0000 441.4000Styrene ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Sulfate mg/L <5.0000 <5.0000 <5.0000 5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 23.0000 <5.0000Sulfide mg/L <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000Sym-trinitrobenzene ug/L <48.0000 <51.0000 <49.0000 <50.0000 <50.0000 <50.0000 <49.0000 <51.0000 <49.0000 <47.0000 <48.0000Tetrachloroethene ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Thallium, total ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Thionazin ug/L <9.5000 <10.0000 <9.7000 <10.0000 <9.9000 <10.0000 <9.9000 <10.0000 <9.8000 <9.5000 <9.7000Tin, total ug/L <100.0000 <100.0000 <100.0000 <100.0000 <100.0000 <100.0000 <100.0000 <100.0000 <100.0000 <100.0000 <100.0000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 21: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Analytical Data Summary for 7/10/2018 to 7/18/2018Constituents MW-11N MW-15 MW-16 MW-17 MW-19 MW-1N MW-20 MW-21 MW-2N MW-3N MW-7N MW-8N

Methapyrilene <50.0000 <51.0000 <48.0000 <47.0000 <48.0000 <49.0000 <47.0000 <48.0000 <51.0000 <47.0000 <52.0000 <49.0000Methoxychlor <.1000 <.1000 <.0980 <.0960 <.1000 <.0950 <.0990 <.0960 <.0970 <.0950 <.0950 <.0950Methyl ethyl ketone <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000Methyl isobutyl ketone <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000Methyl methacrylate <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000Methyl methanesulfonate <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Methyl parathion <50.0000 <51.0000 <48.0000 <47.0000 <48.0000 <49.0000 <47.0000 <48.0000 <51.0000 <47.0000 <52.0000 <49.0000Methylene chloride <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000N-nitroso-di-n-propylamine <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000N-nitrosodi-n-butylamine <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000N-nitrosodiethylamine <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000N-nitrosodimethylamine <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000N-nitrosodiphenylamine <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000N-nitrosomethylethylamine <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000N-nitrosopiperidine <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000N-nitrosopyrrolidine <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Naphthalene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Nickel, total <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 4.7000 <4.0000 53.0000 <4.0000 37.0000 9.5000 44.0000Nitrobenzene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000O-toluidine <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000P-dimethylaminoazobenzene <20.0000 <20.0000 <19.0000 <19.0000 <19.0000 <20.0000 <19.0000 <19.0000 <20.0000 <19.0000 <21.0000 <20.0000P-phenylenediamine <100.0000 <100.0000 <95.0000 <95.0000 <96.0000 <99.0000 <95.0000 <95.0000 <100.0000 <95.0000 <100.0000 <98.0000Parathion <50.0000 <51.0000 <48.0000 <47.0000 <48.0000 <49.0000 <47.0000 <48.0000 <51.0000 <47.0000 <52.0000 <49.0000Pcb 1016 <1.0000 <1.0000 <.9800 <.9600 <1.0000 <.9500 <.9900 <.9600 <.9700 <.9500 <.9500 <.9500Pcb 1221 <1.0000 <1.0000 <.9800 <.9600 <1.0000 <.9500 <.9900 <.9600 <.9700 <.9500 <.9500 <.9500Pcb 1232 <1.0000 <1.0000 <.9800 <.9600 <1.0000 <.9500 <.9900 <.9600 <.9700 <.9500 <.9500 <.9500Pcb 1242 <1.0000 <1.0000 <.9800 <.9600 <1.0000 <.9500 <.9900 <.9600 <.9700 <.9500 <.9500 <.9500Pcb 1248 <1.0000 <1.0000 <.9800 <.9600 <1.0000 <.9500 <.9900 <.9600 <.9700 <.9500 <.9500 <.9500Pcb 1254 <1.0000 <1.0000 <.9800 <.9600 <1.0000 <.9500 <.9900 <.9600 <.9700 <.9500 <.9500 <.9500Pcb 1260 <1.0000 <1.0000 <.9800 <.9600 <1.0000 <.9500 <.9900 <.9600 <.9700 <.9500 <.9500 <.9500Pentachlorobenzene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Pentachloronitrobenzene <50.0000 <51.0000 <48.0000 <47.0000 <48.0000 <49.0000 <47.0000 <48.0000 <51.0000 <47.0000 <52.0000 <49.0000Pentachlorophenol <50.0000 <51.0000 <48.0000 <47.0000 <48.0000 <49.0000 <47.0000 <48.0000 <51.0000 <47.0000 <52.0000 <49.0000pH (Field) 7.3700 6.9300 7.4500 6.9500 7.7800 7.2700 6.7700 6.5000 7.4800 6.4700 6.4500 6.7300Phenacetin <20.0000 <20.0000 <19.0000 <19.0000 <19.0000 <20.0000 <19.0000 <19.0000 <20.0000 <19.0000 <21.0000 <20.0000Phenanthrene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Phenol <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Phorate <50.0000 <51.0000 <48.0000 <47.0000 <48.0000 <49.0000 <47.0000 <48.0000 <51.0000 <47.0000 <52.0000 <49.0000Potassium, total <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000Pronamide <20.0000 <20.0000 <19.0000 <19.0000 <19.0000 <20.0000 <19.0000 <19.0000 <20.0000 <19.0000 <21.0000 <20.0000Propionitrile <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000 <20.0000Pyrene <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Safrole <50.0000 <51.0000 <48.0000 <47.0000 <48.0000 <49.0000 <47.0000 <48.0000 <51.0000 <47.0000 <52.0000 <49.0000Selenium, total <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000 <10.0000Silver, total <50.0000 <50.0000 <50.0000 <50.0000 <50.0000 <50.0000 <50.0000 <50.0000 <50.0000 <50.0000 <50.0000 <50.0000Sodium, total <5.0000 38.0000 7.5000 27.0000 6.4000 5.5000 9.2000 12.0000 8.5000 <5.0000 22.0000 35.0000Specific conductance (field) 342.0000 556.0000 361.0000 471.0000 291.0000 371.3000 506.1000 389.1000 321.4000 525.2000 500.0000 576.0000Styrene <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Sulfate <5.0000 12.0000 9.5000 15.0000 <5.0000 6.5000 <5.0000 24.0000 <5.0000 9.8000 16.0000 30.0000Sulfide <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000 <4.0000Sym-trinitrobenzene <50.0000 <51.0000 <48.0000 <47.0000 <48.0000 <49.0000 <47.0000 <48.0000 <51.0000 <47.0000 <52.0000 <49.0000Tetrachloroethene <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Thallium, total <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Thionazin <10.0000 <10.0000 <9.5000 <9.5000 <9.6000 <9.9000 <9.5000 <9.5000 <10.0000 <9.5000 <10.0000 <9.8000Tin, total <100.0000 <100.0000 <100.0000 <100.0000 <100.0000 <100.0000 <100.0000 <100.0000 <100.0000 <100.0000 <100.0000 <100.0000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 22: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Analytical Data Summary for 7/10/2018 to 7/18/2018Constituents Units LGW-10 LGW-14R LGW-2 LGW-3R LGW-4 LGW-5 LGW-6 LGW-7 LGW-8R LGW-9 MW-10N

Toluene ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Total dissolved solids mg/L 500.0000 230.0000 560.0000 350.0000 330.0000 350.0000 380.0000 350.0000 350.0000 520.0000 280.0000Total organic carbon (toc) mg/L 1.0000* <1.0000* 1.7000* <1.0000* <1.0000* <1.0000* <1.0000* <1.0000* <1.0000* 2.3000* 4.6000*Total xylenes ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Toxaphene ug/L <4.8000 <5.4000 <5.0000 <5.2000 <5.0000 <5.3000 <5.3000 <4.8000 <4.8000 <5.0000 <5.1000Trans-1,2-dichloroethene ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Trans-1,3-dichloropropene ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Trans-1,4-dichloro-2-butene ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Trichloroethene ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Trichlorofluoromethane ug/L <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Turbidity (field) NTU .8300 .8200 1.6700 .0900 <.0100 1.1600 .4500 9.3900 <.0100 <.0100 .0100Vanadium, total ug/L <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000Vinyl acetate ug/L <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000Vinyl chloride ug/L <1.0000 <1.0000 1.7000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Water temperature in deg. celsius (field) C 32.7000 27.8700 31.1000 17.4000 17.0000 17.9000 18.5100 22.8000 16.4000 19.8000 22.4000Zinc, total ug/L 41.0000 60.0000 <5.0000 9.0000 6.6000 21.0000 250.0000 310.0000 <5.0000 160.0000 <5.0000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

* - The displayed value is the arithmetic mean of multiple database matches.

Page 23: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Analytical Data Summary for 7/10/2018 to 7/18/2018Constituents MW-11N MW-15 MW-16 MW-17 MW-19 MW-1N MW-20 MW-21 MW-2N MW-3N MW-7N MW-8N

Toluene <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Total dissolved solids 190.0000 320.0000 220.0000 270.0000 220.0000 220.0000 310.0000 240.0000 200.0000 330.0000 310.0000 330.0000Total organic carbon (toc) <1.0000* <1.0000* <1.0000* 1.1200* <1.0000* <1.0000* <1.0000* 2.0000* <1.0000* <1.0000* 1.3000* 1.9000*Total xylenes <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Toxaphene <5.2000 <5.1000 <4.9000 <4.8000 <5.1000 <4.8000 <4.9000 <4.8000 <4.9000 <4.7000 <4.8000 <4.8000Trans-1,2-dichloroethene <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Trans-1,3-dichloropropene <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Trans-1,4-dichloro-2-butene <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Trichloroethene <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Trichlorofluoromethane <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Turbidity (field) .6900 .2700 .4100 .5700 3.8900 .4100 2.7500 2.5100 <.0100 .3200 6.4400 .2400Vanadium, total <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000 <3.0000Vinyl acetate <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000 <5.0000Vinyl chloride <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000 <1.0000Water temperature in deg. celsius (field) 25.3100 16.4000 26.7000 18.1000 25.0000 29.8000 18.3000 17.5000 25.0000 17.9000 21.9000 26.2000Zinc, total 15.0000 <5.0000 <5.0000 <5.0000 <5.0000 47.0000 <5.0000 72.0000 6.6000 140.0000 40.0000 25.0000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

* - The displayed value is the arithmetic mean of multiple database matches.

Page 24: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Ground Water Statistics for Eco-Vista Sanitary Landfill Third Quarter Monitoring Event In 2018

C:\Otter Creek Environmental\Arkansas\Eco-Vista\ecovistaq318RRRR.doc December 14, 2018

Attachment B

Historical VOC Detections

Page 25: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Historical Volatile Organic Compound DetectionsConstituent Units Well Date Result Limit

1,1-dichloroethane ug/L LGW-10 1/26/2006 1.8000 1.00001,1-dichloroethane ug/L LGW-10 8/01/2006 2.4000 1.00001,1-dichloroethane ug/L LGW-10 8/01/2006 2.4000 1.00001,1-dichloroethane ug/L LGW-10 10/26/2006 1.3000 1.00001,1-dichloroethane ug/L LGW-10 1/25/2007 1.8000 1.00001,1-dichloroethane ug/L LGW-10 4/26/2007 1.3000 1.00001,1-dichloroethane ug/L LGW-10 7/12/2007 1.1000 1.00001,1-dichloroethane ug/L LGW-10 1/23/2008 1.5000 1.00001,1-dichloroethane ug/L LGW-10 7/22/2008 1.6000 1.00001,1-dichloroethane ug/L LGW-10 7/29/2009 1.4000 1.00001,1-dichloroethane ug/L LGW-10 2/03/2010 1.2000 1.00001,1-dichloroethane ug/L LGW-10 2/03/2010 1.2000 1.00001,1-dichloroethane ug/L LGW-10 7/16/2010 2.2000 1.00001,1-dichloroethane ug/L LGW-10 1/19/2011 1.2000 1.00001,1-dichloroethane ug/L LGW-10 7/12/2011 2.2000 1.00001,1-dichloroethane ug/L LGW-10 1/05/2012 1.7000 1.00001,1-dichloroethane ug/L LGW-10 7/09/2012 1.7000 1.00001,1-dichloroethane ug/L LGW-10 5/01/2013 2.0000 1.00001,1-dichloroethane ug/L LGW-10 1/30/2014 1.8000 1.00001,1-dichloroethane ug/L LGW-10 7/09/2014 1.8000 1.00001,1-dichloroethane ug/L LGW-10 2/12/2015 1.9000 1.00001,1-dichloroethane ug/L LGW-10 7/13/2015 2.2000 1.00001,1-dichloroethane ug/L LGW-10 1/05/2016 2.1000 1.00001,1-dichloroethane ug/L LGW-10 2/10/2016 1.8000 1.00001,1-dichloroethane ug/L LGW-10 4/06/2016 1.7000 1.00001,1-dichloroethane ug/L LGW-10 7/21/2016 2.1000 1.00001,1-dichloroethane ug/L LGW-10 10/06/2016 2.0000 1.00001,1-dichloroethane ug/L LGW-10 1/11/2017 1.3000 1.00001,1-dichloroethane ug/L LGW-10 4/04/2017 2.1000 1.00001,1-dichloroethane ug/L LGW-10 7/19/2017 2.2000 1.00001,1-dichloroethane ug/L LGW-10 10/09/2017 2.1000 1.00001,1-dichloroethane ug/L LGW-10 1/24/2018 1.2000 1.00001,1-dichloroethane ug/L LGW-10 4/11/2018 1.7000 1.00001,1-dichloroethane ug/L LGW-10 7/16/2018 1.6000 1.00001,4-dichlorobenzene ug/L LGW-10 1/26/2006 2.2000 1.00001,4-dichlorobenzene ug/L LGW-10 8/01/2006 4.1000 1.00001,4-dichlorobenzene ug/L LGW-10 8/01/2006 4.1000 1.00001,4-dichlorobenzene ug/L LGW-10 10/26/2006 3.0000 1.00001,4-dichlorobenzene ug/L LGW-10 1/25/2007 4.1000 1.00001,4-dichlorobenzene ug/L LGW-10 4/26/2007 4.0000 1.00001,4-dichlorobenzene ug/L LGW-10 7/12/2007 3.5000 1.00001,4-dichlorobenzene ug/L LGW-10 1/23/2008 3.5000 1.00001,4-dichlorobenzene ug/L LGW-10 7/22/2008 2.8000 1.00001,4-dichlorobenzene ug/L LGW-10 7/29/2009 3.5000 1.00001,4-dichlorobenzene ug/L LGW-10 2/03/2010 3.9000 1.00001,4-dichlorobenzene ug/L LGW-10 2/03/2010 3.9000 1.00001,4-dichlorobenzene ug/L LGW-10 7/16/2010 5.4000 1.00001,4-dichlorobenzene ug/L LGW-10 1/19/2011 4.6000 1.00001,4-dichlorobenzene ug/L LGW-10 7/12/2011 6.6000 1.00001,4-dichlorobenzene ug/L LGW-10 1/05/2012 5.3000 1.00001,4-dichlorobenzene ug/L LGW-10 7/09/2012 5.1000 1.00001,4-dichlorobenzene ug/L LGW-10 5/01/2013 6.5000 1.00001,4-dichlorobenzene ug/L LGW-10 1/30/2014 6.4000 1.00001,4-dichlorobenzene ug/L LGW-10 7/09/2014 6.1000 1.00001,4-dichlorobenzene ug/L LGW-10 2/12/2015 7.2000 1.00001,4-dichlorobenzene ug/L LGW-10 7/13/2015 7.6000 1.00001,4-dichlorobenzene ug/L LGW-10 1/05/2016 6.9000 1.00001,4-dichlorobenzene ug/L LGW-10 2/10/2016 6.5000 1.00001,4-dichlorobenzene ug/L LGW-10 4/06/2016 6.3000 1.00001,4-dichlorobenzene ug/L LGW-10 7/21/2016 7.4000 1.00001,4-dichlorobenzene ug/L LGW-10 10/06/2016 6.9000 1.00001,4-dichlorobenzene ug/L LGW-10 1/11/2017 5.6000 1.00001,4-dichlorobenzene ug/L LGW-10 4/04/2017 7.5000 1.00001,4-dichlorobenzene ug/L LGW-10 7/19/2017 7.1000 1.00001,4-dichlorobenzene ug/L LGW-10 10/09/2017 7.0000 1.00001,4-dichlorobenzene ug/L LGW-10 1/24/2018 2.0000 1.00001,4-dichlorobenzene ug/L LGW-10 4/11/2018 2.5000 1.00001,4-dichlorobenzene ug/L LGW-10 7/16/2018 3.7000 1.0000Acetone ug/L LGW-10 1/30/2014 7.5000 5.0000Acetone ug/L LGW-10 7/09/2014 6.3000 5.0000Acetone ug/L LGW-10 7/13/2015 5.4000 5.0000Acetone ug/L LGW-10 7/21/2016 9.8000 5.0000Acetone ug/L LGW-10 1/11/2017 5.3000 5.0000Acetone ug/L LGW-10 4/04/2017 8.0000 5.0000Acetone ug/L LGW-10 10/09/2017 5.1000 5.0000Acetone ug/L LGW-10 1/24/2018 9.2000 5.0000Acetone ug/L LGW-10 4/11/2018 28.0000 5.0000Acetone ug/L LGW-10 7/16/2018 6.9000 5.0000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 26: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Historical Volatile Organic Compound DetectionsConstituent Units Well Date Result Limit

Benzene ug/L LGW-10 1/26/2006 1.3000 1.0000Benzene ug/L LGW-10 8/01/2006 1.8000 1.0000Benzene ug/L LGW-10 8/01/2006 1.8000 1.0000Benzene ug/L LGW-10 10/26/2006 1.3000 1.0000Benzene ug/L LGW-10 1/25/2007 1.4000 1.0000Benzene ug/L LGW-10 1/23/2008 1.4000 1.0000Benzene ug/L LGW-10 7/22/2008 1.7000 1.0000Benzene ug/L LGW-10 7/29/2009 1.4000 1.0000Benzene ug/L LGW-10 2/03/2010 1.2000 1.0000Benzene ug/L LGW-10 2/03/2010 1.2000 1.0000Benzene ug/L LGW-10 7/16/2010 2.4000 1.0000Benzene ug/L LGW-10 1/19/2011 1.1000 1.0000Benzene ug/L LGW-10 7/12/2011 2.4000 1.0000Benzene ug/L LGW-10 1/05/2012 2.1000 1.0000Benzene ug/L LGW-10 7/09/2012 1.6000 1.0000Benzene ug/L LGW-10 5/01/2013 2.4000 1.0000Benzene ug/L LGW-10 1/30/2014 2.0000 1.0000Benzene ug/L LGW-10 7/09/2014 2.0000 1.0000Benzene ug/L LGW-10 2/12/2015 2.3000 1.0000Benzene ug/L LGW-10 7/13/2015 3.2000 1.0000Benzene ug/L LGW-10 1/05/2016 2.6000 1.0000Benzene ug/L LGW-10 2/10/2016 1.5000 1.0000Benzene ug/L LGW-10 4/06/2016 2.4000 1.0000Benzene ug/L LGW-10 7/21/2016 3.2000 1.0000Benzene ug/L LGW-10 10/06/2016 2.6000 1.0000Benzene ug/L LGW-10 1/11/2017 1.6000 1.0000Benzene ug/L LGW-10 4/04/2017 3.2000 1.0000Benzene ug/L LGW-10 7/19/2017 3.4000 1.0000Benzene ug/L LGW-10 10/09/2017 3.2000 1.0000Benzene ug/L LGW-10 1/24/2018 1.3000 1.0000Benzene ug/L LGW-10 4/11/2018 2.2000 1.0000Benzene ug/L LGW-10 7/16/2018 1.9000 1.0000Bis(2-ethylhexyl) phthalate ug/L LGW-10 10/26/2006 20.0000 10.0000Chlorobenzene ug/L LGW-10 5/01/2013 1.1000 1.0000Chlorobenzene ug/L LGW-10 7/13/2015 1.3000 1.0000Chlorobenzene ug/L LGW-10 1/05/2016 1.0000 1.0000Chlorobenzene ug/L LGW-10 7/21/2016 1.3000 1.0000Chlorobenzene ug/L LGW-10 10/06/2016 1.0000 1.0000Chlorobenzene ug/L LGW-10 4/04/2017 1.2000 1.0000Chlorobenzene ug/L LGW-10 7/19/2017 1.3000 1.0000Chlorobenzene ug/L LGW-10 10/09/2017 1.2000 1.0000Chloroethane ug/L LGW-10 7/12/2011 1.6000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 1/26/2006 3.8000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 8/01/2006 4.5000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 8/01/2006 4.5000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 10/26/2006 2.3000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 1/25/2007 2.7000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 4/26/2007 2.2000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 7/12/2007 1.7000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 1/23/2008 2.2000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 7/22/2008 2.8000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 7/29/2009 2.0000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 2/03/2010 1.5000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 2/03/2010 1.5000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 7/16/2010 2.8000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 1/19/2011 1.4000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 7/12/2011 2.8000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 1/05/2012 2.5000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 7/09/2012 2.2000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 5/01/2013 2.9000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 1/30/2014 2.5000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 7/09/2014 2.6000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 2/12/2015 2.9000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 7/13/2015 3.7000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 1/05/2016 3.1000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 2/10/2016 1.7000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 4/06/2016 2.7000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 7/21/2016 3.3000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 10/06/2016 2.9000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 1/11/2017 1.9000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 4/04/2017 3.4000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 7/19/2017 3.4000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 10/09/2017 3.0000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 1/24/2018 1.3000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 4/11/2018 2.2000 1.0000Cis-1,2-dichloroethene ug/L LGW-10 7/16/2018 1.7000 1.0000Iodomethane ug/L LGW-10 1/24/2018 1.4000 1.0000Methyl ethyl ketone ug/L LGW-10 1/25/2007 9.3000 5.0000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 27: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Historical Volatile Organic Compound DetectionsConstituent Units Well Date Result Limit

Vinyl chloride ug/L LGW-10 10/26/2006 1.5000 1.0000Vinyl chloride ug/L LGW-10 1/25/2007 1.2000 1.0000Vinyl chloride ug/L LGW-10 1/23/2008 1.9000 1.0000Vinyl chloride ug/L LGW-10 7/22/2008 1.7000 1.0000Vinyl chloride ug/L LGW-10 7/16/2010 1.6000 1.0000Vinyl chloride ug/L LGW-10 7/12/2011 2.9000 1.0000Vinyl chloride ug/L LGW-10 1/05/2012 1.2000 1.0000Vinyl chloride ug/L LGW-10 5/01/2013 1.6000 1.0000Vinyl chloride ug/L LGW-10 1/30/2014 1.8000 1.0000Vinyl chloride ug/L LGW-10 7/09/2014 1.8000 1.0000Vinyl chloride ug/L LGW-10 2/12/2015 1.8000 1.0000Vinyl chloride ug/L LGW-10 7/13/2015 1.9000 1.0000Vinyl chloride ug/L LGW-10 1/05/2016 1.9000 1.0000Vinyl chloride ug/L LGW-10 4/06/2016 1.3000 1.0000Vinyl chloride ug/L LGW-10 7/21/2016 1.3000 1.0000Vinyl chloride ug/L LGW-10 10/06/2016 1.6000 1.0000Vinyl chloride ug/L LGW-10 4/04/2017 2.1000 1.0000Vinyl chloride ug/L LGW-10 7/19/2017 2.0000 1.0000Vinyl chloride ug/L LGW-10 10/09/2017 1.2000 1.0000Vinyl chloride ug/L LGW-10 4/11/2018 1.2000 1.0000Acetone ug/L LGW-14R 8/02/2006 5.5000 5.0000Acetone ug/L LGW-14R 8/02/2006 5.5000 5.0000Acetone ug/L LGW-14R 7/11/2007 5.8000 5.0000Acetone ug/L LGW-14R 7/09/2012 5.1000 5.0000Acetone ug/L LGW-14R 1/25/2018 8.4000 5.0000Acetone ug/L LGW-14R 6/21/2018 15.0000 5.0000Acetone ug/L LGW-14R 7/17/2018 29.0000 5.0000Acetone ug/L LGW-2 7/30/2009 6.9000 5.0000Acetone ug/L LGW-2 7/18/2017 21.0000 5.0000Acetone ug/L LGW-2 7/12/2018 17.0000 5.0000Vinyl chloride ug/L LGW-2 7/12/2018 1.7000 1.0000Acetone ug/L LGW-3R 7/09/2012 5.7000 5.0000Acetone ug/L LGW-3R 7/08/2014 7.8000 5.0000Acetone ug/L LGW-3R 7/16/2015 7.0000 5.0000Acetone ug/L LGW-3R 7/11/2018 6.2000 5.0000Iodomethane ug/L LGW-4 1/19/2011 1.0000 1.00001,1-dichloroethene ug/L LGW-5 2/10/2015 1.0000 1.0000Bis(2-ethylhexyl) phthalate ug/L LGW-5 10/26/2006 21.0000 10.0000Acetone ug/L LGW-6 7/09/2012 5.1000 5.0000Carbon disulfide ug/L LGW-6 1/24/2006 2.0000 1.0000Acetone ug/L LGW-7 7/12/2018 7.6000 5.0000Acetone ug/L LGW-8R 7/18/2017 7.2000 5.0000Acetone ug/L LGW-8R 1/25/2018 6.9000 5.0000Acetone ug/L LGW-8R 7/13/2018 6.0000 5.0000Acetone ug/L LGW-9 7/18/2017 5.0000 5.0000Acetone ug/L LGW-9 4/11/2018 12.0000 5.0000Acetone ug/L LGW-9 7/13/2018 7.7000 5.0000Acetone ug/L MW-10N 1/22/1998 32.0000 19.0000Acetone ug/L MW-10N 7/08/2003 9.9000 5.0000Acetone ug/L MW-10N 1/24/2007 5.5000 5.0000Acetone ug/L MW-10N 7/11/2018 5.6000 5.0000Benzene ug/L MW-10N 4/28/1998 .4100 6.0000Carbon disulfide ug/L MW-10N 4/28/1998 .6700 8.4000Carbon disulfide ug/L MW-10N 7/10/2002 1.0000 1.0000Carbon disulfide ug/L MW-10N 4/15/2003 1.2000 1.0000Carbon disulfide ug/L MW-10N 7/08/2003 1.3000 1.0000Carbon disulfide ug/L MW-10N 1/28/2004 1.0000 1.0000Carbon disulfide ug/L MW-10N 7/27/2004 5.0000 1.0000Carbon disulfide ug/L MW-10N 7/20/2005 1.1000 1.0000Chloroform ug/L MW-10N 10/22/1997 8.3000 2.7000Chloroform ug/L MW-10N 1/22/1998 3.8000 2.7000Chloroform ug/L MW-10N 4/28/1998 .8400 5.4000Methyl ethyl ketone ug/L MW-10N 7/15/1999 80.0000 9.7000Methyl ethyl ketone ug/L MW-10N 4/10/2001 7.5000 5.0000Methyl ethyl ketone ug/L MW-10N 7/10/2002 50.0000 5.0000Methyl ethyl ketone ug/L MW-10N 10/02/2002 5.1000 5.0000Toluene ug/L MW-10N 4/28/1998 1.4000 5.0000Total xylenes ug/L MW-10N 4/28/1998 .8100 21.0000Total xylenes ug/L MW-10N 10/20/1999 .3200 10.0000Total xylenes ug/L MW-10N 4/25/2000 .3700 10.0000Acetone ug/L MW-11N 7/17/2018 8.9000 5.0000Carbon disulfide ug/L MW-11N 10/22/1997 7.9000 4.2000Carbon disulfide ug/L MW-11N 4/28/1998 10.0000 4.2000Carbon disulfide ug/L MW-11N 7/09/2002 .7500 1.0000Carbon disulfide ug/L MW-11N 1/23/2003 1.1000 1.0000Chloroform ug/L MW-11N 10/22/1997 9.4000 2.7000Chloroform ug/L MW-11N 1/21/1998 4.8000 2.7000Chloroform ug/L MW-11N 4/28/1998 .3900 2.7000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 28: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Historical Volatile Organic Compound DetectionsConstituent Units Well Date Result Limit

Chloroform ug/L MW-11N 7/09/2002 .3100 1.0000Methylene chloride ug/L MW-11N 4/28/1998 1.9000 4.1000Methylene chloride ug/L MW-11N 10/20/1999 .6600 4.1000Methylene chloride ug/L MW-11N 4/25/2000 .5700 4.1000Methylene chloride ug/L MW-11N 7/09/2002 1.2000 1.0000Methylene chloride ug/L MW-11N 10/02/2002 .8700 1.0000Methylene chloride ug/L MW-11N 1/23/2003 1.4000 1.0000Toluene ug/L MW-11N 4/28/1998 .2400 2.5000Acetone ug/L MW-15 6/05/2015 8.5000 5.0000Acetone ug/L MW-15 7/15/2015 7.1000 5.0000Acetone ug/L MW-15 7/18/2017 5.6000 5.0000Acetone ug/L MW-16 6/05/2015 13.0000 5.0000Acetone ug/L MW-16 7/18/2017 6.8000 5.0000Acetone ug/L MW-17 6/05/2015 6.5000 5.0000Acetone ug/L MW-19 7/16/2015 5.9000 5.0000Acetone ug/L MW-19 7/18/2017 6.7000 5.00001,1-dichloroethane ug/L MW-1N 4/13/1999 2.7000 2.50001,1-dichloroethane ug/L MW-1N 7/12/2000 2.1000 1.00001,1-dichloroethane ug/L MW-1N 4/12/2001 3.2000 1.00001,1-dichloroethane ug/L MW-1N 5/29/2002 2.6000 2.50001,1-dichloroethane ug/L MW-1N 5/29/2002 2.6000 1.00001,1-dichloroethane ug/L MW-1N 7/09/2002 2.8000 1.00001,1-dichloroethane ug/L MW-1N 10/03/2002 2.8000 1.00001,1-dichloroethane ug/L MW-1N 1/22/2003 1.6000 1.00001,1-dichloroethane ug/L MW-1N 4/15/2003 1.6000 1.00001,1-dichloroethane ug/L MW-1N 7/08/2003 1.0000 1.00001,4-dichlorobenzene ug/L MW-1N 7/12/2000 .9500 1.00001,4-dichlorobenzene ug/L MW-1N 10/18/2000 .5000 1.00001,4-dichlorobenzene ug/L MW-1N 1/24/2001 .2600 1.00001,4-dichlorobenzene ug/L MW-1N 4/12/2001 2.5000 1.00001,4-dichlorobenzene ug/L MW-1N 7/09/2002 .5700 1.00001,4-dichlorobenzene ug/L MW-1N 10/03/2002 .6200 1.0000Acetone ug/L MW-1N 4/28/1998 7.4000 19.0000Acetone ug/L MW-1N 7/09/2014 10.0000 5.0000Acetone ug/L MW-1N 7/10/2018 26.0000 5.0000Benzene ug/L MW-1N 10/19/1999 .2900 3.0000Benzene ug/L MW-1N 7/12/2000 1.4000 1.0000Benzene ug/L MW-1N 10/18/2000 .8300 1.0000Benzene ug/L MW-1N 1/24/2001 .2100 1.0000Benzene ug/L MW-1N 4/12/2001 2.6000 1.0000Benzene ug/L MW-1N 7/09/2002 .2600 1.0000Benzene ug/L MW-1N 10/03/2002 .2900 1.0000Carbon disulfide ug/L MW-1N 4/28/1998 3.4000 4.2000Carbon disulfide ug/L MW-1N 7/12/2000 .8200 1.0000Carbon disulfide ug/L MW-1N 5/29/2002 1.4000 1.0000Carbon disulfide ug/L MW-1N 7/09/2002 .8500 1.0000Carbon disulfide ug/L MW-1N 7/27/2004 2.9000 1.0000Carbon disulfide ug/L MW-1N 1/18/2006 4.2000 1.0000Chlorobenzene ug/L MW-1N 4/12/2001 .4500 1.0000Chloroethane ug/L MW-1N 7/12/2000 1.9000 1.0000Chloroethane ug/L MW-1N 10/18/2000 1.4000 1.0000Chloroethane ug/L MW-1N 4/12/2001 2.5000 1.0000Chloroethane ug/L MW-1N 7/09/2002 .2400 1.0000Chloroethane ug/L MW-1N 10/03/2002 .2100 1.0000Chloroform ug/L MW-1N 4/28/1998 .4100 2.7000Chloroform ug/L MW-1N 10/19/1999 .3900 2.7000Chloroform ug/L MW-1N 1/14/2000 .2100 2.7000Chloroform ug/L MW-1N 4/25/2000 .4200 2.7000Cis-1,2-dichloroethene ug/L MW-1N 10/19/1999 .3500 2.7000Cis-1,2-dichloroethene ug/L MW-1N 7/12/2000 3.8000 1.0000Cis-1,2-dichloroethene ug/L MW-1N 10/18/2000 2.2000 1.0000Cis-1,2-dichloroethene ug/L MW-1N 1/24/2001 .6100 1.0000Cis-1,2-dichloroethene ug/L MW-1N 4/12/2001 7.4000 1.0000Cis-1,2-dichloroethene ug/L MW-1N 7/09/2002 .9600 1.0000Cis-1,2-dichloroethene ug/L MW-1N 10/03/2002 1.1000 1.0000Methylene chloride ug/L MW-1N 4/28/1998 .5300 4.1000Methylene chloride ug/L MW-1N 1/14/2000 .4800 4.1000Methylene chloride ug/L MW-1N 7/12/2000 .5400 1.0000Methylene chloride ug/L MW-1N 10/18/2000 .3400 1.0000Methylene chloride ug/L MW-1N 4/12/2001 1.2000 1.0000Tetrachloroethene ug/L MW-1N 7/12/2000 .3400 1.0000Toluene ug/L MW-1N 4/28/1998 .2100 2.5000Trichloroethene ug/L MW-1N 7/12/2000 .7100 1.0000Trichloroethene ug/L MW-1N 10/18/2000 .4600 1.0000Trichloroethene ug/L MW-1N 4/12/2001 1.5000 1.0000Trichloroethene ug/L MW-1N 7/09/2002 .5900 1.0000Trichloroethene ug/L MW-1N 10/03/2002 .6400 1.0000Vinyl chloride ug/L MW-1N 1/20/1998 2.2000 2.0000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 29: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Historical Volatile Organic Compound DetectionsConstituent Units Well Date Result Limit

Vinyl chloride ug/L MW-1N 4/28/1998 .5000 2.0000Vinyl chloride ug/L MW-1N 4/13/1999 9.8000 2.0000Vinyl chloride ug/L MW-1N 5/19/1999 2.0000 2.0000Vinyl chloride ug/L MW-1N 7/15/1999 4.4000 2.0000Vinyl chloride ug/L MW-1N 10/19/1999 1.3000 2.0000Vinyl chloride ug/L MW-1N 1/14/2000 .2900 2.0000Vinyl chloride ug/L MW-1N 7/12/2000 6.2000 1.0000Vinyl chloride ug/L MW-1N 10/18/2000 5.6000 1.0000Vinyl chloride ug/L MW-1N 1/24/2001 1.8000 1.0000Vinyl chloride ug/L MW-1N 4/12/2001 4.2000 1.0000Vinyl chloride ug/L MW-1N 7/09/2002 .4400 1.0000Vinyl chloride ug/L MW-1N 10/03/2002 .3400 1.0000Acetone ug/L MW-20 1/12/2017 9.9000 5.00001,4-dichlorobenzene ug/L MW-21 6/05/2015 1.4000 1.00001,4-dichlorobenzene ug/L MW-21 7/14/2015 1.2000 1.00001,4-dichlorobenzene ug/L MW-21 8/04/2015 1.5000 1.00001,4-dichlorobenzene ug/L MW-21 9/02/2015 1.0000 1.00001,4-dichlorobenzene ug/L MW-21 4/05/2016 1.2000 1.00001,4-dichlorobenzene ug/L MW-21 7/19/2017 1.3000 1.00001,4-dichlorobenzene ug/L MW-21 10/06/2017 1.4000 1.00001,4-dichlorobenzene ug/L MW-21 4/11/2018 2.3000 1.00001,4-dichlorobenzene ug/L MW-21 7/11/2018 1.3000 1.0000Acetone ug/L MW-21 10/06/2017 5.1000 5.0000Acetone ug/L MW-21 7/11/2018 24.0000 5.0000Chlorobenzene ug/L MW-21 4/11/2018 1.8000 1.0000Acetone ug/L MW-2N 7/11/2007 6.7000 5.0000Acetone ug/L MW-2N 7/19/2017 8.5000 5.0000Acetone ug/L MW-2N 7/12/2018 39.0000 5.0000Benzene ug/L MW-2N 7/10/2002 4.0000 1.0000Carbon disulfide ug/L MW-2N 7/10/2002 .2100 1.0000Carbon disulfide ug/L MW-2N 7/11/2007 1.0000 1.0000Chloroform ug/L MW-2N 4/28/1998 .4900 2.7000Ethylbenzene ug/L MW-2N 7/10/2002 1.1000 1.0000Methylene chloride ug/L MW-2N 4/28/1998 1.6000 4.1000Toluene ug/L MW-2N 10/17/2000 .2700 1.0000Toluene ug/L MW-2N 7/10/2002 5.8000 1.0000Toluene ug/L MW-2N 10/02/2002 .2200 1.0000Toluene ug/L MW-2N 7/27/2004 1.5000 1.0000Toluene ug/L MW-2N 1/26/2007 1.7000 1.0000Toluene ug/L MW-2N 1/24/2008 1.1000 1.0000Total xylenes ug/L MW-2N 7/10/2002 5.0000 1.00001,1-dichloroethane ug/L MW-3N 4/28/1998 .7800 2.50001,1-dichloroethane ug/L MW-3N 10/20/1999 .9700 2.50001,1-dichloroethane ug/L MW-3N 1/14/2000 .8600 2.50001,1-dichloroethane ug/L MW-3N 4/24/2000 1.6000 2.50001,1-dichloroethane ug/L MW-3N 7/11/2000 .8400 1.00001,1-dichloroethane ug/L MW-3N 10/17/2000 .9300 1.00001,1-dichloroethane ug/L MW-3N 1/23/2001 1.1000 1.00001,1-dichloroethane ug/L MW-3N 4/11/2001 .9600 1.00001,1-dichloroethane ug/L MW-3N 5/29/2002 2.6000 2.50001,1-dichloroethane ug/L MW-3N 5/29/2002 2.6000 1.00001,1-dichloroethane ug/L MW-3N 7/09/2002 2.2000 1.00001,1-dichloroethane ug/L MW-3N 10/02/2002 2.7000 1.00001,1-dichloroethane ug/L MW-3N 1/22/2003 2.0000 1.00001,1-dichloroethane ug/L MW-3N 4/14/2003 2.3000 1.00001,1-dichloroethane ug/L MW-3N 7/07/2003 2.9000 1.00001,1-dichloroethane ug/L MW-3N 1/28/2004 2.7000 1.00001,1-dichloroethane ug/L MW-3N 7/27/2004 2.9000 1.00001,1-dichloroethane ug/L MW-3N 1/12/2005 2.1000 1.00001,1-dichloroethane ug/L MW-3N 7/20/2005 2.7000 1.00001,1-dichloroethane ug/L MW-3N 1/18/2006 2.3000 1.00001,1-dichloroethane ug/L MW-3N 7/19/2006 2.8000 1.00001,1-dichloroethane ug/L MW-3N 7/19/2006 2.8000 1.00001,1-dichloroethane ug/L MW-3N 10/25/2006 2.3000 1.00001,1-dichloroethane ug/L MW-3N 1/26/2007 2.4000 1.00001,1-dichloroethane ug/L MW-3N 7/11/2007 2.1000 1.00001,1-dichloroethane ug/L MW-3N 1/24/2008 2.8000 1.00001,1-dichloroethane ug/L MW-3N 7/22/2008 2.3000 1.00001,1-dichloroethane ug/L MW-3N 2/04/2009 2.0000 1.00001,1-dichloroethane ug/L MW-3N 7/31/2009 2.0000 1.00001,1-dichloroethane ug/L MW-3N 1/26/2010 2.3000 1.00001,1-dichloroethane ug/L MW-3N 7/13/2010 2.1000 1.00001,1-dichloroethane ug/L MW-3N 7/14/2011 1.9000 1.00001,1-dichloroethane ug/L MW-3N 1/05/2012 1.5000 1.00001,1-dichloroethane ug/L MW-3N 7/11/2012 1.5000 1.00001,1-dichloroethane ug/L MW-3N 5/01/2013 1.2000 1.00001,1-dichloroethane ug/L MW-3N 1/24/2014 1.0000 1.00001,1-dichloroethane ug/L MW-3N 7/09/2014 1.3000 1.0000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 30: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Historical Volatile Organic Compound DetectionsConstituent Units Well Date Result Limit

1,1-dichloroethane ug/L MW-3N 4/01/2015 1.1000 1.00001,1-dichloroethane ug/L MW-3N 10/05/2015 1.0000 1.00001,4-dichlorobenzene ug/L MW-3N 7/09/2002 .3700 1.00001,4-dichlorobenzene ug/L MW-3N 10/02/2002 .4600 1.00001,4-dichlorobenzene ug/L MW-3N 1/24/2008 1.0000 1.00001,4-dichlorobenzene ug/L MW-3N 1/26/2010 1.0000 1.0000Acetone ug/L MW-3N 10/09/2017 5.6000 5.0000Benzene ug/L MW-3N 4/28/1998 .2300 3.0000Benzene ug/L MW-3N 10/20/1999 .3400 3.0000Benzene ug/L MW-3N 4/24/2000 .3200 3.0000Benzene ug/L MW-3N 7/11/2000 .2900 1.0000Benzene ug/L MW-3N 10/17/2000 .2800 1.0000Benzene ug/L MW-3N 1/23/2001 .3000 1.0000Benzene ug/L MW-3N 4/11/2001 .5800 1.0000Benzene ug/L MW-3N 7/09/2002 .9700 1.0000Benzene ug/L MW-3N 10/02/2002 1.2000 1.0000Benzene ug/L MW-3N 1/28/2004 1.1000 1.0000Benzene ug/L MW-3N 7/27/2004 1.3000 1.0000Benzene ug/L MW-3N 7/19/2006 1.2000 1.0000Benzene ug/L MW-3N 7/19/2006 1.2000 1.0000Benzene ug/L MW-3N 10/25/2006 1.1000 1.0000Benzene ug/L MW-3N 7/11/2007 1.0000 1.0000Benzene ug/L MW-3N 1/24/2008 1.3000 1.0000Benzene ug/L MW-3N 7/22/2008 1.1000 1.0000Benzene ug/L MW-3N 2/04/2009 1.1000 1.0000Carbon disulfide ug/L MW-3N 4/28/1998 .5800 4.2000Carbon disulfide ug/L MW-3N 5/29/2002 1.4000 1.0000Carbon disulfide ug/L MW-3N 7/09/2002 .4100 1.0000Carbon disulfide ug/L MW-3N 10/02/2002 .4300 1.0000Chlorobenzene ug/L MW-3N 7/09/2002 .2000 1.0000Chlorobenzene ug/L MW-3N 10/02/2002 .2700 1.0000Chloroethane ug/L MW-3N 4/28/1998 .4400 5.9000Chloroethane ug/L MW-3N 10/20/1999 .4300 5.9000Chloroethane ug/L MW-3N 1/14/2000 .2400 5.9000Chloroethane ug/L MW-3N 4/24/2000 .3400 5.9000Chloroethane ug/L MW-3N 5/29/2002 1.0000 1.0000Chloroethane ug/L MW-3N 7/09/2002 .8300 1.0000Chloroethane ug/L MW-3N 10/02/2002 1.0000 1.0000Chloroethane ug/L MW-3N 1/22/2003 1.1000 1.0000Chloroethane ug/L MW-3N 7/07/2003 1.0000 1.0000Chloroethane ug/L MW-3N 1/12/2005 1.2000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 4/28/1998 .6200 2.7000Cis-1,2-dichloroethene ug/L MW-3N 10/20/1999 .7900 2.7000Cis-1,2-dichloroethene ug/L MW-3N 1/14/2000 .3500 2.7000Cis-1,2-dichloroethene ug/L MW-3N 4/24/2000 .9400 2.7000Cis-1,2-dichloroethene ug/L MW-3N 7/11/2000 .6000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 10/17/2000 .6800 1.0000Cis-1,2-dichloroethene ug/L MW-3N 1/23/2001 .6500 1.0000Cis-1,2-dichloroethene ug/L MW-3N 4/11/2001 .9900 1.0000Cis-1,2-dichloroethene ug/L MW-3N 5/29/2002 2.0000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 7/09/2002 1.8000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 10/02/2002 1.9000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 1/22/2003 1.4000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 4/14/2003 1.7000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 7/07/2003 2.3000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 1/28/2004 1.8000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 7/27/2004 2.2000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 1/12/2005 1.4000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 7/20/2005 1.8000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 1/18/2006 1.6000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 7/19/2006 1.9000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 7/19/2006 1.9000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 10/25/2006 1.9000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 1/26/2007 1.2000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 7/11/2007 1.6000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 1/24/2008 1.9000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 7/22/2008 1.9000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 2/04/2009 1.9000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 7/31/2009 1.5000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 1/26/2010 1.6000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 7/13/2010 1.4000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 7/14/2011 1.3000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 1/05/2012 1.3000 1.0000Cis-1,2-dichloroethene ug/L MW-3N 7/11/2012 1.3000 1.0000Dichlorodifluoromethane ug/L MW-3N 1/14/2000 2.9000 1.0000Dichlorodifluoromethane ug/L MW-3N 4/11/2001 2.3000 1.0000Methylene chloride ug/L MW-3N 4/28/1998 .7000 4.1000Methylene chloride ug/L MW-3N 1/14/2000 .3700 4.1000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 31: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Historical Volatile Organic Compound DetectionsConstituent Units Well Date Result Limit

Tetrachloroethene ug/L MW-3N 10/21/1997 1.2000 1.2000Tetrachloroethene ug/L MW-3N 4/28/1998 1.0000 1.2000Tetrachloroethene ug/L MW-3N 7/23/1998 1.2000 1.2000Tetrachloroethene ug/L MW-3N 10/20/1999 .8900 1.2000Tetrachloroethene ug/L MW-3N 1/14/2000 .6700 1.2000Tetrachloroethene ug/L MW-3N 4/24/2000 .9400 1.2000Tetrachloroethene ug/L MW-3N 7/11/2000 .5000 1.0000Tetrachloroethene ug/L MW-3N 10/17/2000 .7600 1.0000Tetrachloroethene ug/L MW-3N 1/23/2001 .5800 1.0000Tetrachloroethene ug/L MW-3N 4/11/2001 .6100 1.0000Tetrachloroethene ug/L MW-3N 7/09/2002 .5900 1.0000Tetrachloroethene ug/L MW-3N 10/02/2002 .2900 1.0000Trichloroethene ug/L MW-3N 4/28/1998 1.5000 3.2000Trichloroethene ug/L MW-3N 10/20/1999 1.4000 3.2000Trichloroethene ug/L MW-3N 1/14/2000 .9900 3.2000Trichloroethene ug/L MW-3N 4/24/2000 1.4000 3.2000Trichloroethene ug/L MW-3N 7/11/2000 1.5000 1.0000Trichloroethene ug/L MW-3N 10/17/2000 1.5000 1.0000Trichloroethene ug/L MW-3N 1/23/2001 1.2000 1.0000Trichloroethene ug/L MW-3N 4/11/2001 1.6000 1.0000Trichloroethene ug/L MW-3N 5/29/2002 1.8000 1.0000Trichloroethene ug/L MW-3N 7/09/2002 1.7000 1.0000Trichloroethene ug/L MW-3N 10/02/2002 1.8000 1.0000Trichloroethene ug/L MW-3N 1/22/2003 1.2000 1.0000Trichloroethene ug/L MW-3N 4/14/2003 1.2000 1.0000Trichloroethene ug/L MW-3N 7/07/2003 1.1000 1.0000Trichloroethene ug/L MW-3N 1/28/2004 1.1000 1.0000Trichloroethene ug/L MW-3N 7/27/2004 1.2000 1.0000Trichloroethene ug/L MW-3N 7/20/2005 1.1000 1.0000Trichlorofluoromethane ug/L MW-3N 4/28/1998 .6400 7.5000Trichlorofluoromethane ug/L MW-3N 10/20/1999 .4100 7.5000Trichlorofluoromethane ug/L MW-3N 1/14/2000 .2500 7.5000Trichlorofluoromethane ug/L MW-3N 4/24/2000 .6100 7.5000Trichlorofluoromethane ug/L MW-3N 7/11/2000 .2800 1.0000Trichlorofluoromethane ug/L MW-3N 10/17/2000 .3100 1.0000Trichlorofluoromethane ug/L MW-3N 1/23/2001 .2800 1.0000Trichlorofluoromethane ug/L MW-3N 7/09/2002 .2200 1.0000Vinyl chloride ug/L MW-3N 4/28/1998 .4600 2.0000Vinyl chloride ug/L MW-3N 10/20/1999 .5700 2.0000Vinyl chloride ug/L MW-3N 1/14/2000 .3700 2.0000Vinyl chloride ug/L MW-3N 4/24/2000 .3800 2.0000Vinyl chloride ug/L MW-3N 7/11/2000 .2600 1.0000Vinyl chloride ug/L MW-3N 10/17/2000 .4300 1.0000Vinyl chloride ug/L MW-3N 1/23/2001 .3500 1.0000Vinyl chloride ug/L MW-3N 4/11/2001 .7400 1.0000Vinyl chloride ug/L MW-3N 5/29/2002 1.4000 1.0000Vinyl chloride ug/L MW-3N 7/09/2002 1.2000 1.0000Vinyl chloride ug/L MW-3N 10/02/2002 1.7000 1.0000Vinyl chloride ug/L MW-3N 1/22/2003 1.5000 1.0000Vinyl chloride ug/L MW-3N 4/14/2003 1.2000 1.0000Vinyl chloride ug/L MW-3N 7/07/2003 1.7000 1.0000Vinyl chloride ug/L MW-3N 1/28/2004 1.6000 1.0000Vinyl chloride ug/L MW-3N 1/12/2005 2.0000 1.0000Vinyl chloride ug/L MW-3N 11/08/2005 3.4000 1.0000Vinyl chloride ug/L MW-3N 1/18/2006 1.2000 1.0000Vinyl chloride ug/L MW-3N 7/19/2006 1.3000 1.0000Vinyl chloride ug/L MW-3N 7/19/2006 1.3000 1.0000Vinyl chloride ug/L MW-3N 1/24/2008 2.2000 1.0000Vinyl chloride ug/L MW-3N 5/03/2008 1.1000 1.0000Vinyl chloride ug/L MW-3N 7/22/2008 1.4000 1.0000Vinyl chloride ug/L MW-3N 2/04/2009 1.3000 1.0000Vinyl chloride ug/L MW-3N 1/26/2010 1.2000 1.0000Vinyl chloride ug/L MW-3N 7/14/2011 2.1000 1.00001,1-dichloroethane ug/L MW-7N 7/22/1998 5.4000 2.50001,1-dichloroethane ug/L MW-7N 8/18/1998 4.7000 2.50001,1-dichloroethane ug/L MW-7N 9/17/1998 4.4000 2.50001,1-dichloroethane ug/L MW-7N 10/15/1998 3.6000 2.50001,1-dichloroethane ug/L MW-7N 11/09/1998 5.0000 2.50001,1-dichloroethane ug/L MW-7N 1/14/1999 3.5000 2.50001,1-dichloroethane ug/L MW-7N 4/14/1999 6.0000 2.50001,1-dichloroethane ug/L MW-7N 7/14/1999 5.6000 2.50001,1-dichloroethane ug/L MW-7N 10/19/1999 5.6000 2.50001,1-dichloroethane ug/L MW-7N 1/13/2000 4.8000 2.50001,1-dichloroethane ug/L MW-7N 4/25/2000 8.4000 2.50001,1-dichloroethane ug/L MW-7N 10/17/2000 5.5000 1.00001,1-dichloroethane ug/L MW-7N 1/23/2001 5.7000 1.00001,1-dichloroethane ug/L MW-7N 4/10/2001 6.1000 1.00001,1-dichloroethane ug/L MW-7N 5/29/2002 7.9000 1.0000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 32: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Historical Volatile Organic Compound DetectionsConstituent Units Well Date Result Limit

1,1-dichloroethane ug/L MW-7N 5/29/2002 7.9000 2.50001,1-dichloroethane ug/L MW-7N 7/09/2002 5.1000 1.00001,1-dichloroethane ug/L MW-7N 10/02/2002 4.7000 1.00001,1-dichloroethane ug/L MW-7N 1/23/2003 3.6000 1.00001,1-dichloroethane ug/L MW-7N 4/14/2003 4.3000 1.00001,1-dichloroethane ug/L MW-7N 7/07/2003 5.0000 1.00001,1-dichloroethane ug/L MW-7N 1/27/2004 4.5000 1.00001,1-dichloroethane ug/L MW-7N 4/08/2004 4.1000 1.00001,1-dichloroethane ug/L MW-7N 7/26/2004 3.6000 1.00001,1-dichloroethane ug/L MW-7N 1/12/2005 3.3000 1.00001,1-dichloroethane ug/L MW-7N 7/19/2005 3.8000 1.00001,1-dichloroethane ug/L MW-7N 1/19/2006 3.1000 1.00001,1-dichloroethane ug/L MW-7N 7/19/2006 3.4000 1.00001,1-dichloroethane ug/L MW-7N 7/19/2006 3.4000 1.00001,1-dichloroethane ug/L MW-7N 10/24/2006 3.2000 1.00001,1-dichloroethane ug/L MW-7N 1/26/2007 1.9000 1.00001,1-dichloroethane ug/L MW-7N 7/10/2007 1.0000 1.00001,1-dichloroethane ug/L MW-7N 2/06/2009 1.0000 1.00001,1-dichloroethane ug/L MW-7N 5/01/2013 1.2000 1.00001,2-dichloroethane ug/L MW-7N 10/02/2002 .2900 1.00001,2-dichloropropane ug/L MW-7N 10/19/1999 .9700 1.40001,2-dichloropropane ug/L MW-7N 1/13/2000 .6500 1.40001,2-dichloropropane ug/L MW-7N 4/25/2000 .8500 1.40001,2-dichloropropane ug/L MW-7N 1/23/2001 .8700 1.00001,2-dichloropropane ug/L MW-7N 4/10/2001 .6000 1.00001,2-dichloropropane ug/L MW-7N 5/29/2002 1.4000 1.40001,2-dichloropropane ug/L MW-7N 5/29/2002 1.4000 1.00001,2-dichloropropane ug/L MW-7N 7/09/2002 1.1000 1.00001,2-dichloropropane ug/L MW-7N 10/02/2002 .9600 1.00001,4-dichlorobenzene ug/L MW-7N 10/19/1999 1.9000 4.30001,4-dichlorobenzene ug/L MW-7N 1/13/2000 1.8000 4.30001,4-dichlorobenzene ug/L MW-7N 4/25/2000 1.5000 4.30001,4-dichlorobenzene ug/L MW-7N 10/17/2000 2.3000 1.00001,4-dichlorobenzene ug/L MW-7N 1/23/2001 1.9000 1.00001,4-dichlorobenzene ug/L MW-7N 4/10/2001 2.3000 1.00001,4-dichlorobenzene ug/L MW-7N 5/29/2002 2.8000 1.00001,4-dichlorobenzene ug/L MW-7N 7/09/2002 2.2000 1.00001,4-dichlorobenzene ug/L MW-7N 10/02/2002 2.2000 1.00001,4-dichlorobenzene ug/L MW-7N 1/23/2003 1.8000 1.00001,4-dichlorobenzene ug/L MW-7N 4/14/2003 1.9000 1.00001,4-dichlorobenzene ug/L MW-7N 7/07/2003 1.8000 1.00001,4-dichlorobenzene ug/L MW-7N 1/27/2004 1.7000 1.00001,4-dichlorobenzene ug/L MW-7N 4/08/2004 2.3000 1.00001,4-dichlorobenzene ug/L MW-7N 7/26/2004 3.1000 1.00001,4-dichlorobenzene ug/L MW-7N 1/12/2005 3.6000 1.00001,4-dichlorobenzene ug/L MW-7N 7/19/2005 4.8000 1.00001,4-dichlorobenzene ug/L MW-7N 1/19/2006 3.6000 1.00001,4-dichlorobenzene ug/L MW-7N 10/24/2006 3.9000 1.00001,4-dichlorobenzene ug/L MW-7N 1/26/2007 2.5000 1.00001,4-dichlorobenzene ug/L MW-7N 7/10/2007 1.4000 1.00001,4-dichlorobenzene ug/L MW-7N 7/21/2008 1.1000 1.00001,4-dichlorobenzene ug/L MW-7N 2/06/2009 1.4000 1.00001,4-dichlorobenzene ug/L MW-7N 1/26/2010 1.4000 1.00001,4-dichlorobenzene ug/L MW-7N 7/14/2010 1.1000 1.00001,4-dichlorobenzene ug/L MW-7N 5/01/2013 2.7000 1.00001,4-dichlorobenzene ug/L MW-7N 6/04/2013 1.3000 1.00001,4-dichlorobenzene ug/L MW-7N 1/11/2017 2.1000 1.00001,4-dichlorobenzene ug/L MW-7N 4/04/2017 1.7000 1.00001,4-dichlorobenzene ug/L MW-7N 7/19/2017 1.3000 1.0000Acetone ug/L MW-7N 1/21/1998 50.0000 19.0000Acetone ug/L MW-7N 4/04/2017 6.3000 5.0000Acetone ug/L MW-7N 7/13/2018 7.3000 5.0000Benzene ug/L MW-7N 7/22/1998 3.3000 3.0000Benzene ug/L MW-7N 8/18/1998 3.0000 3.0000Benzene ug/L MW-7N 11/09/1998 3.1000 3.0000Benzene ug/L MW-7N 7/14/1999 4.0000 3.0000Benzene ug/L MW-7N 10/19/1999 4.2000 3.0000Benzene ug/L MW-7N 1/13/2000 3.6000 3.0000Benzene ug/L MW-7N 4/25/2000 4.4000 3.0000Benzene ug/L MW-7N 10/17/2000 4.3000 1.0000Benzene ug/L MW-7N 1/23/2001 4.4000 1.0000Benzene ug/L MW-7N 4/10/2001 6.2000 1.0000Benzene ug/L MW-7N 5/29/2002 5.3000 3.1000Benzene ug/L MW-7N 5/29/2002 5.3000 1.0000Benzene ug/L MW-7N 7/09/2002 4.4000 1.0000Benzene ug/L MW-7N 10/02/2002 4.0000 1.0000Benzene ug/L MW-7N 1/23/2003 3.0000 1.0000Benzene ug/L MW-7N 4/14/2003 3.3000 1.0000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 33: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Historical Volatile Organic Compound DetectionsConstituent Units Well Date Result Limit

Benzene ug/L MW-7N 7/07/2003 3.3000 1.0000Benzene ug/L MW-7N 1/27/2004 3.2000 1.0000Benzene ug/L MW-7N 4/08/2004 2.9000 1.0000Benzene ug/L MW-7N 7/26/2004 1.8000 1.0000Benzene ug/L MW-7N 1/12/2005 1.7000 1.0000Benzene ug/L MW-7N 7/19/2005 2.0000 1.0000Benzene ug/L MW-7N 1/19/2006 1.5000 1.0000Benzene ug/L MW-7N 7/19/2006 1.4000 1.0000Benzene ug/L MW-7N 7/19/2006 1.4000 1.0000Benzene ug/L MW-7N 10/24/2006 1.3000 1.0000Carbon dioxide ug/L MW-7N 9/02/2010 1500.0000 50.0000Carbon disulfide ug/L MW-7N 10/17/2000 1.4000 1.0000Chlorobenzene ug/L MW-7N 10/19/1999 .3400 2.5000Chlorobenzene ug/L MW-7N 1/13/2000 .3100 2.5000Chlorobenzene ug/L MW-7N 4/25/2000 .2700 2.5000Chlorobenzene ug/L MW-7N 10/17/2000 .4000 1.0000Chlorobenzene ug/L MW-7N 1/23/2001 .3100 1.0000Chlorobenzene ug/L MW-7N 4/10/2001 .4800 1.0000Chlorobenzene ug/L MW-7N 7/09/2002 .5100 1.0000Chlorobenzene ug/L MW-7N 10/02/2002 .4800 1.0000Chloroethane ug/L MW-7N 10/19/1999 3.0000 5.9000Chloroethane ug/L MW-7N 1/13/2000 2.6000 5.9000Chloroethane ug/L MW-7N 4/25/2000 2.6000 5.9000Chloroethane ug/L MW-7N 10/17/2000 2.3000 1.0000Chloroethane ug/L MW-7N 1/23/2001 2.2000 1.0000Chloroethane ug/L MW-7N 4/10/2001 2.2000 1.0000Chloroethane ug/L MW-7N 5/29/2002 2.4000 1.0000Chloroethane ug/L MW-7N 7/09/2002 1.9000 1.0000Chloroethane ug/L MW-7N 10/02/2002 1.7000 1.0000Chloroethane ug/L MW-7N 1/23/2003 1.9000 1.0000Chloroethane ug/L MW-7N 4/14/2003 1.4000 1.0000Chloroethane ug/L MW-7N 7/07/2003 1.8000 1.0000Chloroethane ug/L MW-7N 1/27/2004 1.6000 1.0000Chloroethane ug/L MW-7N 4/08/2004 1.3000 1.0000Cis-1,2-dichloroethene ug/L MW-7N 7/22/1998 12.0000 2.7000Cis-1,2-dichloroethene ug/L MW-7N 8/18/1998 12.0000 2.7000Cis-1,2-dichloroethene ug/L MW-7N 9/17/1998 11.0000 2.7000Cis-1,2-dichloroethene ug/L MW-7N 10/15/1998 9.8000 2.7000Cis-1,2-dichloroethene ug/L MW-7N 11/09/1998 12.0000 2.7000Cis-1,2-dichloroethene ug/L MW-7N 1/14/1999 11.0000 2.7000Cis-1,2-dichloroethene ug/L MW-7N 4/14/1999 9.8000 2.7000Cis-1,2-dichloroethene ug/L MW-7N 7/14/1999 13.0000 2.7000Cis-1,2-dichloroethene ug/L MW-7N 10/19/1999 14.0000 2.7000Cis-1,2-dichloroethene ug/L MW-7N 1/13/2000 13.0000 2.7000Cis-1,2-dichloroethene ug/L MW-7N 4/25/2000 18.0000 2.7000Cis-1,2-dichloroethene ug/L MW-7N 10/17/2000 13.0000 1.0000Cis-1,2-dichloroethene ug/L MW-7N 1/23/2001 13.0000 1.0000Cis-1,2-dichloroethene ug/L MW-7N 4/10/2001 13.0000 1.0000Cis-1,2-dichloroethene ug/L MW-7N 5/29/2002 15.0000 1.0000Cis-1,2-dichloroethene ug/L MW-7N 5/29/2002 15.0000 2.7000Cis-1,2-dichloroethene ug/L MW-7N 7/09/2002 10.0000 1.0000Cis-1,2-dichloroethene ug/L MW-7N 10/02/2002 8.7000 1.0000Cis-1,2-dichloroethene ug/L MW-7N 1/23/2003 6.4000 1.0000Cis-1,2-dichloroethene ug/L MW-7N 4/14/2003 8.7000 1.0000Cis-1,2-dichloroethene ug/L MW-7N 7/07/2003 9.2000 1.0000Cis-1,2-dichloroethene ug/L MW-7N 1/27/2004 7.0000 1.0000Cis-1,2-dichloroethene ug/L MW-7N 4/08/2004 7.0000 1.0000Cis-1,2-dichloroethene ug/L MW-7N 7/26/2004 3.9000 1.0000Cis-1,2-dichloroethene ug/L MW-7N 1/12/2005 1.6000 1.0000Cis-1,2-dichloroethene ug/L MW-7N 7/19/2005 3.5000 1.0000Cis-1,2-dichloroethene ug/L MW-7N 1/19/2006 2.9000 1.0000Cis-1,2-dichloroethene ug/L MW-7N 7/19/2006 3.3000 1.0000Cis-1,2-dichloroethene ug/L MW-7N 7/19/2006 3.3000 1.0000Cis-1,2-dichloroethene ug/L MW-7N 10/24/2006 2.7000 1.0000Cis-1,2-dichloroethene ug/L MW-7N 1/26/2007 1.6000 1.0000Cis-1,2-dichloroethene ug/L MW-7N 1/26/2010 1.0000 1.0000Cis-1,2-dichloroethene ug/L MW-7N 7/14/2010 1.4000 1.0000Cis-1,2-dichloroethene ug/L MW-7N 1/20/2011 1.0000 1.0000Ethylbenzene ug/L MW-7N 10/17/2000 1.0000 1.0000Ethylbenzene ug/L MW-7N 4/10/2001 .2000 1.0000Ethylbenzene ug/L MW-7N 7/09/2002 .3000 1.0000Methyl ethyl ketone ug/L MW-7N 1/21/1998 92.0000 9.7000Methyl isobutyl ketone ug/L MW-7N 1/21/1998 8.0000 3.0000Methylene chloride ug/L MW-7N 4/10/2001 .4300 1.0000Toluene ug/L MW-7N 10/17/2000 .2400 1.0000Toluene ug/L MW-7N 4/10/2001 .4600 1.0000Total xylenes ug/L MW-7N 10/17/2000 .6400 1.0000Total xylenes ug/L MW-7N 4/10/2001 1.0000 1.0000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 34: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Historical Volatile Organic Compound DetectionsConstituent Units Well Date Result Limit

Trichloroethene ug/L MW-7N 10/19/1999 1.4000 3.2000Trichloroethene ug/L MW-7N 1/13/2000 .9200 3.2000Trichloroethene ug/L MW-7N 4/25/2000 1.1000 3.2000Trichloroethene ug/L MW-7N 10/17/2000 1.0000 1.0000Trichloroethene ug/L MW-7N 1/23/2001 .7500 1.0000Trichloroethene ug/L MW-7N 4/10/2001 1.0000 1.0000Trichloroethene ug/L MW-7N 7/09/2002 .9000 1.0000Trichloroethene ug/L MW-7N 10/02/2002 .8700 1.0000Vinyl chloride ug/L MW-7N 7/22/1998 3.6000 2.0000Vinyl chloride ug/L MW-7N 8/18/1998 2.6000 2.0000Vinyl chloride ug/L MW-7N 9/17/1998 3.4000 2.0000Vinyl chloride ug/L MW-7N 10/15/1998 2.1000 2.0000Vinyl chloride ug/L MW-7N 11/09/1998 3.0000 2.0000Vinyl chloride ug/L MW-7N 1/14/1999 2.3000 2.0000Vinyl chloride ug/L MW-7N 4/14/1999 3.1000 2.0000Vinyl chloride ug/L MW-7N 7/14/1999 4.7000 2.0000Vinyl chloride ug/L MW-7N 10/19/1999 5.8000 2.0000Vinyl chloride ug/L MW-7N 1/13/2000 4.7000 2.0000Vinyl chloride ug/L MW-7N 4/25/2000 4.5000 2.0000Vinyl chloride ug/L MW-7N 10/17/2000 5.6000 1.0000Vinyl chloride ug/L MW-7N 1/23/2001 5.1000 1.0000Vinyl chloride ug/L MW-7N 4/10/2001 4.4000 1.0000Vinyl chloride ug/L MW-7N 5/29/2002 5.7000 1.0000Vinyl chloride ug/L MW-7N 5/29/2002 5.7000 2.0000Vinyl chloride ug/L MW-7N 7/09/2002 4.8000 1.0000Vinyl chloride ug/L MW-7N 10/02/2002 4.7000 1.0000Vinyl chloride ug/L MW-7N 1/23/2003 5.9000 1.0000Vinyl chloride ug/L MW-7N 4/14/2003 3.8000 1.0000Vinyl chloride ug/L MW-7N 7/07/2003 5.4000 1.0000Vinyl chloride ug/L MW-7N 1/27/2004 4.6000 1.0000Vinyl chloride ug/L MW-7N 4/08/2004 4.2000 1.0000Vinyl chloride ug/L MW-7N 1/12/2005 2.3000 1.0000Vinyl chloride ug/L MW-7N 7/19/2005 3.6000 1.0000Vinyl chloride ug/L MW-7N 1/19/2006 2.7000 1.0000Vinyl chloride ug/L MW-7N 4/17/2006 2.2000 1.0000Vinyl chloride ug/L MW-7N 7/19/2006 1.9000 1.0000Vinyl chloride ug/L MW-7N 7/19/2006 1.9000 1.0000Vinyl chloride ug/L MW-7N 10/24/2006 1.9000 1.0000Vinyl chloride ug/L MW-7N 1/26/2007 1.2000 1.0000Vinyl chloride ug/L MW-7N 5/03/2008 1.2000 1.0000Vinyl chloride ug/L MW-7N 5/01/2013 1.0000 1.0000Acetone ug/L MW-8N 10/06/2017 5.2000 5.0000Acetone ug/L MW-8N 7/16/2018 6.8000 5.0000Carbon dioxide ug/L MW-8N 9/02/2010 1400.0000 50.0000Carbon disulfide ug/L MW-8N 7/14/1999 4.9000 4.2000Carbon disulfide ug/L MW-8N 5/29/2002 1.2000 1.0000Carbon disulfide ug/L MW-8N 7/09/2002 .2800 1.0000Carbon disulfide ug/L MW-8N 4/14/2003 1.2000 1.0000Carbon disulfide ug/L MW-8N 7/27/2004 1.4000 1.0000Chloroform ug/L MW-8N 1/22/1998 3.2000 2.7000Chloroform ug/L MW-8N 4/28/1998 .3600 2.7000Chloromethane ug/L MW-8N 1/12/2005 1.1000 1.0000Dichlorodifluoromethane ug/L MW-8N 1/14/2000 .4200 1.0000Endosulfan i ug/L MW-8N 7/11/2012 .3400 .0470Methylene chloride ug/L MW-8N 1/14/2000 .4800 4.1000Vinyl chloride ug/L MW-8N 10/19/1999 .2400 2.0000Vinyl chloride ug/L MW-8N 4/25/2000 .2600 2.0000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Detections are shown for constituents selected in the VOC list and all selected wellsThe Limit column refers to the laboratory reporting limit

Page 35: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Ground Water Statistics for Eco-Vista Sanitary Landfill Third Quarter Monitoring Event In 2018

C:\Otter Creek Environmental\Arkansas\Eco-Vista\ecovistaq318RRRR.doc December 14, 2018

Attachment C

Summary Tables and Graphs for the Intrawell Comparisons

Page 36: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Summary Statistics and Intermediate Computationsfor Combined Shewhart-Cusum Control Charts

Constituent Units Well N Mean SD S(i-1) S(i) LimitAntimony, total ug/L LGW-14R 11 2.0000**Arsenic, total ug/L LGW-14R 11 5.0000**Barium, total ug/L LGW-14R 11 34.3636 11.7326 34.3636 34.3636 110.6257Beryllium, total ug/L LGW-14R 11 1.0000**Cadmium, total ug/L LGW-14R 11 1.0000**Chromium, total ug/L LGW-14R 10 3.0000**Cobalt, total ug/L LGW-14R 11 3.0000**Copper, total ug/L LGW-14R 11 4.0000**Iron, total ug/L LGW-14R 10 120.0000**Lead, total ug/L LGW-14R 11 5.0000**Manganese, total ug/L LGW-14R 10 3.2800 0.5903 3.6097 3.2800 7.1169Nickel, total ug/L LGW-14R 10 4.0000**Selenium, total ug/L LGW-14R 11 10.0000**Silver, total ug/L LGW-14R 11 50.0000**Sulfate mg/L LGW-14R 11 5.0000**Thallium, total ug/L LGW-14R 11 1.0000**Total dissolved solids mg/L LGW-14R 11 195.4545 9.3420 251.4719 276.6753 256.1775Total organic carbon (toc) mg/L LGW-14R 11 1.0000**Vanadium, total ug/L LGW-14R 11 3.0000**Zinc, total ug/L LGW-14R 10 5.4000**Antimony, total ug/L LGW-2 21 2.0000**Arsenic, total ug/L LGW-2 21 5.0000**Barium, total ug/L LGW-2 20 117.4500 35.3873 117.4500 117.4500 347.4674Beryllium, total ug/L LGW-2 21 1.0000**Cadmium, total ug/L LGW-2 21 1.0000**Chromium, total ug/L LGW-2 21 56.0000**Cobalt, total ug/L LGW-2 20 3.0000**Copper, total ug/L LGW-2 21 9.3000**Iron, total ug/L LGW-2 20 298.7500 370.5724 9722.0707 16722.0707 2707.4704Lead, total ug/L LGW-2 19 5.0000**Manganese, total ug/L LGW-2 20 35.7300 57.2442 168.4037 289.7406 407.8172Nickel, total ug/L LGW-2 21 10.5667 9.4635 10.5667 10.5667 72.0796Selenium, total ug/L LGW-2 20 10.0000**Silver, total ug/L LGW-2 20 50.0000**Sulfate mg/L LGW-2 19 9.4579 5.0769 9.4579 9.4579 42.4577Thallium, total ug/L LGW-2 21 1.0000**Total dissolved solids mg/L LGW-2 20 338.1000 21.5844 510.9469 610.9469 478.3983Total organic carbon (toc) mg/L LGW-2 19 1.0000**Vanadium, total ug/L LGW-2 21 5.4000**Zinc, total ug/L LGW-2 21 8.7762 3.8471 8.7762 8.7762 33.7821Antimony, total ug/L LGW-3R 7 *Arsenic, total ug/L LGW-3R 7 *Barium, total ug/L LGW-3R 7 *Beryllium, total ug/L LGW-3R 7 *Cadmium, total ug/L LGW-3R 7 *Chromium, total ug/L LGW-3R 7 *Cobalt, total ug/L LGW-3R 7 *Copper, total ug/L LGW-3R 7 *Iron, total ug/L LGW-3R 7 *Lead, total ug/L LGW-3R 7 *Manganese, total ug/L LGW-3R 7 *Nickel, total ug/L LGW-3R 7 *Selenium, total ug/L LGW-3R 7 *Silver, total ug/L LGW-3R 7 *Sulfate mg/L LGW-3R 7 *Thallium, total ug/L LGW-3R 7 *Total dissolved solids mg/L LGW-3R 7 *Total organic carbon (toc) mg/L LGW-3R 7 *Vanadium, total ug/L LGW-3R 7 *Zinc, total ug/L LGW-3R 7 *Antimony, total ug/L LGW-4 21 2.0000**Arsenic, total ug/L LGW-4 21 5.0000**Barium, total ug/L LGW-4 20 46.9000 9.3522 58.9859 64.0717 107.6891Beryllium, total ug/L LGW-4 21 1.0000**Cadmium, total ug/L LGW-4 21 1.0000**Chromium, total ug/L LGW-4 21 3.5000**Cobalt, total ug/L LGW-4 20 3.0000**Copper, total ug/L LGW-4 21 4.0000**Iron, total ug/L LGW-4 19 121.6842 73.9557 121.6842 121.6842 602.3965Lead, total ug/L LGW-4 20 5.0000**Manganese, total ug/L LGW-4 20 16.5750 23.1186 16.5750 20.6611 166.8457Nickel, total ug/L LGW-4 21 5.3000**Selenium, total ug/L LGW-4 20 10.0000**Silver, total ug/L LGW-4 20 50.0000**Sulfate mg/L LGW-4 19 5.2842 0.9026 5.2842 5.2842 11.1513Thallium, total ug/L LGW-4 21 1.0000**

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwmim]

Page 37: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Summary Statistics and Intermediate Computationsfor Combined Shewhart-Cusum Control Charts

Constituent Units Well N Mean SD S(i-1) S(i) LimitTotal dissolved solids mg/L LGW-4 20 257.7000 39.5303 338.3092 380.9615 514.6467Total organic carbon (toc) mg/L LGW-4 19 1.0500**Vanadium, total ug/L LGW-4 21 3.0000**Zinc, total ug/L LGW-4 20 5.9100 1.6219 9.1572 8.6308 16.4521Antimony, total ug/L LGW-8R 12 2.0000**Arsenic, total ug/L LGW-8R 12 5.0000**Barium, total ug/L LGW-8R 12 56.5833 4.7186 91.8496 85.8496 87.2542Beryllium, total ug/L LGW-8R 12 1.0000**Cadmium, total ug/L LGW-8R 12 1.0000**Chromium, total ug/L LGW-8R 12 3.0000**Cobalt, total ug/L LGW-8R 12 3.0000**Copper, total ug/L LGW-8R 12 4.0000**Iron, total ug/L LGW-8R 12 60.0000**Lead, total ug/L LGW-8R 12 5.0000**Manganese, total ug/L LGW-8R 12 3.0000**Nickel, total ug/L LGW-8R 12 4.0000**Selenium, total ug/L LGW-8R 12 10.0000**Silver, total ug/L LGW-8R 12 50.0000**Sulfate mg/L LGW-8R 12 5.3000**Thallium, total ug/L LGW-8R 12 1.0000**Total dissolved solids mg/L LGW-8R 12 284.1667 13.1137 410.1549 400.1549 369.4059Total organic carbon (toc) mg/L LGW-8R 12 1.0000**Vanadium, total ug/L LGW-8R 12 3.0000**Zinc, total ug/L LGW-8R 12 11.0000**Antimony, total ug/L MW-15 8 2.0000**Arsenic, total ug/L MW-15 8 5.0000**Barium, total ug/L MW-15 8 27.0000 5.4772 27.0000 27.0000 62.6020Beryllium, total ug/L MW-15 8 1.0000**Cadmium, total ug/L MW-15 8 1.0000**Chromium, total ug/L MW-15 8 4.8000**Cobalt, total ug/L MW-15 8 3.0000**Copper, total ug/L MW-15 8 4.0000**Iron, total ug/L MW-15 7 *Lead, total ug/L MW-15 8 5.0000**Manganese, total ug/L MW-15 8 42.3875 76.4626 42.3875 42.3875 539.3945Nickel, total ug/L MW-15 8 4.0000**Selenium, total ug/L MW-15 8 17.0000**Silver, total ug/L MW-15 8 50.0000**Sulfate mg/L MW-15 8 5.8625 1.1843 12.7688 17.7220 13.5608Thallium, total ug/L MW-15 8 1.0000**Total dissolved solids mg/L MW-15 8 277.5000 19.0863 277.5000 300.9137 401.5608Total organic carbon (toc) mg/L MW-15 8 1.0113 0.0360 1.0113 1.0113 1.2454Vanadium, total ug/L MW-15 8 3.3000**Zinc, total ug/L MW-15 7 *Antimony, total ug/L MW-16 8 2.0000**Arsenic, total ug/L MW-16 8 5.0000**Barium, total ug/L MW-16 8 66.5000 13.9898 66.5000 66.5000 157.4336Beryllium, total ug/L MW-16 8 1.0000**Cadmium, total ug/L MW-16 8 1.0000**Chromium, total ug/L MW-16 8 3.0000**Cobalt, total ug/L MW-16 8 3.0000**Copper, total ug/L MW-16 8 15.0000**Iron, total ug/L MW-16 8 104.0000 73.8357 104.0000 104.0000 583.9322Lead, total ug/L MW-16 8 5.0000**Manganese, total ug/L MW-16 8 13.0125 13.0757 13.0125 13.0125 98.0042Nickel, total ug/L MW-16 8 4.0000**Selenium, total ug/L MW-16 8 16.0000**Silver, total ug/L MW-16 8 50.0000**Sulfate mg/L MW-16 8 16.3125 7.3724 16.3125 16.3125 64.2333Thallium, total ug/L MW-16 8 1.0000**Total dissolved solids mg/L MW-16 8 241.2500 13.5620 241.2500 241.2500 329.4032Total organic carbon (toc) mg/L MW-16 8 1.1813 0.3359 1.1813 1.1813 3.3644Vanadium, total ug/L MW-16 8 3.0000**Zinc, total ug/L MW-16 8 6.7625 3.1405 6.7625 6.7625 27.1757Antimony, total ug/L MW-17 8 2.0000**Arsenic, total ug/L MW-17 8 5.0000**Barium, total ug/L MW-17 8 33.6250 24.5993 54.9521 49.7278 193.5204Beryllium, total ug/L MW-17 8 1.0000**Cadmium, total ug/L MW-17 8 1.0000**Chromium, total ug/L MW-17 8 3.0000**Cobalt, total ug/L MW-17 8 3.0000**Copper, total ug/L MW-17 8 4.0000**Iron, total ug/L MW-17 8 169.5000 193.3664 169.5000 169.5000 1426.3817Lead, total ug/L MW-17 8 5.0000**Manganese, total ug/L MW-17 8 27.0125 39.0389 27.0125 27.0125 280.7651Nickel, total ug/L MW-17 8 4.0000**

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwmim]

Page 38: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Summary Statistics and Intermediate Computationsfor Combined Shewhart-Cusum Control Charts

Constituent Units Well N Mean SD S(i-1) S(i) LimitSelenium, total ug/L MW-17 8 12.0000**Silver, total ug/L MW-17 8 50.0000**Sulfate mg/L MW-17 8 6.6375 2.6854 11.3689 17.0460 24.0925Thallium, total ug/L MW-17 8 1.0000**Total dissolved solids mg/L MW-17 8 188.6250 61.7436 188.6250 208.2564 589.9582Total organic carbon (toc) mg/L MW-17 8 1.0438 0.0904 1.0438 1.0438 1.6313Vanadium, total ug/L MW-17 8 3.0000**Zinc, total ug/L MW-17 8 5.5375 1.1698 5.5375 5.5375 13.1411Antimony, total ug/L MW-19 8 2.0000**Arsenic, total ug/L MW-19 8 5.0000**Barium, total ug/L MW-19 8 47.8750 22.4018 92.3215 47.8750 193.4865Beryllium, total ug/L MW-19 8 1.0000**Cadmium, total ug/L MW-19 8 1.0000**Chromium, total ug/L MW-19 8 3.8000**Cobalt, total ug/L MW-19 8 3.0000**Copper, total ug/L MW-19 8 4.0000**Iron, total ug/L MW-19 8 253.0000 244.1335 253.0000 253.0000 1839.8674Lead, total ug/L MW-19 8 5.0000**Manganese, total ug/L MW-19 8 51.1125 75.4543 51.1125 51.1125 541.5658Nickel, total ug/L MW-19 8 5.2000**Selenium, total ug/L MW-19 8 18.0000**Silver, total ug/L MW-19 8 50.0000**Sulfate mg/L MW-19 8 6.1250 2.0457 6.1250 6.1250 19.4222Thallium, total ug/L MW-19 8 1.0000**Total dissolved solids mg/L MW-19 8 228.7500 52.7629 228.7500 228.7500 571.7092Total organic carbon (toc) mg/L MW-19 8 1.0875 0.1529 1.0875 1.0875 2.0817Vanadium, total ug/L MW-19 8 3.0000**Zinc, total ug/L MW-19 8 7.1000 3.5428 7.1000 7.1000 30.1282

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwmim]

* - Insufficient Data** - Detection Frequency < 25%*** - Zero Variance

Page 39: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

LGW-14RAntimony, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.200.400.600.801.001.201.401.601.802.00

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-14RArsenic, total

Nonparametric Prediction Limit

ug/L

YearManual ND

0.000.501.001.502.002.503.003.504.004.505.00

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-14RBarium, total

Normal Control Limit

ug/L

Year

0.20.40.60.80.

100.120.140.160.180.200.

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-14RBeryllium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.100.200.300.400.500.600.700.800.901.00

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-14RCadmium, total

Nonparametric Prediction Limit

ug/L

YearManual ND

0.000.100.200.300.400.500.600.700.800.901.00

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-14RChromium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.5.

10.15.20.25.30.35.40.45.50.

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-14RCobalt, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-14RCopper, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-14RIron, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.200.400.600.800.

1000.1200.1400.1600.1800.2000.

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-14RLead, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-14RManganese, total

Normal Control Limit

ug/L

YearMedian ND

0.20.40.60.80.

100.120.140.160.180.200.

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-14RNickel, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.5.

10.15.20.25.30.35.40.45.50.

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwmim]

Page 40: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

LGW-14RSelenium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-14RSilver, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.5.

10.15.20.25.30.35.40.45.50.

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-14RSulfate

Nonparametric Prediction Limit

mg/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-14RThallium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.100.200.300.400.500.600.700.800.901.00

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-14RTotal dissolved solidsNormal Control Limit

mg/L

Year

0.50.

100.150.200.250.300.350.400.450.500.

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-14RTotal organic carbon (toc)

Nonparametric Prediction Limit

mg/L

YearMedian ND

0.000.100.200.300.400.500.600.700.800.901.00

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-14RVanadium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-14RZinc, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.10.20.30.40.50.60.70.80.90.

100.

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwmim]

Page 41: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

LGW-2Antimony, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-2Arsenic, total

Verified Hit / Nonparametric Prediction Limit

ug/L

YearManual ND

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-2Barium, total

Normal Control Limit

ug/L

Year

0.50.

100.150.200.250.300.350.400.450.500.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-2Beryllium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-2Cadmium, total

Nonparametric Prediction Limit

ug/L

YearManual ND

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-2Chromium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.10.20.30.40.50.60.70.80.90.

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-2Cobalt, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-2Copper, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-2Iron, total

Verified Exceedance / Normal Control Limit

ug/L

YearMedian ND

0.

2000.

4000.

6000.

8000.

10000.

12000.

14000.

16000.

18000.

20000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-2Lead, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-2Manganese, total

Normal Control Limit

ug/L

Year

0.50.

100.150.200.250.300.350.400.450.500.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-2Nickel, total

Normal Control Limit

ug/L

YearMedian ND

0.10.20.30.40.50.60.70.80.90.

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwmim]

Page 42: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

LGW-2Selenium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-2Silver, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.5.

10.15.20.25.30.35.40.45.50.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-2Sulfate

Normal Control Limit

mg/L

YearMedian ND

0.5.

10.15.20.25.30.35.40.45.50.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-2Thallium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-2Total dissolved solids

Verified Exceedance / Normal Control Limit

mg/L

Year

0.100.200.300.400.500.600.700.800.900.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-2Total organic carbon (toc)

Verified Hit / Nonparametric Prediction Limit

mg/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-2Vanadium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-2Zinc, total

Normal Control Limit

ug/L

YearMedian ND

0.5.

10.15.20.25.30.35.40.45.50.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwmim]

Page 43: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

LGW-3RAntimony, total

ug/L

Month / Year Median ND

0.000.200.400.600.801.001.201.401.601.802.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-3RArsenic, total

ug/L

Month / Year Manual ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-3RBarium, total

ug/L

Month / Year

0.10.20.30.40.50.60.70.80.90.

100.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-3RBeryllium, total

ug/L

Month / Year Median ND

0.000.100.200.300.400.500.600.700.800.901.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-3RCadmium, total

ug/L

Month / Year Manual ND

0.000.100.200.300.400.500.600.700.800.901.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-3RChromium, total

ug/L

Month / Year Median ND

0.01.02.03.04.05.06.07.08.09.0

10.0

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-3RCobalt, total

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-3RCopper, total

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-3RIron, total

ug/L

Month / Year Median ND

0.500.

1000.1500.2000.2500.3000.3500.4000.4500.5000.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-3RLead, total

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-3RManganese, total

ug/L

Month / Year Median ND

0.50.

100.150.200.250.300.350.400.450.500.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-3RNickel, total

ug/L

Month / Year Median ND

0.01.02.03.04.05.06.07.08.09.0

10.0

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwmim]

Page 44: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

LGW-3RSelenium, total

ug/L

Month / Year Median ND

0.02.04.06.08.0

10.012.014.016.018.020.0

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-3RSilver, total

ug/L

Month / Year Median ND

0.5.

10.15.20.25.30.35.40.45.50.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-3RSulfate

mg/L

Month / Year Median ND

0.01.02.03.04.05.06.07.08.09.0

10.0

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-3RThallium, total

ug/L

Month / Year Median ND

0.000.100.200.300.400.500.600.700.800.901.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-3RTotal dissolved solids

mg/L

Month / Year

0.50.

100.150.200.250.300.350.400.450.500.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-3RTotal organic carbon (toc)

mg/L

Month / Year Median ND

0.000.200.400.600.801.001.201.401.601.802.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-3RVanadium, total

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-3RZinc, total

ug/L

Month / Year Median ND

0.20.40.60.80.

100.120.140.160.180.200.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwmim]

Page 45: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

LGW-4Antimony, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-4Arsenic, total

Nonparametric Prediction Limit

ug/L

YearManual ND

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-4Barium, total

Normal Control Limit

ug/L

Year

0.20.40.60.80.

100.120.140.160.180.200.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-4Beryllium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-4Cadmium, total

Nonparametric Prediction Limit

ug/L

YearManual ND

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-4Chromium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-4Cobalt, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-4Copper, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-4Iron, total

Normal Control Limit

ug/L

YearMedian ND

0.200.400.600.800.

1000.1200.1400.1600.1800.2000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-4Lead, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-4Manganese, total

Normal Control Limit

ug/L

Year

0.20.40.60.80.

100.120.140.160.180.200.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-4Nickel, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.5.

10.15.20.25.30.35.40.45.50.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwmim]

Page 46: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

LGW-4Selenium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-4Silver, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.5.

10.15.20.25.30.35.40.45.50.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-4Sulfate

Normal Control Limit

mg/L

YearMedian ND

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-4Thallium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-4Total dissolved solidsNormal Control Limit

mg/L

Year

0.100.200.300.400.500.600.700.800.900.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-4Total organic carbon (toc)

Nonparametric Prediction Limit

mg/L

YearMedian ND

0.000.200.400.600.801.001.201.401.601.802.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-4Vanadium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-4Zinc, total

Normal Control Limit

ug/L

YearMedian ND

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwmim]

Page 47: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

LGW-8RAntimony, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.200.400.600.801.001.201.401.601.802.00

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-8RArsenic, total

Nonparametric Prediction Limit

ug/L

YearManual ND

0.000.501.001.502.002.503.003.504.004.505.00

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-8RBarium, total

Normal Control Limit

ug/L

Year

0.10.20.30.40.50.60.70.80.90.

100.

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-8RBeryllium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.100.200.300.400.500.600.700.800.901.00

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-8RCadmium, total

Nonparametric Prediction Limit

ug/L

YearManual ND

0.000.100.200.300.400.500.600.700.800.901.00

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-8RChromium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-8RCobalt, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-8RCopper, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-8RIron, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.10.20.30.40.50.60.70.80.90.

100.

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-8RLead, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-8RManganese, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.5.

10.15.20.25.30.35.40.45.50.

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-8RNickel, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwmim]

Page 48: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

LGW-8RSelenium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-8RSilver, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.5.

10.15.20.25.30.35.40.45.50.

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-8RSulfate

Nonparametric Prediction Limit

mg/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-8RThallium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.100.200.300.400.500.600.700.800.901.00

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-8RTotal dissolved solids

Verified Exceedance / Normal Control Limit

mg/L

Year

0.50.

100.150.200.250.300.350.400.450.500.

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-8RTotal organic carbon (toc)

Nonparametric Prediction Limit

mg/L

YearMedian ND

0.000.100.200.300.400.500.600.700.800.901.00

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-8RVanadium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-8RZinc, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.02.04.06.08.0

10.012.014.016.018.020.0

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwmim]

Page 49: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

MW-15Antimony, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.200.400.600.801.001.201.401.601.802.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-15Arsenic, total

Nonparametric Prediction Limit

ug/L

Month / Year Manual ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-15Barium, total

Normal Control Limit

ug/L

Month / Year

0.10.20.30.40.50.60.70.80.90.

100.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-15Beryllium, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.100.200.300.400.500.600.700.800.901.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-15Cadmium, total

Nonparametric Prediction Limit

ug/L

Month / Year Manual ND

0.000.200.400.600.801.001.201.401.601.802.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-15Chromium, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-15Cobalt, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-15Copper, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-15Iron, total

ug/L

Month / Year Median ND

0.200.400.600.800.

1000.1200.1400.1600.1800.2000.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-15Lead, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-15Manganese, total

Normal Control Limit

ug/L

Month / Year Median ND

0.500.

1000.1500.2000.2500.3000.3500.4000.4500.5000.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-15Nickel, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.01.02.03.04.05.06.07.08.09.0

10.0

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwmim]

Page 50: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

MW-15Selenium, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.02.04.06.08.0

10.012.014.016.018.020.0

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-15Silver, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.5.

10.15.20.25.30.35.40.45.50.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-15Sulfate

Normal Control Limit

mg/L

Month / Year Median ND

0.02.04.06.08.0

10.012.014.016.018.020.0

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-15Thallium, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.100.200.300.400.500.600.700.800.901.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-15Total dissolved solidsNormal Control Limit

mg/L

Month / Year

0.50.

100.150.200.250.300.350.400.450.500.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-15Total organic carbon (toc)

Normal Control Limit

mg/L

Month / Year Median ND

0.000.200.400.600.801.001.201.401.601.802.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-15Vanadium, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-15Zinc, total

ug/L

Month / Year Median ND

0.5.

10.15.20.25.30.35.40.45.50.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwmim]

Page 51: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

MW-16Antimony, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.200.400.600.801.001.201.401.601.802.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-16Arsenic, total

Nonparametric Prediction Limit

ug/L

Month / Year Manual ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-16Barium, total

Normal Control Limit

ug/L

Month / Year

0.20.40.60.80.

100.120.140.160.180.200.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-16Beryllium, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.100.200.300.400.500.600.700.800.901.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-16Cadmium, total

Nonparametric Prediction Limit

ug/L

Month / Year Manual ND

0.000.100.200.300.400.500.600.700.800.901.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-16Chromium, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-16Cobalt, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-16Copper, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.02.04.06.08.0

10.012.014.016.018.020.0

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-16Iron, total

Normal Control Limit

ug/L

Month / Year Median ND

0.100.200.300.400.500.600.700.800.900.

1000.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-16Lead, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-16Manganese, total

Normal Control Limit

ug/L

Month / Year Median ND

0.10.20.30.40.50.60.70.80.90.

100.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-16Nickel, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwmim]

Page 52: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

MW-16Selenium, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.02.04.06.08.0

10.012.014.016.018.020.0

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-16Silver, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.5.

10.15.20.25.30.35.40.45.50.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-16Sulfate

Significant Trend / Normal Control Limit

mg/L

Month / Year Median ND

0.10.20.30.40.50.60.70.80.90.

100.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-16Thallium, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.100.200.300.400.500.600.700.800.901.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-16Total dissolved solidsNormal Control Limit

mg/L

Month / Year

0.50.

100.150.200.250.300.350.400.450.500.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-16Total organic carbon (toc)

Normal Control Limit

mg/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-16Vanadium, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-16Zinc, total

Normal Control Limit

ug/L

Month / Year Median ND

0.5.

10.15.20.25.30.35.40.45.50.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwmim]

Page 53: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

MW-17Antimony, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.200.400.600.801.001.201.401.601.802.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-17Arsenic, total

Nonparametric Prediction Limit

ug/L

Month / Year Manual ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-17Barium, total

Normal Control Limit

ug/L

Month / Year

0.20.40.60.80.

100.120.140.160.180.200.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-17Beryllium, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.100.200.300.400.500.600.700.800.901.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-17Cadmium, total

Nonparametric Prediction Limit

ug/L

Month / Year Manual ND

0.000.100.200.300.400.500.600.700.800.901.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-17Chromium, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-17Cobalt, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-17Copper, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-17Iron, total

Normal Control Limit

ug/L

Month / Year Median ND

0.200.400.600.800.

1000.1200.1400.1600.1800.2000.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-17Lead, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-17Manganese, total

Normal Control Limit

ug/L

Month / Year

0.50.

100.150.200.250.300.350.400.450.500.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-17Nickel, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwmim]

Page 54: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

MW-17Selenium, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.02.04.06.08.0

10.012.014.016.018.020.0

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-17Silver, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.5.

10.15.20.25.30.35.40.45.50.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-17Sulfate

Significant Trend / Normal Control Limit

mg/L

Month / Year Median ND

0.5.

10.15.20.25.30.35.40.45.50.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-17Thallium, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.100.200.300.400.500.600.700.800.901.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-17Total dissolved solidsNormal Control Limit

mg/L

Month / Year

0.100.200.300.400.500.600.700.800.900.

1000.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-17Total organic carbon (toc)

Normal Control Limit

mg/L

Month / Year Median ND

0.000.200.400.600.801.001.201.401.601.802.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-17Vanadium, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-17Zinc, total

Normal Control Limit

ug/L

Month / Year Median ND

0.02.04.06.08.0

10.012.014.016.018.020.0

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwmim]

Page 55: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

MW-19Antimony, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.200.400.600.801.001.201.401.601.802.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-19Arsenic, total

Nonparametric Prediction Limit

ug/L

Month / Year Manual ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-19Barium, total

Normal Control Limit

ug/L

Month / Year

0.20.40.60.80.

100.120.140.160.180.200.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-19Beryllium, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.100.200.300.400.500.600.700.800.901.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-19Cadmium, total

Nonparametric Prediction Limit

ug/L

Month / Year Manual ND

0.000.100.200.300.400.500.600.700.800.901.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-19Chromium, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-19Cobalt, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-19Copper, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-19Iron, total

Normal Control Limit

ug/L

Month / Year Median ND

0.200.400.600.800.

1000.1200.1400.1600.1800.2000.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-19Lead, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-19Manganese, total

Normal Control Limit

ug/L

Month / Year Median ND

0.100.200.300.400.500.600.700.800.900.

1000.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-19Nickel, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.01.02.03.04.05.06.07.08.09.0

10.0

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwmim]

Page 56: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

MW-19Selenium, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.02.04.06.08.0

10.012.014.016.018.020.0

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-19Silver, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.5.

10.15.20.25.30.35.40.45.50.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-19Sulfate

Normal Control Limit

mg/L

Month / Year Median ND

0.02.04.06.08.0

10.012.014.016.018.020.0

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-19Thallium, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.100.200.300.400.500.600.700.800.901.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-19Total dissolved solidsNormal Control Limit

mg/L

Month / Year

0.100.200.300.400.500.600.700.800.900.

1000.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-19Total organic carbon (toc)

Normal Control Limit

mg/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-19Vanadium, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-19Zinc, total

Normal Control Limit

ug/L

Month / Year Median ND

0.5.

10.15.20.25.30.35.40.45.50.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwmim]

Page 57: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

False Positive and False Negative Rates for Current

Intra-Well Control Charts Monitoring Program

Power

%

0.

10.

20.

30.

40.

50.

60.

70.

80.

90.

100.

S. D. Units

0.0 0.5 1.0 1.5 2.0 2.5 3.0 3.5 4.0 4.5 5.0

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwmim]

Page 58: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Summary Statistics and Intermediate Computationsfor Combined Shewhart-Cusum Control Charts

Constituent Units Well N Mean SD S(i-1) S(i) LimitAntimony, total ug/L MW-10N 19 2.0000**Arsenic, total ug/L MW-10N 19 5.0000**Barium, total ug/L MW-10N 18 34.8889 5.4437 34.8889 34.8889 70.2730Beryllium, total ug/L MW-10N 19 1.0000**Cadmium, total ug/L MW-10N 19 1.0000**Chloride mg/L MW-10N 18 5.7444 0.4018 5.7444 5.7444 8.3561Chromium, total ug/L MW-10N 19 3.0000**Cobalt, total ug/L MW-10N 18 3.0000**Copper, total ug/L MW-10N 19 4.0000**Iron, total ug/L MW-10N 18 775.0000 583.7329 775.0000 775.0000 4569.2640Lead, total ug/L MW-10N 18 5.0000**Manganese, total ug/L MW-10N 17 34.5882 9.7792 34.5882 34.5882 98.1529Nickel, total ug/L MW-10N 19 4.1000**Selenium, total ug/L MW-10N 18 10.0000**Silver, total ug/L MW-10N 18 50.0000**Sulfate mg/L MW-10N 18 11.0000**Thallium, total ug/L MW-10N 19 1.0000**Total dissolved solids mg/L MW-10N 18 295.2778 33.2757 295.2778 295.2778 511.5697Total organic carbon (toc) mg/L MW-10N 17 5.1265 0.8777 5.1265 5.1265 10.8315Vanadium, total ug/L MW-10N 19 3.0000**Zinc, total ug/L MW-10N 18 5.1556 0.4382 5.1556 5.1556 8.0039Antimony, total ug/L MW-11N 20 2.0000**Arsenic, total ug/L MW-11N 20 5.0000**Barium, total ug/L MW-11N 19 75.5789 32.9668 75.5789 75.5789 289.8634Beryllium, total ug/L MW-11N 20 1.0000**Cadmium, total ug/L MW-11N 20 1.0000**Chloride mg/L MW-11N 19 3.0000**Chromium, total ug/L MW-11N 20 3.0000**Cobalt, total ug/L MW-11N 19 3.0000**Copper, total ug/L MW-11N 20 6.6000**Iron, total ug/L MW-11N 19 100.0526 95.7198 100.0526 100.0526 722.2312Lead, total ug/L MW-11N 18 5.0000**Manganese, total ug/L MW-11N 19 12.1316 13.3373 12.1316 12.1316 98.8243Nickel, total ug/L MW-11N 20 9.7000**Selenium, total ug/L MW-11N 19 10.0000**Silver, total ug/L MW-11N 19 50.0000**Sulfate mg/L MW-11N 19 5.0000**Thallium, total ug/L MW-11N 20 1.0000**Total dissolved solids mg/L MW-11N 19 195.6842 15.8642 195.6842 195.6842 298.8014Total organic carbon (toc) mg/L MW-11N 18 3.8500**Vanadium, total ug/L MW-11N 20 3.8000**Zinc, total ug/L MW-11N 20 17.7700 4.6527 20.5105 17.7700 48.0124Antimony, total ug/L MW-1N 16 2.0000**Arsenic, total ug/L MW-1N 16 5.0000**Barium, total ug/L MW-1N 15 41.4667 5.8293 73.9507 68.1120 79.3572Beryllium, total ug/L MW-1N 16 1.0000**Cadmium, total ug/L MW-1N 16 1.0000**Chloride mg/L MW-1N 15 4.6667 1.0788 4.6667 4.6667 11.6789Chromium, total ug/L MW-1N 16 3.0000**Cobalt, total ug/L MW-1N 15 4.2000**Copper, total ug/L MW-1N 16 4.0000**Iron, total ug/L MW-1N 15 464.6667 331.9610 464.6667 464.6667 2622.4131Lead, total ug/L MW-1N 15 5.0000**Manganese, total ug/L MW-1N 15 254.2667 133.2192 254.2667 254.2667 1120.1914Nickel, total ug/L MW-1N 16 13.4250 8.4371 13.4250 13.4250 68.2662Selenium, total ug/L MW-1N 15 10.0000**Silver, total ug/L MW-1N 15 50.0000**Sulfate mg/L MW-1N 15 7.5733 2.4403 14.2556 11.3521 23.4351Thallium, total ug/L MW-1N 16 1.0000**Total dissolved solids mg/L MW-1N 15 240.0667 25.2147 240.0667 240.0667 403.9622Total organic carbon (toc) mg/L MW-1N 14 1.6000**Vanadium, total ug/L MW-1N 16 3.0000**Zinc, total ug/L MW-1N 16 21.9625 18.7761 143.3058 154.2612 144.0072Antimony, total ug/L MW-20 8 2.0000**Arsenic, total ug/L MW-20 8 5.0000**Barium, total ug/L MW-20 8 102.1250 22.8438 102.1250 102.1250 250.6097Beryllium, total ug/L MW-20 8 1.2000**Cadmium, total ug/L MW-20 8 1.0000**Chloride mg/L MW-20 9 5.3667 0.5362 5.3667 5.3667 8.8519Chromium, total ug/L MW-20 8 3.2500 0.3854 3.2500 3.2500 5.7554Cobalt, total ug/L MW-20 8 3.0000**Copper, total ug/L MW-20 8 4.0000**Iron, total ug/L MW-20 8 738.7500 971.9706 738.7500 738.7500 7056.5587Lead, total ug/L MW-20 8 7.3000**Manganese, total ug/L MW-20 8 403.8750 371.5552 403.8750 403.8750 2818.9838Nickel, total ug/L MW-20 8 4.1375 0.2669 4.1375 4.1375 5.8725

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 59: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Summary Statistics and Intermediate Computationsfor Combined Shewhart-Cusum Control Charts

Constituent Units Well N Mean SD S(i-1) S(i) LimitSelenium, total ug/L MW-20 8 10.0000**Silver, total ug/L MW-20 8 50.0000**Sulfate mg/L MW-20 7 *Thallium, total ug/L MW-20 8 1.0000**Total dissolved solids mg/L MW-20 8 361.2500 61.7454 361.2500 361.2500 762.5954Total organic carbon (toc) mg/L MW-20 8 1.0000**Vanadium, total ug/L MW-20 8 3.2750 0.7778 3.2750 3.2750 8.3308Zinc, total ug/L MW-20 8 7.9250 3.0886 7.9250 7.9250 28.0007

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

* - Insufficient Data** - Detection Frequency < 25%*** - Zero Variance

Page 60: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

MW-10NAntimony, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-10NArsenic, total

Nonparametric Prediction Limit

ug/L

YearManual ND

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-10NBarium, total

Normal Control Limit

ug/L

Year

0.10.20.30.40.50.60.70.80.90.

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-10NBeryllium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-10NCadmium, total

Nonparametric Prediction Limit

ug/L

YearManual ND

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-10NChloride

Normal Control Limit

mg/L

Year

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-10NChromium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-10NCobalt, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-10NCopper, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-10NIron, total

Normal Control Limit

ug/L

Year

0.500.

1000.1500.2000.2500.3000.3500.4000.4500.5000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-10NLead, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-10NManganese, total

Normal Control Limit

ug/L

Year

0.10.20.30.40.50.60.70.80.90.

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 61: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

MW-10NNickel, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.5.

10.15.20.25.30.35.40.45.50.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-10NSelenium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-10NSilver, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.5.

10.15.20.25.30.35.40.45.50.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-10NSulfate

Nonparametric Prediction Limit

mg/L

YearMedian ND

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-10NThallium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-10NTotal dissolved solidsNormal Control Limit

mg/L

Year

0.100.200.300.400.500.600.700.800.900.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-10NTotal organic carbon (toc)

Normal Control Limit

mg/L

Year

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-10NVanadium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-10NZinc, total

Normal Control Limit

ug/L

YearMedian ND

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 62: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

MW-11NAntimony, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-11NArsenic, total

Nonparametric Prediction Limit

ug/L

YearManual ND

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-11NBarium, total

Normal Control Limit

ug/L

Year

0.50.

100.150.200.250.300.350.400.450.500.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-11NBeryllium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-11NCadmium, total

Nonparametric Prediction Limit

ug/L

YearManual ND

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-11NChloride

Nonparametric Prediction Limit

mg/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-11NChromium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-11NCobalt, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-11NCopper, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-11NIron, total

Normal Control Limit

ug/L

YearMedian ND

0.100.200.300.400.500.600.700.800.900.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-11NLead, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-11NManganese, total

Normal Control Limit

ug/L

YearMedian ND

0.10.20.30.40.50.60.70.80.90.

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 63: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

MW-11NNickel, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.5.

10.15.20.25.30.35.40.45.50.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-11NSelenium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-11NSilver, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.5.

10.15.20.25.30.35.40.45.50.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-11NSulfate

Nonparametric Prediction Limit

mg/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-11NThallium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-11NTotal dissolved solidsNormal Control Limit

mg/L

Year

0.50.

100.150.200.250.300.350.400.450.500.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-11NTotal organic carbon (toc)

Nonparametric Prediction Limit

mg/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-11NVanadium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-11NZinc, total

Normal Control Limit

ug/L

YearMedian ND

0.5.

10.15.20.25.30.35.40.45.50.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 64: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

MW-1NAntimony, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-1NArsenic, total

Nonparametric Prediction Limit

ug/L

YearManual ND

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-1NBarium, total

Normal Control Limit

ug/L

Year

0.10.20.30.40.50.60.70.80.90.

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-1NBeryllium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-1NCadmium, total

Nonparametric Prediction Limit

ug/L

YearManual ND

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-1NChloride

Normal Control Limit

mg/L

Year

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-1NChromium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-1NCobalt, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-1NCopper, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-1NIron, total

Normal Control Limit

ug/L

YearMedian ND

0.500.

1000.1500.2000.2500.3000.3500.4000.4500.5000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-1NLead, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-1NManganese, total

Normal Control Limit

ug/L

Year

0.200.400.600.800.

1000.1200.1400.1600.1800.2000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 65: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

MW-1NNickel, total

Normal Control Limit

ug/L

YearMedian ND

0.10.20.30.40.50.60.70.80.90.

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-1NSelenium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-1NSilver, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.5.

10.15.20.25.30.35.40.45.50.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-1NSulfate

Significant Trend / Normal Control Limit

mg/L

Year

0.5.

10.15.20.25.30.35.40.45.50.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-1NThallium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-1NTotal dissolved solidsNormal Control Limit

mg/L

Year

0.50.

100.150.200.250.300.350.400.450.500.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-1NTotal organic carbon (toc)

Nonparametric Prediction Limit

mg/L

YearMedian ND

0.000.200.400.600.801.001.201.401.601.802.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-1NVanadium, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-1NZinc, total

Significant Trend / Normal Control Limit

ug/L

YearMedian ND

0.20.40.60.80.

100.120.140.160.180.200.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 66: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

MW-20Antimony, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.200.400.600.801.001.201.401.601.802.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-20Arsenic, total

Nonparametric Prediction Limit

ug/L

Month / Year Manual ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-20Barium, total

Normal Control Limit

ug/L

Month / Year

0.50.

100.150.200.250.300.350.400.450.500.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-20Beryllium, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.200.400.600.801.001.201.401.601.802.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-20Cadmium, total

Nonparametric Prediction Limit

ug/L

Month / Year Manual ND

0.000.100.200.300.400.500.600.700.800.901.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-20Chloride

Normal Control Limit

mg/L

Month / Year

0.02.04.06.08.0

10.012.014.016.018.020.0

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-20Chromium, total

Normal Control Limit

ug/L

Month / Year Median ND

0.02.04.06.08.0

10.012.014.016.018.020.0

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-20Cobalt, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-20Copper, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-20Iron, total

Normal Control Limit

ug/L

Month / Year

0.

1000.

2000.

3000.

4000.

5000.

6000.

7000.

8000.

9000.

10000.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-20Lead, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.01.02.03.04.05.06.07.08.09.0

10.0

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-20Manganese, total

Normal Control Limit

ug/L

Month / Year

0.500.

1000.1500.2000.2500.3000.3500.4000.4500.5000.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 67: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Control Charts

MW-20Nickel, total

Normal Control Limit

ug/L

Month / Year Median ND

0.01.02.03.04.05.06.07.08.09.0

10.0

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-20Selenium, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.01.02.03.04.05.06.07.08.09.0

10.0

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-20Silver, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.5.

10.15.20.25.30.35.40.45.50.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-20Sulfate

mg/L

Month / Year Median ND

0.10.20.30.40.50.60.70.80.90.

100.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-20Thallium, total

Nonparametric Prediction Limit

ug/L

Month / Year Median ND

0.000.100.200.300.400.500.600.700.800.901.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-20Total dissolved solidsNormal Control Limit

mg/L

Month / Year

0.100.200.300.400.500.600.700.800.900.

1000.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-20Total organic carbon (toc)

Nonparametric Prediction Limit

mg/L

Month / Year Median ND

0.000.100.200.300.400.500.600.700.800.901.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-20Vanadium, total

Normal Control Limit

ug/L

Month / Year Median ND

0.01.02.03.04.05.06.07.08.09.0

10.0

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-20Zinc, total

Normal Control Limit

ug/L

Month / Year Median ND

0.5.

10.15.20.25.30.35.40.45.50.

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 68: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

False Positive and False Negative Rates for Current

Intra-Well Control Charts Monitoring Program

Power

%

0.

10.

20.

30.

40.

50.

60.

70.

80.

90.

100.

S. D. Units

0.0 0.5 1.0 1.5 2.0 2.5 3.0 3.5 4.0 4.5 5.0

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 69: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Summary Statistics and Intermediate Computationsfor Combined Shewhart-Cusum Control Charts

Constituent Units Well N Mean SD S(i-1) S(i) Limit Total dissolved solids mg/L LGW-14R 11 195.4545 9.3420 276.6753 276.6753 256.1775Zinc, total ug/L LGW-14R 10 5.4000 **Sulfate mg/L MW-15 8 5.8625 1.1843 17.7220 16.7220 13.5608Zinc, total ug/L MW-1N 16 21.9625 18.7761 154.2612 154.2612 144.0072

Prepared by: Otter Creek Environmental

Analysis prepared on: November 2018Eco-Vista [gw]

* - Insufficient Data** - Detection Frequency < 25%*** - Zero Variance

Page 70: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Intra-Well Sublist Control Charts

LGW-14RTotal dissolved solidsNormal Control Limit

mg/L

Year

0.50.

100.150.200.250.300.350.400.450.500.

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

LGW-14RZinc, total

Nonparametric Prediction Limit

ug/L

YearMedian ND

0.10.20.30.40.50.60.70.80.90.

100.

09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-15Sulfate

Normal Control Limit

mg/L

Month / Year Median ND

0.02.04.06.08.0

10.012.014.016.018.020.0

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

MW-1NZinc, total

Significant Trend / Normal Control Limit

ug/L

YearMedian ND

0.20.40.60.80.

100.120.140.160.180.200.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Backgnd

Samples

CUSUM

Limit

Detect

ND

CUSUM

Outlier

Man. outlier

Verify

Prepared by: Otter Creek Environmental

Analysis prepared on: November 2018Eco-Vista [gw]

Page 71: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Ground Water Statistics for Eco-Vista Sanitary Landfill Third Quarter Monitoring Event In 2018

C:\Otter Creek Environmental\Arkansas\Eco-Vista\ecovistaq318RRRR.doc December 14, 2018

Attachment D

95% LCLs for VOC Detections – Assessment Wells

Page 72: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Confidence Intervals for Comparing the Mean of the Last4 Measurements to an Assessment Monitoring Standard

Constituent Units Well N Mean SD Factor 95% LCL 95% UCL Standard 1,1-dichloroethane ug/L LGW-10 4 1.650 0.370 1.176 1.215 2.085 2.4001,2-dichloroethane ug/L LGW-10 4 0.500 0.000 1.176 0.500 0.500 5.0001,2-dichloropropane ug/L LGW-10 4 0.500 0.000 1.176 0.500 0.500 5.0001,4-dichlorobenzene ug/L LGW-10 4 3.800 2.249 1.176 1.154 6.446 75.000Acetone ug/L LGW-10 4 12.300 10.600 1.176 0.000 24.769 12000.000Benzene ug/L LGW-10 4 2.150 0.794 1.176 1.216 3.084 5.000Bis(2-ethylhexyl) phthalate ug/L LGW-10 4 4.750 0.000 1.176 4.750 4.750 6.000Carbon disulfide ug/L LGW-10 4 0.500 0.000 1.176 0.500 0.500 720.000Chlorobenzene ug/L LGW-10 4 0.675 0.350 1.176 0.263 1.087 100.000Chloroethane ug/L LGW-10 4 0.500 0.000 1.176 0.500 0.500 21000.000Chloroform ug/L LGW-10 4 0.500 0.000 1.176 0.500 0.500 80.000Cis-1,2-dichloroethene ug/L LGW-10 4 2.050 0.733 1.176 1.188 2.912 70.000Dichlorodifluoromethane ug/L LGW-10 4 1.000 0.000 1.176 1.000 1.000 190.000Ethylbenzene ug/L LGW-10 4 0.500 0.000 1.176 0.500 0.500 700.000Methyl ethyl ketone ug/L LGW-10 4 2.500 0.000 1.176 2.500 2.500 4900.000Methylene chloride ug/L LGW-10 4 0.500 0.000 1.176 0.500 0.500 5.000Tetrachloroethene ug/L LGW-10 4 0.500 0.000 1.176 0.500 0.500 5.000Toluene ug/L LGW-10 4 0.500 0.000 1.176 0.500 0.500 1000.000Total xylenes ug/L LGW-10 4 0.500 0.000 1.176 0.500 0.500 10000.000Trichloroethene ug/L LGW-10 4 0.500 0.000 1.176 0.500 0.500 5.000Trichlorofluoromethane ug/L LGW-10 4 0.500 0.000 1.176 0.500 0.500 1100.000Vinyl chloride ug/L LGW-10 4 0.850 0.404 1.176 0.375 1.325 2.0001,1-dichloroethane ug/L LGW-5 4 0.500 0.000 1.176 0.500 0.500 2.4001,2-dichloroethane ug/L LGW-5 4 0.500 0.000 1.176 0.500 0.500 5.0001,2-dichloropropane ug/L LGW-5 4 0.500 0.000 1.176 0.500 0.500 5.0001,4-dichlorobenzene ug/L LGW-5 4 0.500 0.000 1.176 0.500 0.500 75.000Acetone ug/L LGW-5 4 2.500 0.000 1.176 2.500 2.500 12000.000Benzene ug/L LGW-5 4 0.500 0.000 1.176 0.500 0.500 5.000Bis(2-ethylhexyl) phthalate ug/L LGW-5 4 4.750 0.000 1.176 4.750 4.750 6.000Carbon disulfide ug/L LGW-5 4 0.500 0.000 1.176 0.500 0.500 720.000Chlorobenzene ug/L LGW-5 4 0.500 0.000 1.176 0.500 0.500 100.000Chloroethane ug/L LGW-5 4 0.500 0.000 1.176 0.500 0.500 21000.000Chloroform ug/L LGW-5 4 0.500 0.000 1.176 0.500 0.500 80.000Cis-1,2-dichloroethene ug/L LGW-5 4 0.500 0.000 1.176 0.500 0.500 70.000Dichlorodifluoromethane ug/L LGW-5 4 1.000 0.000 1.176 1.000 1.000 190.000Ethylbenzene ug/L LGW-5 4 0.500 0.000 1.176 0.500 0.500 700.000Methyl ethyl ketone ug/L LGW-5 4 2.500 0.000 1.176 2.500 2.500 4900.000Methylene chloride ug/L LGW-5 4 0.500 0.000 1.176 0.500 0.500 5.000Tetrachloroethene ug/L LGW-5 4 0.500 0.000 1.176 0.500 0.500 5.000Toluene ug/L LGW-5 4 0.500 0.000 1.176 0.500 0.500 1000.000Total xylenes ug/L LGW-5 4 0.500 0.000 1.176 0.500 0.500 10000.000Trichloroethene ug/L LGW-5 4 0.500 0.000 1.176 0.500 0.500 5.000Trichlorofluoromethane ug/L LGW-5 4 0.500 0.000 1.176 0.500 0.500 1100.000Vinyl chloride ug/L LGW-5 4 0.500 0.000 1.176 0.500 0.500 2.0001,1-dichloroethane ug/L LGW-6 4 0.500 0.000 1.176 0.500 0.500 2.4001,2-dichloroethane ug/L LGW-6 4 0.500 0.000 1.176 0.500 0.500 5.0001,2-dichloropropane ug/L LGW-6 4 0.500 0.000 1.176 0.500 0.500 5.0001,4-dichlorobenzene ug/L LGW-6 4 0.500 0.000 1.176 0.500 0.500 75.000Acetone ug/L LGW-6 4 2.500 0.000 1.176 2.500 2.500 12000.000Benzene ug/L LGW-6 4 0.500 0.000 1.176 0.500 0.500 5.000Bis(2-ethylhexyl) phthalate ug/L LGW-6 4 4.950 0.000 1.176 4.950 4.950 6.000Carbon disulfide ug/L LGW-6 4 0.500 0.000 1.176 0.500 0.500 720.000Chlorobenzene ug/L LGW-6 4 0.500 0.000 1.176 0.500 0.500 100.000Chloroethane ug/L LGW-6 4 0.500 0.000 1.176 0.500 0.500 21000.000Chloroform ug/L LGW-6 4 0.500 0.000 1.176 0.500 0.500 80.000Cis-1,2-dichloroethene ug/L LGW-6 4 0.500 0.000 1.176 0.500 0.500 70.000Dichlorodifluoromethane ug/L LGW-6 4 1.000 0.000 1.176 1.000 1.000 190.000Ethylbenzene ug/L LGW-6 4 0.500 0.000 1.176 0.500 0.500 700.000Methyl ethyl ketone ug/L LGW-6 4 2.500 0.000 1.176 2.500 2.500 4900.000Methylene chloride ug/L LGW-6 4 0.500 0.000 1.176 0.500 0.500 5.000Tetrachloroethene ug/L LGW-6 4 0.500 0.000 1.176 0.500 0.500 5.000Toluene ug/L LGW-6 4 0.500 0.000 1.176 0.500 0.500 1000.000Total xylenes ug/L LGW-6 4 0.500 0.000 1.176 0.500 0.500 10000.000Trichloroethene ug/L LGW-6 4 0.500 0.000 1.176 0.500 0.500 5.000Trichlorofluoromethane ug/L LGW-6 4 0.500 0.000 1.176 0.500 0.500 1100.000Vinyl chloride ug/L LGW-6 4 0.500 0.000 1.176 0.500 0.500 2.0001,1-dichloroethane ug/L LGW-7 4 0.500 0.000 1.176 0.500 0.500 2.4001,2-dichloroethane ug/L LGW-7 4 0.500 0.000 1.176 0.500 0.500 5.0001,2-dichloropropane ug/L LGW-7 4 0.500 0.000 1.176 0.500 0.500 5.0001,4-dichlorobenzene ug/L LGW-7 4 0.500 0.000 1.176 0.500 0.500 75.000Acetone ug/L LGW-7 4 3.775 2.550 1.176 0.775 6.775 12000.000Benzene ug/L LGW-7 4 0.500 0.000 1.176 0.500 0.500 5.000Bis(2-ethylhexyl) phthalate ug/L LGW-7 4 4.800 0.000 1.176 4.800 4.800 6.000Carbon disulfide ug/L LGW-7 4 0.500 0.000 1.176 0.500 0.500 720.000Chlorobenzene ug/L LGW-7 4 0.500 0.000 1.176 0.500 0.500 100.000Chloroethane ug/L LGW-7 4 0.500 0.000 1.176 0.500 0.500 21000.000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwvoc]

Page 73: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Confidence Intervals for Comparing the Mean of the Last4 Measurements to an Assessment Monitoring Standard

Constituent Units Well N Mean SD Factor 95% LCL 95% UCL Standard Chloroform ug/L LGW-7 4 0.500 0.000 1.176 0.500 0.500 80.000Cis-1,2-dichloroethene ug/L LGW-7 4 0.500 0.000 1.176 0.500 0.500 70.000Dichlorodifluoromethane ug/L LGW-7 4 1.000 0.000 1.176 1.000 1.000 190.000Ethylbenzene ug/L LGW-7 4 0.500 0.000 1.176 0.500 0.500 700.000Methyl ethyl ketone ug/L LGW-7 4 2.500 0.000 1.176 2.500 2.500 4900.000Methylene chloride ug/L LGW-7 4 0.500 0.000 1.176 0.500 0.500 5.000Tetrachloroethene ug/L LGW-7 4 0.500 0.000 1.176 0.500 0.500 5.000Toluene ug/L LGW-7 4 0.500 0.000 1.176 0.500 0.500 1000.000Total xylenes ug/L LGW-7 4 0.500 0.000 1.176 0.500 0.500 10000.000Trichloroethene ug/L LGW-7 4 0.500 0.000 1.176 0.500 0.500 5.000Trichlorofluoromethane ug/L LGW-7 4 0.500 0.000 1.176 0.500 0.500 1100.000Vinyl chloride ug/L LGW-7 4 0.500 0.000 1.176 0.500 0.500 2.0001,1-dichloroethane ug/L LGW-9 4 0.500 0.000 1.176 0.500 0.500 2.4001,2-dichloroethane ug/L LGW-9 4 0.500 0.000 1.176 0.500 0.500 5.0001,2-dichloropropane ug/L LGW-9 4 0.500 0.000 1.176 0.500 0.500 5.0001,4-dichlorobenzene ug/L LGW-9 4 0.500 0.000 1.176 0.500 0.500 75.000Acetone ug/L LGW-9 4 6.175 4.592 1.176 0.773 11.577 12000.000Benzene ug/L LGW-9 4 0.500 0.000 1.176 0.500 0.500 5.000Bis(2-ethylhexyl) phthalate ug/L LGW-9 4 4.800 0.000 1.176 4.800 4.800 6.000Carbon disulfide ug/L LGW-9 4 0.500 0.000 1.176 0.500 0.500 720.000Chlorobenzene ug/L LGW-9 4 0.500 0.000 1.176 0.500 0.500 100.000Chloroethane ug/L LGW-9 4 0.500 0.000 1.176 0.500 0.500 21000.000Chloroform ug/L LGW-9 4 0.500 0.000 1.176 0.500 0.500 80.000Cis-1,2-dichloroethene ug/L LGW-9 4 0.500 0.000 1.176 0.500 0.500 70.000Dichlorodifluoromethane ug/L LGW-9 4 1.000 0.000 1.176 1.000 1.000 190.000Ethylbenzene ug/L LGW-9 4 0.500 0.000 1.176 0.500 0.500 700.000Methyl ethyl ketone ug/L LGW-9 4 2.500 0.000 1.176 2.500 2.500 4900.000Methylene chloride ug/L LGW-9 4 0.500 0.000 1.176 0.500 0.500 5.000Tetrachloroethene ug/L LGW-9 4 0.500 0.000 1.176 0.500 0.500 5.000Toluene ug/L LGW-9 4 0.500 0.000 1.176 0.500 0.500 1000.000Total xylenes ug/L LGW-9 4 0.500 0.000 1.176 0.500 0.500 10000.000Trichloroethene ug/L LGW-9 4 0.500 0.000 1.176 0.500 0.500 5.000Trichlorofluoromethane ug/L LGW-9 4 0.500 0.000 1.176 0.500 0.500 1100.000Vinyl chloride ug/L LGW-9 4 0.500 0.000 1.176 0.500 0.500 2.0001,1-dichloroethane ug/L MW-21 4 0.500 0.000 1.176 0.500 0.500 2.4001,2-dichloroethane ug/L MW-21 4 0.500 0.000 1.176 0.500 0.500 5.0001,2-dichloropropane ug/L MW-21 4 0.500 0.000 1.176 0.500 0.500 5.0001,4-dichlorobenzene ug/L MW-21 4 1.375 0.737 1.176 0.509 2.241 75.000Acetone ug/L MW-21 4 8.525 10.389 1.176 0.000 20.746 12000.000Benzene ug/L MW-21 4 0.500 0.000 1.176 0.500 0.500 5.000Bis(2-ethylhexyl) phthalate ug/L MW-21 3 *Carbon disulfide ug/L MW-21 4 0.500 0.000 1.176 0.500 0.500 720.000Chlorobenzene ug/L MW-21 4 0.825 0.650 1.176 0.060 1.590 100.000Chloroethane ug/L MW-21 4 0.500 0.000 1.176 0.500 0.500 21000.000Chloroform ug/L MW-21 4 0.500 0.000 1.176 0.500 0.500 80.000Cis-1,2-dichloroethene ug/L MW-21 4 0.500 0.000 1.176 0.500 0.500 70.000Dichlorodifluoromethane ug/L MW-21 3 *Ethylbenzene ug/L MW-21 4 0.500 0.000 1.176 0.500 0.500 700.000Methyl ethyl ketone ug/L MW-21 4 2.500 0.000 1.176 2.500 2.500 4900.000Methylene chloride ug/L MW-21 4 0.500 0.000 1.176 0.500 0.500 5.000Tetrachloroethene ug/L MW-21 4 0.500 0.000 1.176 0.500 0.500 5.000Toluene ug/L MW-21 4 0.500 0.000 1.176 0.500 0.500 1000.000Total xylenes ug/L MW-21 4 0.500 0.000 1.176 0.500 0.500 10000.000Trichloroethene ug/L MW-21 4 0.500 0.000 1.176 0.500 0.500 5.000Trichlorofluoromethane ug/L MW-21 4 0.500 0.000 1.176 0.500 0.500 1100.000Vinyl chloride ug/L MW-21 4 0.500 0.000 1.176 0.500 0.500 2.0001,1-dichloroethane ug/L MW-2N 4 0.500 0.000 1.176 0.500 0.500 2.4001,2-dichloroethane ug/L MW-2N 4 0.500 0.000 1.176 0.500 0.500 5.0001,2-dichloropropane ug/L MW-2N 4 0.500 0.000 1.176 0.500 0.500 5.0001,4-dichlorobenzene ug/L MW-2N 4 0.500 0.000 1.176 0.500 0.500 75.000Acetone ug/L MW-2N 4 13.125 17.480 1.176 0.000 33.687 12000.000Benzene ug/L MW-2N 4 0.500 0.000 1.176 0.500 0.500 5.000Bis(2-ethylhexyl) phthalate ug/L MW-2N 4 5.000 0.000 1.176 5.000 5.000 6.000Carbon disulfide ug/L MW-2N 4 0.500 0.000 1.176 0.500 0.500 720.000Chlorobenzene ug/L MW-2N 4 0.500 0.000 1.176 0.500 0.500 100.000Chloroethane ug/L MW-2N 4 0.500 0.000 1.176 0.500 0.500 21000.000Chloroform ug/L MW-2N 4 0.500 0.000 1.176 0.500 0.500 80.000Cis-1,2-dichloroethene ug/L MW-2N 4 0.500 0.000 1.176 0.500 0.500 70.000Dichlorodifluoromethane ug/L MW-2N 4 1.000 0.000 1.176 1.000 1.000 190.000Ethylbenzene ug/L MW-2N 4 0.500 0.000 1.176 0.500 0.500 700.000Methyl ethyl ketone ug/L MW-2N 4 2.500 0.000 1.176 2.500 2.500 4900.000Methylene chloride ug/L MW-2N 4 0.500 0.000 1.176 0.500 0.500 5.000Tetrachloroethene ug/L MW-2N 4 0.500 0.000 1.176 0.500 0.500 5.000Toluene ug/L MW-2N 4 0.500 0.000 1.176 0.500 0.500 1000.000Total xylenes ug/L MW-2N 4 0.500 0.000 1.176 0.500 0.500 10000.000Trichloroethene ug/L MW-2N 4 0.500 0.000 1.176 0.500 0.500 5.000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwvoc]

Page 74: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Confidence Intervals for Comparing the Mean of the Last4 Measurements to an Assessment Monitoring Standard

Constituent Units Well N Mean SD Factor 95% LCL 95% UCL Standard Trichlorofluoromethane ug/L MW-2N 4 0.500 0.000 1.176 0.500 0.500 1100.000Vinyl chloride ug/L MW-2N 4 0.500 0.000 1.176 0.500 0.500 2.0001,1-dichloroethane ug/L MW-3N 4 0.500 0.000 1.176 0.500 0.500 2.4001,2-dichloroethane ug/L MW-3N 4 0.500 0.000 1.176 0.500 0.500 5.0001,2-dichloropropane ug/L MW-3N 4 0.500 0.000 1.176 0.500 0.500 5.0001,4-dichlorobenzene ug/L MW-3N 4 0.500 0.000 1.176 0.500 0.500 75.000Acetone ug/L MW-3N 4 3.275 1.550 1.176 1.452 5.098 12000.000Benzene ug/L MW-3N 4 0.500 0.000 1.176 0.500 0.500 5.000Bis(2-ethylhexyl) phthalate ug/L MW-3N 4 4.800 0.000 1.176 4.800 4.800 6.000Carbon disulfide ug/L MW-3N 4 0.500 0.000 1.176 0.500 0.500 720.000Chlorobenzene ug/L MW-3N 4 0.500 0.000 1.176 0.500 0.500 100.000Chloroethane ug/L MW-3N 4 0.500 0.000 1.176 0.500 0.500 21000.000Chloroform ug/L MW-3N 4 0.500 0.000 1.176 0.500 0.500 80.000Cis-1,2-dichloroethene ug/L MW-3N 4 0.500 0.000 1.176 0.500 0.500 70.000Dichlorodifluoromethane ug/L MW-3N 4 1.000 0.000 1.176 1.000 1.000 190.000Ethylbenzene ug/L MW-3N 4 0.500 0.000 1.176 0.500 0.500 700.000Methyl ethyl ketone ug/L MW-3N 4 2.500 0.000 1.176 2.500 2.500 4900.000Methylene chloride ug/L MW-3N 4 0.500 0.000 1.176 0.500 0.500 5.000Tetrachloroethene ug/L MW-3N 4 0.500 0.000 1.176 0.500 0.500 5.000Toluene ug/L MW-3N 4 0.500 0.000 1.176 0.500 0.500 1000.000Total xylenes ug/L MW-3N 4 0.500 0.000 1.176 0.500 0.500 10000.000Trichloroethene ug/L MW-3N 4 0.500 0.000 1.176 0.500 0.500 5.000Trichlorofluoromethane ug/L MW-3N 4 0.500 0.000 1.176 0.500 0.500 1100.000Vinyl chloride ug/L MW-3N 4 0.500 0.000 1.176 0.500 0.500 2.0001,1-dichloroethane ug/L MW-7N 4 0.500 0.000 1.176 0.500 0.500 2.4001,2-dichloroethane ug/L MW-7N 4 0.500 0.000 1.176 0.500 0.500 5.0001,2-dichloropropane ug/L MW-7N 4 0.500 0.000 1.176 0.500 0.500 5.0001,4-dichlorobenzene ug/L MW-7N 4 0.500 0.000 1.176 0.500 0.500 75.000Acetone ug/L MW-7N 4 3.700 2.400 1.176 0.877 6.523 12000.000Benzene ug/L MW-7N 4 0.500 0.000 1.176 0.500 0.500 5.000Bis(2-ethylhexyl) phthalate ug/L MW-7N 4 5.000 0.000 1.176 5.000 5.000 6.000Carbon disulfide ug/L MW-7N 4 0.500 0.000 1.176 0.500 0.500 720.000Chlorobenzene ug/L MW-7N 4 0.500 0.000 1.176 0.500 0.500 100.000Chloroethane ug/L MW-7N 4 0.500 0.000 1.176 0.500 0.500 21000.000Chloroform ug/L MW-7N 4 0.500 0.000 1.176 0.500 0.500 80.000Cis-1,2-dichloroethene ug/L MW-7N 4 0.500 0.000 1.176 0.500 0.500 70.000Dichlorodifluoromethane ug/L MW-7N 4 1.000 0.000 1.176 1.000 1.000 190.000Ethylbenzene ug/L MW-7N 4 0.500 0.000 1.176 0.500 0.500 700.000Methyl ethyl ketone ug/L MW-7N 4 2.500 0.000 1.176 2.500 2.500 4900.000Methylene chloride ug/L MW-7N 4 0.500 0.000 1.176 0.500 0.500 5.000Tetrachloroethene ug/L MW-7N 4 0.500 0.000 1.176 0.500 0.500 5.000Toluene ug/L MW-7N 4 0.500 0.000 1.176 0.500 0.500 1000.000Total xylenes ug/L MW-7N 4 0.500 0.000 1.176 0.500 0.500 10000.000Trichloroethene ug/L MW-7N 4 0.500 0.000 1.176 0.500 0.500 5.000Trichlorofluoromethane ug/L MW-7N 4 0.500 0.000 1.176 0.500 0.500 1100.000Vinyl chloride ug/L MW-7N 4 0.500 0.000 1.176 0.500 0.500 2.0001,1-dichloroethane ug/L MW-8N 4 0.500 0.000 1.176 0.500 0.500 2.4001,2-dichloroethane ug/L MW-8N 4 0.500 0.000 1.176 0.500 0.500 5.0001,2-dichloropropane ug/L MW-8N 4 0.500 0.000 1.176 0.500 0.500 5.0001,4-dichlorobenzene ug/L MW-8N 4 0.500 0.000 1.176 0.500 0.500 75.000Acetone ug/L MW-8N 4 4.250 2.124 1.176 1.752 6.748 12000.000Benzene ug/L MW-8N 4 0.500 0.000 1.176 0.500 0.500 5.000Bis(2-ethylhexyl) phthalate ug/L MW-8N 4 4.850 0.000 1.176 4.850 4.850 6.000Carbon disulfide ug/L MW-8N 4 0.500 0.000 1.176 0.500 0.500 720.000Chlorobenzene ug/L MW-8N 4 0.500 0.000 1.176 0.500 0.500 100.000Chloroethane ug/L MW-8N 4 0.500 0.000 1.176 0.500 0.500 21000.000Chloroform ug/L MW-8N 4 0.500 0.000 1.176 0.500 0.500 80.000Cis-1,2-dichloroethene ug/L MW-8N 4 0.500 0.000 1.176 0.500 0.500 70.000Dichlorodifluoromethane ug/L MW-8N 4 1.000 0.000 1.176 1.000 1.000 190.000Ethylbenzene ug/L MW-8N 4 0.500 0.000 1.176 0.500 0.500 700.000Methyl ethyl ketone ug/L MW-8N 4 2.500 0.000 1.176 2.500 2.500 4900.000Methylene chloride ug/L MW-8N 4 0.500 0.000 1.176 0.500 0.500 5.000Tetrachloroethene ug/L MW-8N 4 0.500 0.000 1.176 0.500 0.500 5.000Toluene ug/L MW-8N 4 0.500 0.000 1.176 0.500 0.500 1000.000Total xylenes ug/L MW-8N 4 0.500 0.000 1.176 0.500 0.500 10000.000Trichloroethene ug/L MW-8N 4 0.500 0.000 1.176 0.500 0.500 5.000Trichlorofluoromethane ug/L MW-8N 4 0.500 0.000 1.176 0.500 0.500 1100.000Vinyl chloride ug/L MW-8N 4 0.500 0.000 1.176 0.500 0.500 2.000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwvoc]

* - Insufficient Data** - Significant ExceedanceLCL = Lower Confidence LimitUCL = Upper Confidence Limit

Page 75: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

LGW-101,1-dichloroethane

ug/L

Year

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-101,2-dichloroethane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-101,2-dichloropropane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-101,4-dichlorobenzene

Significant Increasing Trend

ug/L

Year

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-10Acetone

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

10000.

100000.

0.0006 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-10Benzene

Significant Increasing Trend

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-10Bis(2-ethylhexyl) phthalate

ug/L

YearMedian ND/2

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-10Carbon disulfide

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-10Chlorobenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-10Chloroethane

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

100000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-10Chloroform

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-10Cis-1,2-dichloroethene

ug/L

Year

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwvoc]

Page 76: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

LGW-10Dichlorodifluoromethane

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-10Ethylbenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-10Methyl ethyl ketone

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-10Methylene chloride

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-10Tetrachloroethene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-10Toluene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-10Total xylenes

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-10Trichloroethene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-10Trichlorofluoromethane

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-10Vinyl chloride

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwvoc]

Page 77: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

LGW-51,1-dichloroethane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-51,2-dichloroethane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-51,2-dichloropropane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-51,4-dichlorobenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-5Acetone

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

10000.

100000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-5Benzene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-5Bis(2-ethylhexyl) phthalate

ug/L

YearMedian ND/2

0.5.

10.15.20.25.30.35.40.45.50.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-5Carbon disulfide

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-5Chlorobenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-5Chloroethane

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

100000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-5Chloroform

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-5Cis-1,2-dichloroethene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwvoc]

Page 78: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

LGW-5Dichlorodifluoromethane

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-5Ethylbenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-5Methyl ethyl ketone

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-5Methylene chloride

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-5Tetrachloroethene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-5Toluene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-5Total xylenes

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-5Trichloroethene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-5Trichlorofluoromethane

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-5Vinyl chloride

ug/L

YearMedian ND/2

0.000.200.400.600.801.001.201.401.601.802.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwvoc]

Page 79: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

LGW-61,1-dichloroethane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-61,2-dichloroethane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-61,2-dichloropropane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-61,4-dichlorobenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-6Acetone

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

10000.

100000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-6Benzene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-6Bis(2-ethylhexyl) phthalate

ug/L

YearMedian ND/2

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-6Carbon disulfide

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-6Chlorobenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-6Chloroethane

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

100000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-6Chloroform

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-6Cis-1,2-dichloroethene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwvoc]

Page 80: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

LGW-6Dichlorodifluoromethane

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-6Ethylbenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-6Methyl ethyl ketone

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-6Methylene chloride

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-6Tetrachloroethene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-6Toluene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-6Total xylenes

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-6Trichloroethene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-6Trichlorofluoromethane

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-6Vinyl chloride

ug/L

YearMedian ND/2

0.000.200.400.600.801.001.201.401.601.802.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwvoc]

Page 81: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

LGW-71,1-dichloroethane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-71,2-dichloroethane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-71,2-dichloropropane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-71,4-dichlorobenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-7Acetone

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

100000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-7Benzene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-7Bis(2-ethylhexyl) phthalate

ug/L

YearMedian ND/2

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-7Carbon disulfide

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-7Chlorobenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-7Chloroethane

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

100000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-7Chloroform

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-7Cis-1,2-dichloroethene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwvoc]

Page 82: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

LGW-7Dichlorodifluoromethane

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-7Ethylbenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-7Methyl ethyl ketone

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-7Methylene chloride

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-7Tetrachloroethene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-7Toluene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-7Total xylenes

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-7Trichloroethene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-7Trichlorofluoromethane

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-7Vinyl chloride

ug/L

YearMedian ND/2

0.000.200.400.600.801.001.201.401.601.802.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwvoc]

Page 83: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

LGW-91,1-dichloroethane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-91,2-dichloroethane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-91,2-dichloropropane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-91,4-dichlorobenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-9Acetone

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

100000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-9Benzene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-9Bis(2-ethylhexyl) phthalate

ug/L

YearMedian ND/2

0.01.02.03.04.05.06.07.08.09.0

10.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-9Carbon disulfide

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-9Chlorobenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-9Chloroethane

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

100000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-9Chloroform

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-9Cis-1,2-dichloroethene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwvoc]

Page 84: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

LGW-9Dichlorodifluoromethane

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-9Ethylbenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-9Methyl ethyl ketone

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-9Methylene chloride

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-9Tetrachloroethene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-9Toluene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-9Total xylenes

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-9Trichloroethene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-9Trichlorofluoromethane

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-9Vinyl chloride

ug/L

YearMedian ND/2

0.000.200.400.600.801.001.201.401.601.802.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwvoc]

Page 85: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

MW-211,1-dichloroethane

ug/L

Month / Year Median ND/2

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-211,2-dichloroethane

ug/L

Month / Year Median ND/2

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-211,2-dichloropropane

ug/L

Month / Year Median ND/2

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-211,4-dichlorobenzene

ug/L

Month / Year Median ND/2

0.100

1.00

10.0

100.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-21Acetone

ug/L

Month / Year Median ND/2

1.00

10.0

100.

1000.

10000.

100000.

0.00jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-21Benzene

ug/L

Month / Year Median ND/2

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-21Bis(2-ethylhexyl) phthalate

ug/L

Month / Year Median ND/2

0.01.02.03.04.05.06.07.08.09.0

10.0

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-21Carbon disulfide

ug/L

Month / Year Median ND/2

0.100

1.00

10.0

100.

1000.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-21Chlorobenzene

ug/L

Month / Year Median ND/2

0.0100

0.100

1.00

10.0

100.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-21Chloroethane

ug/L

Month / Year Median ND/2

0.100

1.00

10.0

100.

1000.

10000.

100000.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-21Chloroform

ug/L

Month / Year Median ND/2

0.100

1.00

10.0

100.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-21Cis-1,2-dichloroethene

ug/L

Month / Year Median ND/2

0.100

1.00

10.0

100.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwvoc]

Page 86: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

MW-21Dichlorodifluoromethane

ug/L

Month / Year Median ND/2

1.00

10.0

100.

1000.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-21Ethylbenzene

ug/L

Month / Year Median ND/2

0.100

1.00

10.0

100.

1000.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-21Methyl ethyl ketone

ug/L

Month / Year Median ND/2

1.00

10.0

100.

1000.

10000.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-21Methylene chloride

ug/L

Month / Year Median ND/2

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-21Tetrachloroethene

ug/L

Month / Year Median ND/2

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-21Toluene

ug/L

Month / Year Median ND/2

0.100

1.00

10.0

100.

1000.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-21Total xylenes

ug/L

Month / Year Median ND/2

0.100

1.00

10.0

100.

1000.

10000.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-21Trichloroethene

ug/L

Month / Year Median ND/2

0.000.501.001.502.002.503.003.504.004.505.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-21Trichlorofluoromethane

ug/L

Month / Year Median ND/2

0.100

1.00

10.0

100.

1000.

10000.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-21Vinyl chloride

ug/L

Month / Year Median ND/2

0.000.200.400.600.801.001.201.401.601.802.00

jan15

maysep jan16

maysep jan17

maysep jan18

maysep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwvoc]

Page 87: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

MW-2N1,1-dichloroethane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2N1,2-dichloroethane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2N1,2-dichloropropane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2N1,4-dichlorobenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2NAcetone

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

10000.

100000.

0.0096 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2NBenzene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2NBis(2-ethylhexyl) phthalate

ug/L

YearMedian ND/2

0.01.02.03.04.05.06.07.08.09.0

10.0

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2NCarbon disulfide

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2NChlorobenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2NChloroethane

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

100000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2NChloroform

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2NCis-1,2-dichloroethene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwvoc]

Page 88: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

MW-2NDichlorodifluoromethane

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2NEthylbenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2NMethyl ethyl ketone

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

10000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2NMethylene chloride

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2NTetrachloroethene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2NToluene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2NTotal xylenes

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2NTrichloroethene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2NTrichlorofluoromethane

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2NVinyl chloride

ug/L

YearMedian ND/2

0.000.200.400.600.801.001.201.401.601.802.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwvoc]

Page 89: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

MW-3N1,1-dichloroethane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3N1,2-dichloroethane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3N1,2-dichloropropane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3N1,4-dichlorobenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3NAcetone

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

10000.

100000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3NBenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3NBis(2-ethylhexyl) phthalate

ug/L

YearMedian ND/2

0.01.02.03.04.05.06.07.08.09.0

10.0

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3NCarbon disulfide

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3NChlorobenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3NChloroethane

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

100000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3NChloroform

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3NCis-1,2-dichloroethene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwvoc]

Page 90: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

MW-3NDichlorodifluoromethane

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3NEthylbenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3NMethyl ethyl ketone

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

10000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3NMethylene chloride

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3NTetrachloroethene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3NToluene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3NTotal xylenes

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3NTrichloroethene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3NTrichlorofluoromethane

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3NVinyl chloride

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwvoc]

Page 91: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

MW-7N1,1-dichloroethane

Significant Decreasing Trend

ug/L

YearMedian ND/2

0.01.02.03.04.05.06.07.08.09.0

10.0

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7N1,2-dichloroethane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7N1,2-dichloropropane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7N1,4-dichlorobenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7NAcetone

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

100000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7NBenzene

ug/L

YearMedian ND/2

0.01.02.03.04.05.06.07.08.09.0

10.0

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7NBis(2-ethylhexyl) phthalate

ug/L

YearMedian ND/2

0.01.02.03.04.05.06.07.08.09.0

10.0

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7NCarbon disulfide

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7NChlorobenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7NChloroethane

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

100000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7NChloroform

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7NCis-1,2-dichloroethene

Significant Decreasing Trend

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwvoc]

Page 92: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

MW-7NDichlorodifluoromethane

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7NEthylbenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7NMethyl ethyl ketone

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

10000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7NMethylene chloride

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7NTetrachloroethene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7NToluene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7NTotal xylenes

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7NTrichloroethene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7NTrichlorofluoromethane

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7NVinyl chloride

Significant Decreasing Trend

ug/L

YearMedian ND/2

0.01.02.03.04.05.06.07.08.09.0

10.0

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwvoc]

Page 93: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

MW-8N1,1-dichloroethane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8N1,2-dichloroethane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8N1,2-dichloropropane

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8N1,4-dichlorobenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8NAcetone

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

10000.

100000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8NBenzene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8NBis(2-ethylhexyl) phthalate

ug/L

YearMedian ND/2

0.01.02.03.04.05.06.07.08.09.0

10.0

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8NCarbon disulfide

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8NChlorobenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8NChloroethane

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

100000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8NChloroform

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8NCis-1,2-dichloroethene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwvoc]

Page 94: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

MW-8NDichlorodifluoromethane

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8NEthylbenzene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8NMethyl ethyl ketone

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

10000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8NMethylene chloride

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8NTetrachloroethene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8NToluene

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8NTotal xylenes

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8NTrichloroethene

ug/L

YearMedian ND/2

0.000.501.001.502.002.503.003.504.004.505.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8NTrichlorofluoromethane

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

10000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8NVinyl chloride

ug/L

YearMedian ND/2

0.000.200.400.600.801.001.201.401.601.802.00

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gwvoc]

Page 95: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Ground Water Statistics for Eco-Vista Sanitary Landfill Third Quarter Monitoring Event In 2018

C:\Otter Creek Environmental\Arkansas\Eco-Vista\ecovistaq318RRRR.doc December 14, 2018

Attachment E

95% LCL Calculations for Metals and Inorganics

Page 96: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Confidence Intervals for Comparing the Mean of the Last4 Measurements to an Assessment Monitoring Standard

Constituent Units Well N Mean SD Factor 95% LCL 95% UCL Standard Arsenic, total ug/L LGW-10 4 2.500 0.000 1.176 2.500 2.500 10.000Barium, total ug/L LGW-10 4 101.250 21.654 1.176 75.778 126.722 2000.000Cadmium, total ug/L LGW-10 4 0.500 0.000 1.176 0.500 0.500 5.000Cobalt, total ug/L LGW-10 4 79.750 30.226 1.176 44.196 115.304 11.000 **Nickel, total ug/L LGW-10 4 177.500 55.603 1.176 112.095 242.905 300.000Zinc, total ug/L LGW-10 4 41.125 29.795 1.176 6.078 76.172 4700.000Arsenic, total ug/L LGW-14R 4 2.500 0.000 1.176 2.500 2.500 10.000Barium, total ug/L LGW-14R 4 32.000 2.160 1.176 29.459 34.541 2000.000Cadmium, total ug/L LGW-14R 4 0.500 0.000 1.176 0.500 0.500 5.000Cobalt, total ug/L LGW-14R 4 1.500 0.000 1.176 1.500 1.500 11.000Nickel, total ug/L LGW-14R 4 2.000 0.000 1.176 2.000 2.000 300.000Zinc, total ug/L LGW-14R 4 20.300 26.508 1.176 0.000 51.481 4700.000Arsenic, total ug/L LGW-2 4 8.100 1.490 1.176 6.347 9.853 10.000Barium, total ug/L LGW-2 4 107.000 10.132 1.176 95.081 118.919 2000.000Cadmium, total ug/L LGW-2 4 0.500 0.000 1.176 0.500 0.500 5.000Cobalt, total ug/L LGW-2 4 3.350 2.504 1.176 0.405 6.295 11.000Nickel, total ug/L LGW-2 4 6.750 5.620 1.176 0.139 13.361 300.000Zinc, total ug/L LGW-2 4 7.650 6.495 1.176 0.010 15.290 4700.000Arsenic, total ug/L LGW-5 4 2.500 0.000 1.176 2.500 2.500 10.000Barium, total ug/L LGW-5 4 72.750 3.096 1.176 69.109 76.391 2000.000Cadmium, total ug/L LGW-5 4 1.825 0.714 1.176 0.986 2.664 5.000Cobalt, total ug/L LGW-5 4 1.500 0.000 1.176 1.500 1.500 11.000Nickel, total ug/L LGW-5 4 7.975 2.903 1.176 4.560 11.390 300.000Zinc, total ug/L LGW-5 4 16.000 4.082 1.176 11.198 20.802 4700.000Arsenic, total ug/L LGW-6 4 2.500 0.000 1.176 2.500 2.500 10.000Barium, total ug/L LGW-6 4 100.000 14.142 1.176 83.365 116.635 2000.000Cadmium, total ug/L LGW-6 4 67.000 8.042 1.176 57.541 76.459 5.000 **Cobalt, total ug/L LGW-6 4 1.500 0.000 1.176 1.500 1.500 11.000Nickel, total ug/L LGW-6 4 135.000 12.910 1.176 119.814 150.186 300.000Zinc, total ug/L LGW-6 4 267.500 12.583 1.176 252.699 282.301 4700.000Arsenic, total ug/L LGW-7 4 2.500 0.000 1.176 2.500 2.500 10.000Barium, total ug/L LGW-7 4 35.250 10.046 1.176 23.433 47.067 2000.000Cadmium, total ug/L LGW-7 4 37.250 10.372 1.176 25.049 49.451 5.000 **Cobalt, total ug/L LGW-7 4 1.500 0.000 1.176 1.500 1.500 11.000Nickel, total ug/L LGW-7 4 104.000 26.783 1.176 72.495 135.505 300.000Zinc, total ug/L LGW-7 4 415.000 113.871 1.176 281.055 548.945 4700.000Arsenic, total ug/L LGW-8R 4 2.500 0.000 1.176 2.500 2.500 10.000Barium, total ug/L LGW-8R 4 73.000 4.163 1.176 68.103 77.897 2000.000Cadmium, total ug/L LGW-8R 4 0.500 0.000 1.176 0.500 0.500 5.000Cobalt, total ug/L LGW-8R 4 1.500 0.000 1.176 1.500 1.500 11.000Nickel, total ug/L LGW-8R 4 2.000 0.000 1.176 2.000 2.000 300.000Zinc, total ug/L LGW-8R 4 3.300 1.600 1.176 1.418 5.182 4700.000Arsenic, total ug/L LGW-9 4 2.500 0.000 1.176 2.500 2.500 10.000Barium, total ug/L LGW-9 4 175.000 5.774 1.176 168.209 181.791 2000.000Cadmium, total ug/L LGW-9 4 44.500 8.888 1.176 34.045 54.955 5.000 **Cobalt, total ug/L LGW-9 4 7.225 1.935 1.176 4.949 9.501 11.000Nickel, total ug/L LGW-9 4 52.500 1.915 1.176 50.248 54.752 300.000Zinc, total ug/L LGW-9 4 170.000 11.547 1.176 156.417 183.583 4700.000Arsenic, total ug/L MW-21 4 2.500 0.000 1.176 2.500 2.500 10.000Barium, total ug/L MW-21 4 287.500 72.744 1.176 201.932 373.068 2000.000Cadmium, total ug/L MW-21 4 1.475 0.862 1.176 0.461 2.489 5.000Cobalt, total ug/L MW-21 4 22.750 7.042 1.176 14.467 31.033 11.000 **Nickel, total ug/L MW-21 4 55.250 13.048 1.176 39.902 70.598 300.000Zinc, total ug/L MW-21 4 83.000 17.108 1.176 62.877 103.123 4700.000Arsenic, total ug/L MW-2N 4 2.500 0.000 1.176 2.500 2.500 10.000Barium, total ug/L MW-2N 4 58.000 4.761 1.176 52.400 63.600 2000.000Cadmium, total ug/L MW-2N 4 0.500 0.000 1.176 0.500 0.500 5.000Cobalt, total ug/L MW-2N 4 1.500 0.000 1.176 1.500 1.500 11.000Nickel, total ug/L MW-2N 4 2.000 0.000 1.176 2.000 2.000 300.000Zinc, total ug/L MW-2N 4 8.075 1.195 1.176 6.669 9.481 4700.000Arsenic, total ug/L MW-3N 4 2.500 0.000 1.176 2.500 2.500 10.000Barium, total ug/L MW-3N 4 117.500 9.574 1.176 106.238 128.762 2000.000Cadmium, total ug/L MW-3N 4 26.250 7.805 1.176 17.069 35.431 5.000 **Cobalt, total ug/L MW-3N 4 2.075 1.150 1.176 0.722 3.428 11.000Nickel, total ug/L MW-3N 4 36.500 16.663 1.176 16.899 56.101 300.000Zinc, total ug/L MW-3N 4 137.500 28.723 1.176 103.714 171.286 4700.000Arsenic, total ug/L MW-7N 4 2.500 0.000 1.176 2.500 2.500 10.000Barium, total ug/L MW-7N 4 142.500 22.174 1.176 116.417 168.583 2000.000Cadmium, total ug/L MW-7N 4 4.550 3.757 1.176 0.130 8.970 5.000Cobalt, total ug/L MW-7N 4 4.850 2.509 1.176 1.898 7.802 11.000Nickel, total ug/L MW-7N 4 24.125 11.302 1.176 10.831 37.419 300.000Zinc, total ug/L MW-7N 4 330.000 419.126 1.176 0.000 823.013 4700.000Arsenic, total ug/L MW-8N 4 2.500 0.000 1.176 2.500 2.500 10.000Barium, total ug/L MW-8N 4 177.500 5.000 1.176 171.619 183.381 2000.000Cadmium, total ug/L MW-8N 4 16.750 1.500 1.176 14.986 18.514 5.000 **Cobalt, total ug/L MW-8N 4 1.500 0.000 1.176 1.500 1.500 11.000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 97: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Table 1

Confidence Intervals for Comparing the Mean of the Last4 Measurements to an Assessment Monitoring Standard

Constituent Units Well N Mean SD Factor 95% LCL 95% UCL Standard Nickel, total ug/L MW-8N 4 41.750 3.304 1.176 37.863 45.637 300.000Zinc, total ug/L MW-8N 4 35.500 9.000 1.176 24.913 46.087 4700.000

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

* - Insufficient Data** - Significant ExceedanceLCL = Lower Confidence LimitUCL = Upper Confidence Limit

Page 98: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

LGW-10Arsenic, total

ug/L

YearManual ND/2

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-10Barium, total

ug/L

Year

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-10Cadmium, total

ug/L

YearManual ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-10Cobalt, total

Confidence Limit Exceeds Standard

ug/L

Year

0.20.40.60.80.

100.120.140.160.180.200.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-10Nickel, total

ug/L

Year

0.50.

100.150.200.250.300.350.400.450.500.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-10Zinc, total

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-14RArsenic, total

ug/L

YearManual ND/2

0.01.02.03.04.05.06.07.08.09.0

10.0

09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-14RBarium, total

ug/L

Year

10.0

100.

1000.

10000.

09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-14RCadmium, total

ug/L

YearManual ND/2

0.000.501.001.502.002.503.003.504.004.505.00

09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 99: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

LGW-14RCobalt, total

ug/L

YearMedian ND/2

0.02.04.06.08.0

10.012.014.016.018.020.0

09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-14RNickel, total

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-14RZinc, total

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

10000.

0.0009 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-2Arsenic, total

ug/L

YearManual ND/2

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-2Barium, total

ug/L

Year

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-2Cadmium, total

ug/L

YearManual ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-2Cobalt, total

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-2Nickel, total

ug/L

YearMedian ND/2

0.100

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-2Zinc, total

ug/L

YearMedian ND/2

0.0100

0.100

1.00

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 100: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

LGW-5Arsenic, total

ug/L

YearManual ND/2

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-5Barium, total

ug/L

Year

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-5Cadmium, total

ug/L

YearManual ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-5Cobalt, total

ug/L

YearMedian ND/2

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-5Nickel, total

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-5Zinc, total

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-6Arsenic, total

ug/L

YearManual ND/2

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-6Barium, total

Significant Increasing Trend

ug/L

Year

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-6Cadmium, total

Confidence Limit Exceeds Standard

ug/L

YearManual ND/2

0.100

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 101: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

LGW-6Cobalt, total

ug/L

YearMedian ND/2

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-6Nickel, total

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-6Zinc, total

Significant Increasing Trend

ug/L

Year

1.00

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-7Arsenic, total

ug/L

YearManual ND/2

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-7Barium, total

ug/L

Year

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-7Cadmium, total

Confidence Limit Exceeds Standard

ug/L

YearManual ND/2

0.100

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-7Cobalt, total

ug/L

YearMedian ND/2

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-7Nickel, total

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-7Zinc, total

Significant Increasing Trend

ug/L

Year

1.00

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 102: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

LGW-8RArsenic, total

ug/L

YearManual ND/2

0.01.02.03.04.05.06.07.08.09.0

10.0

09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-8RBarium, total

ug/L

Year

10.0

100.

1000.

10000.

09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-8RCadmium, total

ug/L

YearManual ND/2

0.000.501.001.502.002.503.003.504.004.505.00

09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-8RCobalt, total

ug/L

YearMedian ND/2

0.02.04.06.08.0

10.012.014.016.018.020.0

09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-8RNickel, total

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-8RZinc, total

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

10000.

09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-9Arsenic, total

ug/L

YearManual ND/2

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-9Barium, total

Significant Increasing Trend

ug/L

Year

0.200.400.600.800.

1000.1200.1400.1600.1800.2000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-9Cadmium, total

Confidence Limit Exceeds Standard

ug/L

YearManual ND/2

0.100

1.00

10.0

100.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 103: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

LGW-9Cobalt, total

ug/L

Year

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-9Nickel, total

Significant Decreasing Trend

ug/L

Year

0.50.

100.150.200.250.300.350.400.450.500.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

LGW-9Zinc, total

Significant Increasing Trend

ug/L

Year

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-21Arsenic, total

ug/L

Month / Year Manual ND/2

0.01.02.03.04.05.06.07.08.09.0

10.0

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-21Barium, total

ug/L

Month / Year

0.200.400.600.800.

1000.1200.1400.1600.1800.2000.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-21Cadmium, total

ug/L

Month / Year Manual ND/2

0.000.501.001.502.002.503.003.504.004.505.00

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-21Cobalt, total

Exceedance / Sig. Decreasing Trend

ug/L

Month / Year

0.5.

10.15.20.25.30.35.40.45.50.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-21Nickel, total

ug/L

Month / Year

0.50.

100.150.200.250.300.350.400.450.500.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-21Zinc, total

ug/L

Month / Year

10.0

100.

1000.

10000.

jan15

may sep jan16

may sep jan17

may sep jan18

may sep jan19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 104: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

MW-2NArsenic, total

ug/L

YearManual ND/2

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2NBarium, total

Significant Increasing Trend

ug/L

Year

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2NCadmium, total

ug/L

YearManual ND/2

0.000.501.001.502.002.503.003.504.004.505.00

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2NCobalt, total

ug/L

YearMedian ND/2

0.02.04.06.08.0

10.012.014.016.018.020.0

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2NNickel, total

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-2NZinc, total

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

10000.

06 07 08 09 10 11 12 13 14 15 16 17 18 19

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3NArsenic, total

ug/L

YearManual ND/2

0.5.

10.15.20.25.30.35.40.45.50.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3NBarium, total

ug/L

Year

0.200.400.600.800.

1000.1200.1400.1600.1800.2000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3NCadmium, total

Exceedance / Sig. Increasing Trend

ug/L

YearManual ND/2

0.100

1.00

10.0

100.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 105: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

MW-3NCobalt, total

ug/L

YearMedian ND/2

0.02.04.06.08.0

10.012.014.016.018.020.0

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3NNickel, total

Significant Increasing Trend

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-3NZinc, total

Significant Increasing Trend

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

10000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7NArsenic, total

ug/L

YearManual ND/2

0.5.

10.15.20.25.30.35.40.45.50.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7NBarium, total

Significant Decreasing Trend

ug/L

Year

10.0

100.

1000.

10000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7NCadmium, total

ug/L

YearManual ND/2

0.100

1.00

10.0

100.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7NCobalt, total

Significant Decreasing Trend

ug/L

YearMedian ND/2

1.00

10.0

100.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7NNickel, total

Significant Decreasing Trend

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-7NZinc, total

Significant Decreasing Trend

ug/L

Year

10.0

100.

1000.

10000.

0.096 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 106: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Confidence Limits (Assessment)

MW-8NArsenic, total

ug/L

YearManual ND/2

0.5.

10.15.20.25.30.35.40.45.50.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8NBarium, total

ug/L

Year

10.0

100.

1000.

10000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8NCadmium, total

Confidence Limit Exceeds Standard

ug/L

YearManual ND/2

0.100

1.00

10.0

100.

1000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8NCobalt, total

ug/L

YearMedian ND/2

0.02.04.06.08.0

10.012.014.016.018.020.0

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8NNickel, total

Significant Decreasing Trend

ug/L

Year

0.100.200.300.400.500.600.700.800.900.

1000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

MW-8NZinc, total

Significant Decreasing Trend

ug/L

YearMedian ND/2

1.00

10.0

100.

1000.

10000.

96 98 00 02 04 06 08 10 12 14 16 18 20

Trend test

Samples

95% LCL

Standard

Detect

ND

Man. outlier

Prepared by: Otter Creek Environmental

Analysis prepared on: October 2018Eco-Vista [gw]

Page 107: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Attachment 2 — Revised Page 6, Second Half 2018 Groundwater Monitoring

Report

Page 108: Microsoft Outlook - Memo Style · The most useful technique for intrawell comparisons is the combined Shewhart-CUSUM control chart. This control chart procedure is useful because

Groundwater Monitoring Report (Revised January 22, 2019) Eco-Vista Landfill, Arkansas 6

On June 12, 2014, a letter detailing the ongoing gas extraction efforts at the facility was submitted to ADEQ (Document 66045). Document 69516 “Approval of Plan for Modification to the Gas Extraction System at the Eco-Vista Landfill” was received on May 5, 2016. ADEQ approved the final nature and extent work plan (Documents 70569 and 70585) and well installation began in December 2016. The installation of the eight new nature and extent wells (NE-6 through NE-13) at the site was completed in December 2016 and a field activity report was submitted to ADEQ (Document 71488). Quarterly monitoring was conducted in 2017 and a report that discussed the findings of the nature and extent investigation was submitted to ADEQ on January 19, 2018 (Document 73049). As stated in the January 2018 report, current corrective action at the site is based on impacts to groundwater from landfill gas. Based on the results of the investigation, the CAMP for the facility will be updated and include representative sampling from select nature and extent wells to monitor the effectiveness of corrective action measures. Upon ADEQ approval of the January 19, 2018 report, the facility anticipates submitting the updated CAMP. Beginning with the First Half 2019 monitoring period, wells NE-6 through NE-13 will be sampled semi-annually (per Document 74554). In correspondence dated July 18, 2018, ADEQ issued comments (Document 74217) on the Nature and Extent Report (Document 73049). In correspondence dated September 12, 2018, FTN issued a response (Document 74554) to the ADEQ comments. In correspondence dated September 28, 2018, ADEQ issued a response (Document 74635) to FTN’s comments. The site is currently compiling a Nature and Extent Investigation Work Plan to address the ADEQ comments.

7.0 CONCLUSIONS The following conclusions are based on the results of the Second Half 2018 groundwater sampling events and analytical testing: Groundwater Flow The water level data for the third quarter (July 2018) and fourth quarter (October 2018) sampling events indicated that the groundwater flow direction within the uppermost aquifer was to the southeast across the site, consistent with past events. The groundwater flow rate was 1.43 feet/day (July 2018) and 1.43 feet/day (October 2018), consistent with past events. Analytical Results The GWPSs were exceeded for cobalt at MW-21, LGW-10, and NE-5; and cadmium at MW-3N, MW-8N, LGW-6, LGW-7, and LGW-9 during the July 2018 and October 2018 events, consistent with recent events. During the July 2018 event, VOCs were detected above the PQLs at quantified concentrations at MW-21, LGW-10, and NE-5, consistent with past events. Vinyl chloride was detected for the first time at LGW-2 during the July 2018 event. None of the July 2018 VOC detections exceeded a GWPS. Acetone was detected at quantified concentrations at various wells; however, was also detected in the Equipment Blank and Trip Blank 1. Acetone is a known laboratory contaminant and may represent a laboratory artifact. During the October 2018 event, VOCs were detected above the PQLs at quantified concentrations at LGW-2, LGW-10, and NE-5. Acetone was detected at quantified concentrations at various wells but was also detected at quantified levels in the Equipment Blank and laboratory Method Blank. With regards to acetone detections, as noted above, acetone is a known laboratory contaminant and may represent a laboratory artifact. The VOC detections at LGW-10 and NE-5 were consistent with previous events. Vinyl chloride was verified detected at LGW-2 during the October 2018 event.