ML16256A778

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Submittal of Corrected May 2016 Toxicity Report
ML16256A778
Person / Time
Site: Sequoyah  Tennessee Valley Authority icon.png
Issue date: 09/07/2016
From: Schwartz C
Tennessee Valley Authority
To: Hall A
Office of Nuclear Reactor Regulation, State of TN, Dept of Environment & Conservation, Div of Water Resources
References
TN0026450
Download: ML16256A778 (88)


Text

{{#Wiki_filter:Tennessee Valley Authority, Post Office Box 2000, Soddy Daisy, Tennessee 37384-2000 September 7, 2016 Ms. Angela Hall Tennessee Department of Environment and Conservation Division of Water Resources William R. Snodgrass Tennessee Tower 312 Rosa L. Parks Avenue, 11th Floor Nashville, Tennessee 37243

Dear Ms. Hall:

TENNESSEE VALLEY AUTHORITY (TVA) - SEQUOYAH NUCLEAR PLANT (SQN) - NPDES PERMIT NO. TN0026450 - May 2016 Toxicity.Report - Corrected ) Enclosed is a corrected copy of the May 2016 Toxicity report. The toxicity report previously submitted with the June 2016 DMR may have had missing pages. If you have any questions or need additional information, please contact Millicent Garland by email at mrmoore@tva.gov or by phone at (423) 843-6714.. I certify under penalty of law that this document and all attachments were prepared under my direction or supervision in accordance with a system designed to assure that qualified personnel properly gather and evaluate the information submitted. Based on my inquiry of the person or persons who manage the system, or those persons directly responsible for gathering the information, the information submitted is, to the best of my knowledge and belief, true, accurate, and complete. I am aware that there are significant penalties for submitting false information, including the possibility of fine and imprisonment for knowing violations. Sincerely, Enclosures cc (Enclosures): Chattanooga Environmental Field Office Division of Water Pollution Control State Office Building, Suite 550 540 Mccallie Avenue Chattanooga, Tennessee 37402-2013 U.S. Nuclear Regulatory Commission Attn: Document Control Desk Washington, DC 20555

TENNESSEE VALLEY AUTHORITY TOXICITY TEST REPORT INTRODUCTION I EXECUTIVE

SUMMARY

Report Date: June 16, 2016

1. Facility I Discharger: Seguoyah Nuclear Plant I TV A
2. County I State:. Hamilton I Tennessee
3. NPDES Permit#: TN0026450
4. Type of Facility: Nuclear-Fueled Electric Generating Plant
5. Design Flow (MGD): 1,579
6. Receiving Stream: Tennessee River CTRM 483.6)
7. lQIO: 3,491
8. Outfall Tested: 101
9. Dates Sampled: May 15-20, 2016
10. Average Flow on Days Sampled (MGD): 1794, 1797, 1789
11. Pertinent Site Conditions:* Production I operation data will be provided upon request.
12. Test Dates: May 17 -24. 2016
13. Test Type: Short-term Chronic Definitive
14. Test Species: Fathead Minnows (Pimephales promelas)

Daphnids (Ceriodaphnia dubia)

15. Concentrations Tested(%):

Pimephales promelas: UV treated Outfall 101: 10.7, 21.4. 42.8, 85.6, 100 UV treated Intake: 100 Ceriodaphnia dufoa: Non-treated Outfall 101: 10.7, 21.4. 42.8, 85.6. 100 Non-treated Intake: 100

16. Permit Limit Endpoint(%): Outfa.11101: ICJs = 42.8%
17. Test Results: Outfall 101: Pimephales promelas: IC?5 > 100%

Ceriodaplinia dubia: ICJ5 > 100% Page 1of87

18. Facility

Contact:

Millicent Garland Phone#: (423) 843-6714 ~9. Consulting I Testing Lab: Environmental Testing Solutions. Inc.

20. Lab

Contact:

Jim Sumner Phone#:. (828) 350-9364

21. TVA

Contact:

Donald W. Snodgrass Phone#: (256) 386-2787

22. Notes: Exposures to samples collected May 15 - 20, 2016 from Outfall 101 resulted in no toxic effects to fathead minnows or daphnids. The resulting IC2s values, for both species, were > 100 percent. Exposure of daphnids to intake samples resulted in no significant difference from the control during this study period. Exposure of minnows to intake samples reduced minnow growth significantly from the control.

Page 2of87

METHODS

SUMMARY

Samples:

1. Sampling Point: Outfall 101, Intake
2. Sample Type: Composite
3. Sample Information:

Date Date Date (MM-DD-YY) (MM-DD-YY) Arrival Initial (MM-DD-YY) Sample Time (ET) Time (ET) Temp. TRC* Time (ET) ID Collected Received (aC) (mg/L) Last Used By 101 05-15-16 0705 to 05-16-16 1250 3 t <0.10 05-17-16 1333 05-16-16 0605

1. ' 1.5 05-18-16 1234 Intake 05-15-16 0720 to 05-16-16 1250 2.4

<0.10 05-17-16 1333 05-16-16 0620 05-18-16 1234 101 05-17-16 0700 to 05-18~16 1200 1.0, 1.2t <0.10 05-19-16 1233 05-18-16 0600 05-20-16 1240 Intake 05-i7-16 0715 to 05-18-16 1200 0.4 <0.10 05-19-16 1233 05-18-16 0615 05-20-16 1240 05-19-1.6 0650 to 05-21-16 1237 101 05-20-16 1225 2.0, l.Ot <0.10 05-22-16 1250 05-20-16 0550 05-23-16 1305 05-19-16 0705 to 05-2}-16 1237

  • Intake 05-20-16 0605 05-20'-16 1225 1.8

<0.10 05-22-16 1250 05-23-16 1305

  • TRC =Total Residual Chlonne tsamples were collected in two 2.5 gallon cubitainers. Temperature was measured in each cubitainer upon arrival.
4. Sample Manipulation: Samples from Outfall 101 and intake were wanned to test temperature (25.0 +/- l.0°C) iri. a warm water bath.

Aliquots ofOutfall 101 and Intake samples were UV-treated through a 40-watt Smart UV Sterilizer (manufactured by Emperor Aquatics, Inc.) for 2 minutes. Page 3of87

Pimephales promelas Test Organisms:

1. Source:

In-house Cultures

2. Age:

< 24-hours old Test Method Summary:

1. Test Conditions:

Static. Renewal

2. Test Duration:

7 days

3. Control I Dilution Water: Moderately Hard Svnthetic
4. Number of Replicates:

1:

5. Organisms per Replicate: lQ
6. Test Initiation: (Date/Time): 05-17-16 1333 ET
7. Test Termination: (Date/Time): 05-24-16 1238 ET
8. Test Temperature: Outfall 101:

Mean= 24.7°C (24.2 -25.0°C)

9. Physical I Chemical Ceriodaphnia dubia In-house Cultures

< 24-hours old Static. Renewal Until at least 60% of control females have 3 broods Moderately Hard Svnthetic l 05-17-16 0827ET 05-24-16 0830 ET* Mean= 24.8°C (24.2 -25.2°C) Measurements: Alkalinity. hardness, total residual chlorine. and conductivity were measrired at the laboratory in each 100% sample. Daily temperatures were measured in one replicate for each test concentration. Pre~ and post-exposure test solutions were analyzed daily for pH and dissolved oxygen.

10. Statistics:

Page4 of87 Statistics were performed according to methods prescribed by EPA using ToxCalc version 5.0 statistical software (Tidepool Scientific Software, McKin:Ilevville, CA).

TOXICITY TEST RESULTS (see Appendix C for Bench Sheets)

1.

Results of a Pimephales promelas Chronic/ 7-day Toxicity Test. (Genus species) (Type I Duration) Conducted May 17 - 24, 2016 using effluent from Outfall 101. Test Percent Surviving' Solutions (time interval used-days) (%Effluent) 1 2 3 4 5 6 7

Control, 100 100 100 100 100 100 100 UV-treated 10.7%

100 100 100 \\ 100 100 100 100 21.4% 100 100 100 100 100 100 100 42.8% 100 100 100 100 100 100 100 85.6% 100 100 100 100 100 100 100 100.0% 100 100 100 100 100 100 100 Intake 100 100 100 100 100 100 100

Control, 100 100 100 100 100 100 100 Non-treated Test Solutions Mean Dry Weight (mg)

(% Effluent) (replicate number) 1 2 3 4 Mean

Control, 0.470 0.421 0.485 0.552 0.482 UV-treated 10.7%

0.546 0.585 0.593 0.507 0.558 21.4% 0.505 0.470 0.614 0.563 0.538 42.8% 0.509 0.516 0.514 0.564 0.526 85.6% 0.439 0.455 0.478 0.452 0.456 100.0% 0.453. 0.482 0.428 0.491 0.464 Intake 0.378 0.460 0.405 0.406 0.412

Control, 0.573 0.555 0.565 0.628 0.580 Non-treated IC2s Value: > 100%

Calculated TU Estimates: < 1.0 TUc* Permit Limit: 42.8% Permit Limit: 2.3 TUc 95% Confidence Limits: Upper Limit: NA Lower Limit: NA

  • TUa = 100/LC50: TUc = 100/ IC2s Page 5 of87

TOXICITY TEST RESULTS (see Appendix C for Bench Sheets)

2.

Results of a Ceriodaphnia dubia Chronic/ 7-day Toxicity Test. (Genus species) (Type I Duration) Conducted May 17 - 24, 2016 using effluent from Outfall IOI. Percent Surviving Test (time interval used - days) Solutions 1 2 3 4 5 6 7 (%Effluent) Control 100 100 100 100 100 100 100 10.7% 100 100 100 100 .100 100 100 21.4% 100 100 100 100 100 100 100 42.8% 100 100 100 100 100 100 100 85.6% 100 100 100 100 100 100 100 100.0% 100 100 100 100 100 100 .100 Test Solutions Reproduction (#young/female/7 days) (% Effluent) Data (replicate number) 1 2 3 4 5 6 7 8 9 10 *Mean Control 33 29 30 29 27 29 ~7 28 29 29 29.0 10.7% 29 32 34 29 28 31 29 30 29 32 30.3 21.4% 31 30 31 35 30 29 27 32 32 30 30.7 42.8% 32 34 32 32 33 33 29 30 32 35 32.2 85.6% 34 33 34 32 36 31 35 32 29 31 32.7 100.0% 34 35 36 33 37 35 34. 37 33 33 34.7 IC2s Value: > 100% Calculated TU Estimates: < 1.0 TUc* Pennit Limit: 42.8% Permit Limit: 2.3 TUc 95% Confidence Limits: Upper Limit: NA Lower Limit: NA

  • TUa = 100/LCso: TUc = 100/ IC2s Page 6 of87

TOXICITY. TEST RESULTS (see Appendix C for Bench Sheets)

2.

Results of a Ceriodaphnia dubia Chronic/ 7-day Toxicity Test. (Genus species) (Type I Duration) Conducted May 17 - 24, 2016 usin$ water from Intake Percent Surviving Test (time interval used ~ days) Solutions 1 2 3 4 5 6 7 (%Effluent) Control 100 100 100 100 100 100 100 Intake 100 100 100 100 100 100 100 Test Solutions Reproduction (#young/female/7 days) (% Effluent) Data (replicate number) 1 2 3 4 5 6 7 8 9 10 Mean Control 27 26 28 29 31 30 31 29 30 32 29.3 Intake 34 35 32 28 31 29 30 29 32 32 31.2 IC2s Value: > 100% Calculated TU Estimates: < 1.0 TUc* Pennit Limit: N/ A. Permit Limit: N/ A 95% Confidence Limits: Upper Limit: NA Lower Limit: NA

  • TUa = 100/LC50: TUc = 100/ IC2s REFERENCE TOXICANT TEST RESULTS (see Appendix A and D)

Species Date Time Duration Toxicant Results (lCzs) Pimephales promelas May 17 -24, 2016 1300 7-days KCl 0.64 g/L Ceriodaphnia dubia May 10- 17, 2016 0940 7-days NaCl 1.06 g/L Page 7of87

Pl-IYSICAL/CHF:M ICAL

SUMMARY

Water Chemislly Mean Values and Ranh>es for UV-lrca!cd Pimeplwles pm111elas and Non-treated Ceriodaplmia dubia. Sequoyah Nuclear Plant (SQN), Ellluenl Outfall I OJ and lnlake pcrl01111cd May 17-24, 2016. Test Sample ID Temncmiurc ("CJ Dissolved OXY!!en (m!!IL) Initial Final Initial Final

Cnntrol, 24.7

.24.5 7.8 7.8 Nun-lrcalcd 24.5 - 24.8 24.3 - 24.6 7.7 - 7.8 7.7 - 7.9

Cnnlrnl, 24.8 24.5 7.8 7.8 llV-ln*nlc.*d 24.7 - 24.8 24.2 - 24.6 7.7 - 7.9 7.8 -

8.0 10.nr.1 24.8 24.5 7.8 7.8 24.7 - 24.9 24.3 - 24.7 7.7 - 7.9 7.8 - 7.9 24.8 24.5 7.9 7.9 1: 21.4"/.1 ~ 24.7 - 24.9 24.3 - 24.7 7.8 - 7.9 7.8 - 7.9 ~

  • 24.8 24.5 7.9 7.8 42.8'X1

..::: e-24.7 - 24.9 24.3 - 24.7 7.8 - 8.0 7.7 - 7.9 ~ 85.6'Yo 24.8 24.6 7.9 7.9 24.7 - 24.9 24.3 - 24.8 7.8 - 8.0 7.8 - 8.0 100% 24.9 24.5 7.9 7.9 24.8 - 25.0 24.2 - 24.7 7.8 - 8.0 7.7 - 8.0 Intake 24.8 24.5 7.9 7.9 24.7 - 25.0 24.3 - 24.8 7.8 - -8.0 7.8 - 8.1

Cnnlrol, 24.8 24.8 7.8 7.8 Non-I rented 24.7 - 24.9 24.4 - 25.2 7.7 -

7.9 7.7 - 7.8 I0.7% 24.8 24.8 7.8 7.8 24.7 - 25.0 24.6 - 25.0 7.7 - 7.8 7.7 -- 7.9 24.8 24.7 7.8 7.9 oC) 21.4'Yc1 .§ .24. 7 - 25.0 24.6 - 24.8 7.7. - 8.0 7.8 - 7.9 24.9 24.7 ' 7.9 - 7.9 42.8°/.1 §< 24.7 - 25.0 24.2 - 25.0 7.8 - 8.0 7.7 - 7.9 24.9 24.7 7.9 7.9

  • ~

85.6% d 24.8 - 25.0 24.4 - 25.0 7.8 - 8.0 7.7 - 8.0 !00% 24.9 24.7 7.9 7.9 24.8 - 25.0 24.4 - 24.9 7.9 - 8.1 7.7 - 8.0 Intake 24.9 24.8 7.9 7.9 24.8 - 25.0 24.4 - 25.l 7.8 - 8.1 7.8 - 8.0

  • Nole: Total residual chlorine was performed on non-treated Outfall 101 and Intake samples.

Overnll tempernture ( 0C) Pimeplwles pro111e/as Ceriodaplmia tlubia Avemgc 24.7 24.8 Minimum Maximum 24.2 25.0 24.2 25.2 pH (S.U.) Conductance Alkalinity Hanlncss

  • Total Residual Initial Final (111nhos/c111) (mg/L CnC0.1) (mg/L CaC03)

Chlo1ine (mg/L) 7.48 7.20 313 61 87 7.30 - 7.65 7.00 - 7.48 299 - 322 61 - 62 86 - 88 7.45 7.23 . 307 62 88 7.22 - 7.64 6.97 - 7.63 297 - 321 61 - 63 88 - 88 7.44 7.22 296 7.23 - 7.65 6.95 - 7.58 287 - 307 7.43 7.22 282 7.23 - 7.65 6.99 - 7.61 273 - 290 7.42 7.20 255 7.23 - 7.64 6.95 - 7.56 251 - 261 7.42 7.17 205 7.22 - 7.64 6.90 - 7.52 201 - 208 7.41 7.23 187 62 71 <0.10 7.20 - 7.63 6.98 - 7.53 183 - 192 60 - 64 68 72 <0.10 - <0.10 7.41 7.25 199 65 73 <0.10 7.18 - 7.66 6.97 - 7.63 196 - 205 64 - 68 68 - 80 <0.10 - <0.10 7.49 7.35 313 61 87 7.30 - 7.65 7.13 - 7.56 299 - 322 61 62 86 - 88 7.43 7.35 289 7.22 - 7.63 7.17 - 7.59 261 - 312 7.44 7.33. 282 7.24 - 7.64 7.08 - 7.59 274 - 291 7.43 7.33 254 7.22 - 7.64 7.11 - 7.59 247 - 261 7.42 7.32 - 204 7.20 - 7.63 7.05 - 7.59 201 - 210 7.40 7.31 186 65 75 <0.10 7.17 - 7.63 7.06 - 7.59 182 - 191 64 66 72 76 <0.10 - <0.10 7.42 7.33 198 71 73 <0.10 7.21 - 7.62 7.11 - 7.58 188 - 204 68 - 73 72 - 76 <0.10 - <0.10

SUMMARY

I CONCLUSIONS Exposures to samples collected May 15 -20, 2016 from Outfall IOI resulted in no toxic effects to fathead minnows or daphnids. The resulting IC25 values, for both species, were > 100 percent. Exposure of daphnids to intake samples resulted in no significant difference from the control during this study period. Exposure of minnows to intake samples reduced minnow growth significantly from the control. Page 9of87

Appendix A ADDITIONAL TOXICITY TEST INFORMATION

SUMMARY

OF METHODS

1. Pimephales promelas Tests were conducted according to EPA-821-R-02~013 (October 2002) using four replicates, each containing ten test iorganisms, per treatment. Test vessels consisted of 500-mL plastic disposable cups, each containing 250-mL of test solution.
2. Ceriodaphnia dubia Tests were conducted according to EPA-82l-R-02-013 (October 2002) using ten replicates, each containing one test organism, per treatment. Test vessels consisted of 30-mL polypropylene cups, 1each containing 15-mL oftest solution.

DEVIATIONS I MODIFICATIONS TO TEST PROTOCOL

1. Pimephales promelas Samples used in the fathead minnow test were exposed to UV light for two minutes prior to introduction of test organisms. UV treatment is used to control interference of fish pathogens. This treatment n;iethod was approved on November 23, 2015.by the State of Tennessee in a letter from Jessica Murphy to Terry Cheek, Senior Manager of TV A Water Permits, Compliance, and Monitoring. *
2. Cerfodaphnia dubia None DEVIATIONS I MODIFICATIONS TO PRETEST CULTURE OR HOLDING OF TEST ORGANISMS*

I.. Pimephales promelas None

2. Ceriodaphnia dubia None Page 10of87

PHYSICAL AND CHEMICAL METHODS

1. Reagents, Titrants, Buffers, etc.: All chemicals were certified products used before t;ixpiration dates (where applicable).

I

2. Instruments: All identification, service, and calibration information pertaining to laboratory instruments i~ recorded in calibration and maintenance logbooks.
3. Temperature was measured by SM 2550 B-2000.
4. Dissolved oxygen was measured by SM 4500-0 G-2001.
5. The pH was measured by SM 4500-H+ B-2000.
6. Conductance was measured by SM 2510 B-1997.
7. Alkalinity was measured by SM 2320 B-1997.
8. Total hardness was measured by SM 2340 C-1997.
9. Total residual chlorine was measured by ORION 97-70-1977.

QUALITY ASSURANCE Toxicity Test Methods: All phases of the study including, but not limited to, sample collection, handling and storage, glassware preparation, test organism culturing/acquisition and acclimation, test organism handling during test, and maintaining appropriate test conditions were conducted according to the protocol as described in this report and EPA-821-R-02-013. Any known deviations were noted during the study and are reported herein. . REFERENCE TOXICANT TESTS (See Appendix D for control chart information)

1. Test Type: 7-day chronic tests with results expressed as IC25 values in g/L KCl or NaCL
2.

Standard Toxicant: Potassium Chloride (KCI crystalline) for Pimephales promelas. Sodium Chloride (NaCl crystalline) for Ceriodaphnia dubia.

3. Dilution Water Used: Moderately hard synthetic water.
4.

Statistics: ToxCalc software Version 5.0 was used for statistical analyses. Page 11of87

REFERENCES

1. NPDES Permit No. TN0026450.
2. USEP A. Short-Term Methods for Estimating the Chronic Toxicity of Effluents and Receiving Waters to Freshwater Omanisms. EPA-821-R-02-013 (October 2002).
3. Standard Methods for the Examination of Water and Wastewater. 22nd Edition, 2012.
4. Quality Assurance Program: Standard Ooerating Procedures, Environmental Testing Solutions, Inc (most current version).

Page 12of87

Page 13of87 Sequoyah Nuclear Plant Biomonitoring May 17 -24, 2016 AppendixB Diffuser Discharge Concentrations of Total Residual Chlorine, Diffuser Discharge Concentrations of Chemicals Used to Control Microbiologically Induced Corrosion and Mollusks During Toxicity Test Sampling

Table B-1. Sequoyah Nuclear Plant Outfall 101 Diffuser Discharge Concentrations of Chemicals Used to Control Microbiologically Induced Corrosion and Mollusks, During Toxicity Test Sampling, February 6, 2005 -May 20, 2016 Date $~1um. Towerbrom * *pct:;::222 PCL-401 HYJ>Ci9bl()rit~ mg!L

  • fug/r; ***

mo/L TRC

.Ph_o.:;:rih_

.*.... _a_t_-~-**.. *.. Copolymer . *.:. JllT~:_.. _.R&fIJ_._*c*_*-.. --*._. "'r- -( '. ~~ *' ~ :-,~_- : 02/06/2005 0210712005 02/08/2005 02/09/2005 02/10/2005 02/11/2005 06/05/2005 06/06/2005 06/07/2005 06/08/2005. _, 06/09/2005 0611012005 07/17/2005 07118/2005 07119/2005 07/20/2005 07/21/2005 07/22/2005 10/30/2005 10/31/2005 11/01/2005

~..

11/0212005 11/03/2005 11/04/2005 7 11114/2005 11/15/2005 I 1/16/2005 11/17/2005 11/18/2005 11/19/2005 'Page 14 of87 <0.0042 <0.0116 <0.0080 0.0199 <0.0042 0.0155 0.0063 0.0043 0.0103 0.0295 0.0129 0.0184 0.0109 0.0150 0.0163 0.0209 0.0242 0.0238 0.0068 0.0112 0.0104 0.0104 0.0117 0.0165 0.0274 0.0256 0.0234 0.0231 0.0200 0.0116 . 6~02~.,. 0,026**:; i"lil~~ 0.010 0.010 0.010 0.010 0.010 0.010 0.009 0:009 0.009 0.009 0.009 0.018 .*-~ --,:.:.~.. Nalco 73551 mg/L EOIPO 0.007 0.007 0.014 0.014 Ji:l5QM

  • niWL

- Quat 0.037 0.037 0.037 0.036 '0.036 . 0.036 O.Q35 0;036 0:036 0,035

/ Date 11112/2006. 11/13/2006 11114/2006 11115/2006 11/16/2006 11/17/2006 *- 11/26/2006.. 1112712006. 11128/2006 11/29/2006 11/30/2006 12/0112006. 05/28/07 05/29/07 05130107 05/31/07 06/01/07 06/02/07 12/02/07 12/03/07 12/04/07 12/05/07 12/06/07 12/07/07 04/13/08 04/14/08 04/15/08 04/16/08 04/17/08 04118/08 10/26/08 10/27/08 10/28/08 10/29/08 10/30/08 10/31/08 Table B-1. Sequoyah Nuclear Plant Outfall IOI Diffuser Discharge Concentrations of Chemicals Used to Control Microbiologically Induced Corrosion and Mollusks, During Toxicity Test Sampling, February 6, 2005 - May 20, ~016 0.0260 0.0151 0.0172 0.0154 0.0086

  • l:, _._,.
. ' - ~.

PCL-401 mg/L Copolymer -*.~.

    • r.,

~-- - -.-. - ' ~..:*. - 0.017 1 0.018 Page 15 of 87 -

\\0.037 t~o:o~1 -

'.,_6,037 . :;Q.037 -. ~- '='_'.{L036 '::.;9p'~6. >,.*0.0.:'16

.yo;o36
  • 0;041 0~041 0,041

. 0.041 MSW 101 mg/L Phos hate 0.015 0.015 O.Dl5 O.Dl5 O.Dl5 0.015 0.030 0.030 0.030

Date 02/08/09 02109109 02110109 02111109 02/12/09 02/13/09 05110109 05111109 05/12/09 05113109 05/14/09 05/15/09 11115/09 11116/09 11/17/09 11/18/09 11119/09 11/20/09 05109110 05110110 05111110 05112110 05/13110 05/14110 Table B-1. Sequoyah Nuclear Plant Outfall 101 Diffuser Discharge Concentrations of Chemicals Used to Control Microbiologically Induced Corrosion and Mollusks, During Toxicity Test Sampling, February 6, 2005 -May 20, 2016 0.0197 0.0237 0.0104 '0.0155 0.0106 0.0129 ' ~ 0.0415 O.Oo53 0.0049 <0.0141 <0.0160 0.025., 0.0152 0.0255 Page 16 of87 H-150M

  • MSW.

mg/L

  • 101.

Quat -mg/L 0.0446 0.0396 0.0396 0.0397 ~Jiosph~te

r.
  • ~.:. -

Table B-1. Sequoyah Nuclear Plant Outfall IOI Diffuser Discharge Concentrations of Chemicals Used to Control Microbiologically Induced Corrosion and Mollusks, During Toxicity Test Sampling, Date 10/31/10 11/01/10 11/02/10 11/03/10 11/04/10 11/05/10 05/01/2011 0510212011 05/03/2011 05/04/2011 05/05/2011 05/06/2011 c 11/06/2011,_ - 11/07/2011 - - 11/08/2011 11/09/2011. 11110/2011 11111/2011.. 05/06/2012 >"'":.!.';/' 05/07/2012. 05/08/2012 -... - 05/09/2012 ** 05/10/2012 \\' 05/11/2012 - 08/12/2012 08/13/2012 08/14/2012 08/15/2012. 08/16/2012 ' 08/17/2012 ! -., \\ 05/12/20i3 05/13/2013 ~-. 05/14/2013 ' 05/15/2013 05/16/2013 05/17/2013 09/15/2013 09/16/2013 09/17/2013 09118/2013 09/19/2013 09/20/2013 0.0256 0.0209 0.0279 0.0076 0.0446 0.0099 0.0091 0.0096 0.0229 0.0063 0.0072 0.0107 0.0217 0.0172 0.0173 Page 17 of87 February 6, 2005 -May 20, 2016 Nalco 73551 mg/L EOIPO 0.028 0.039 0.039 0.036 0.036 .'.'Specfuis; H-150M 'MSW Floguard ,;¢$,1J30Q( mg/L i )01-MS6236 !1~.* Quat ',~. Ph:'~ O~D3T'-;

  • -BY0_)1-. -*

~*: ~...: '~.

  • ~* *:*"* .? :

O:Q~79 0.0379 0.0379 ,:,~'. 0.029 0.029 0.029 0.029 0.029 0.032 0.064 0.064 0.064 0.032 0.032 0.03 0.03 0.03 0.03 0.03 0.03

Table B-1. Sequoyah Nuclear Plant Outfall 101 Diffuser Discharge Concentrations of Chemicals Used to Control Mici-obiologically Induced Corrosion and Mollusks, During Toxicity Test Sampling, February 6, 2005 -May 20, 2016

  • S9.4Nw': Towerbro
H:W~'

mg!L Date clilorite TRC .(${~.~ 05/04/2014 05/05/2014' 0510612014 ' 05/07/2014 05/08/2014 05/09/2014 09/07/2014 09/08/2014 09/09/2014 09/10/2014 *. 09/11/2014.:* ~-*.-.... 09112/2014 08/09/2015 08/10/2015 08/1112015 08/12/2015 08/13/2015 08114/2015 10118/2015 10/19/2015 10/20/2015 10/2112015.. -**-

~,'*

10/22/2015 10/23/2015 ' 05/15/2016 ' 05/16/2016 05/17/2016 05/18/2016 05/19/2016 ' ' 05/20/2016 0.0118 0.0112 0.0096 0.0164 0.0235 0.0110 0.0070 0.0074 0.0130 0.0174 0.015p 0.0209 0.0210 0.036'1 0.0254 0.0261 Page 18 of87 . / 0.03 0.03 0.03

l.

Page 19of87 Sequoyah Nuclear Plant Biomonitoiing May 17 - 24, 2016 Appendix C Chain of Custody Records and Toxicity Test Bench Sheets

BIOMONITORING CHAIN OF CUSTODY RECORD Page~l~of~l~ 'l!jent TV A Environmental Testing So~ution, Inc. Delivered By (Circle One): FedEx UPS Bus -Client '@oject Name: Sequoyah NP Toxicity 351 Depot Street. ~

Sonic... V-eli'11e.ry

@:>.Number: NIA Asheville, NC Other (specify): ~ility Sampled: Sequoyah NP . 28801 General Comments* 1ii(.)K.~awrp!r:5 f1r(),,,., /{)/.Ja,..jJlc-l"t? 06?.'i"O NPDES Number: TN0026450 Phone: .. 828-350~9364 I /:,,k ~7/f"f IJ-"n..Z-,ralc~ 5~?kre {)7i/ 7 C II d B /11~r~"-' tJ. /r?oNt' f >i<l~o.f" Fax: 828-350~9368 Jf /!)/ 8ac4 ~,,Pl~ vJ!l~../A'):',?ee/.z:b 6'v/~,.,.,-e.tf< o ecte~ ~ ~.-) /

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  • -K-01/s. Me'/lrls weYe ~~Ill!'~/ 1'-,e-~./~n.>::>4:

(/ v I I P"OJ e,U-~, lLl90 Container Field Identification I Number& Flow Rain Event? S11rt1ple Description Grab/Comp. Collection Daterrime Volume (MOD) Laboratory Use Collected (Mark as Appropriate) ~y*, .. :~* *;:2.<*,* -,;j:_*'. '..:\\.-.:*::~ ;_'. :'.:,;::, '.'>~i.. J : .. :) ~: Siert End ~,]~::-~~~;::~;{ i~iJ 0:~'.~~{~:{r' Yes If Yes, No Trace ETS Log Arrivnl.Tcmp. By Time Appear-Inches Number c*c> (.1 once S-15'"--/(,, 5'-/t,-11;. '/ \\\\.105\\~.0) \\$\\\\.C:,"C.... \\t.40 -1. SQN-101-TOX Comp 2(2.5gal) 1'11'3. si& ~- 1J10~ &.Jr /)IPOS° $JT SQN-INT-TOX Comp ~15'*/{p .)-/(, -/{;, 1(2.S gal) fl/II. 1 l~c.Gll? Dt.- -z.A *t. t \\-t:,u /.. ~7:JO G'JT' {) {p ;J.() fjr ~ Sample Custody - Fill Jn From Top Down f: C".S"TI>t\\-l 5eAl5 \\r.JTK,\\, ~~ ...ec. ~l'l\\Je.r. Relinquished By (Signature): Date/Time Received By (Signature): LK) 6-to~ COt-)b.lTl°l), ffc_ A~~ 1"1 Al..L at~ 1me SH-\\~,,)( d //Id -r\\J t\\

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5Hl\\(. bet..\\~ ~'\\ 0.5-- /l-/f; / 0 ~:/6' ET r C../.7\\. .? !hi_ Sa~\\L. ( ~~Iv.-- A~ Jb .S':. t 6.. / J, /;:J;$0 < ~ trs os-11.o ~11.:> * 'heii~ ~ '1.Sa ET f .v I Instructions: Clients should fill in all areas except those in the *'Laboratory Use" block. Biomonitoring samples arc preserved by storing them at 6°C and shipping them in ice. The hold time for each sample is 36 hours from the time of collection. Therefore. please collect and ship in such a way that !he labornlory will receive the st1mples with ample time to initiate testing within that time frame. Samples shipped overnight on Friday via FedEx or UPS must be marked for Saturday delivery or they will not an*ivc until the following Monday.

Whole Effluent Sample Receipt Log

  • sample temperature performed using Sample Receiving Thermometer: SN 130580085 Date Time Received,

Received

  • Sample Project Sample Sample name and description,_

State Comments Received Received by from Temp. (°C) number number 05*16*16 1250 J. Sumner TVA Courier 1.3/1.5 11480 160516.01 TVA - Sequoyah Nuclear Plant-101 TN 05*16*16 1250 J. Sumner TVA Courier 2.4 11480 160516.02 TV A* Sequoyah Nuclear Plant - Intake TN SOP G4 - Exhibit G4.2, revision 01-03-12

~ent: TVA fi,ject Name: Sequoyah NP Toxicity ~*Number: N/A ~ility Sampled: Sequoyah NP NPDES Number: TN0026450 v v I I BIOMONITORING CHAIN OF CUSTODY RECORD Environmental Testing Solution, Inc. 3 51 Depot Street. Phone: Fax: Asheville, NC 28801 828-350-9364 828-350-9368 Container Delivered By (Circle One): FedEx UPS Bus Page_l_of_l_ Client Field ldcntifrdtion I Sample Description Grab/Comp. Collection Dateffime Number&' Flow Volume (MGD) Rain Event? (Mark as Appropriate) p~ e,ct--Y: I l~ 80 Laboratory Use SQN-101-TOX Comp SQN-INT-TOX Comp }elinquished By ~gnature): Stan S-1'7*/(;p O'J()D~f,1 5,1rj..J{p IJ'1 /"'S' t"-'r c' Collected End 2(2.Sgal) ()~(){) f'61' 1(2.5 gal) t>(D t 'Se~r If Yes. Inches Sample Custody-.Fill In From Top Down Date/Time Received By (Signature): ( .l) v No Trace "'f. o.ol

f.

0.01 ETS Log Arrival Temp. By Numbor C°C> / 0S.*lcr*1" \\'2.00 ET" Time <c..T Appear-ance lnstrnctions: Clients should fill in all areas except those in the *'Laboratory Use block. Biomonitoring samples are preserved by storing them at 6°C and shipping them in ice. The hold time for each sample is 36 hours from the lime of collection. Therefore. please collect and ship in such a way that the laboratory will receive the samples with ample time to initiate testing within that time frame. Samples shipped overnight on Friday via FedEx or UPS must be marked for Saturday delivery or they will not arrive until the following Monday.

Date Time Received Received Received Received by from 05-18-16 1000 K.Keenan Fed* Ex 05-18-16 1000 K.Keenan Fed* Ex 05-18*16 1000 K.Keenan Fed. Ex 05*18*16 1000 K.Keenan Fed. Ex 05*18*16 12.00 J. Sumner TVA Courier 05*18~16 1200 J.sumntir TVA Courier 05-18-16 1451 J. Sumner TVACoui'ler OHS-16 1451 J. Sumner TVA Courier 05*18-16 1451 J. Sumner TVA Courier 05-18-16 1451 J. Sunnier TVA Courier r* . Whole Effluent Sample Receipt.log Page_kg

  • sample temperature performed using Sample Rccel*lng Thermometer: SN 130580085
  • Sample Project Sample Sample name and description State Comments Temp. (°C}

number number 0.7 11483 160518.Ol Washington WWTP NC 0.4 11484 160518 ;02 TVA - Allen Fossil Plant - Outfall 001 TN 0.3 11484 160518.03 TVA-Allen Fossil Plant-Intake TN 0.3 11484 160518.04 TVA -Allen FossilPlant-Upstream TN 1.0/1.2 11480. 160518.05 TVA-Sequoyah Nuclear Plant* 101 TN 0.4 . 11480

  • . 160518'.0(i TVA ~ Seauovah Ni.iclea.i' Plant - Intake.

TN 1.3 11485 160518,07 TVA. Shawnee NP - Outfall 001 AA KY 1.7 11485 160518.. 08 TVA* Shawnee NP - Outfall Intake AA KY 2.2 11485 160518.09' TVA. Shawnee NP. Outfall 001 AP KY 2.0 11485 160518.10 TVA* Shawnee NP-Outfall Intake AP KY SOP G4 - Exhibit G4.2, revision 01-03-12

BIOMONITORING CHAIN OF CUSTODY RECORD Page*_l_ of _1_ Gijent: TVA Environmental Testing Solution, Inc. Delivered By*(Circle One): fi>ject Name: Sequoyah NP Toxicity 351 Depot Street. FedEx UPS Bus Client P~. Number: N/A Asheville, NC Other (specify): Son]e_ De\\ivef( ClO 28801 General Comments: Ftltillty Sampled: Sequoyah NP . *' ~~~/,ps./;({)- /t>I' ~p1ere.!J1P?5' NPDES Number: TN0026450 .Phone: . 828-350-93 64 TV&>,,e ~?k..s /;o;-, ~I& .sa-_?le.,.._.a ~/S' r, jf- /OI o~a..e-p ~tfe ~$ 5),~p/ -60 Collected By: ~11Uc5 t>. J't'ft:JDre, r:i-n~.~~ Fax: 828-350-9368 6?Y1°reJ,..-e,rl;l'"a./ /~$_/,._J1 $1).u.~n;H -~--VP?- 'k~*;) ~ fJ1~J.P"h/...J~ µei'e 6,/~,l-kfil--ti.1t.;<<,~ {/ v . \\ .. Container. p rU)) ~ 1\\..ieo Field Identification'/ Grab/Comp. Number& Flow

  • Rain Event?

Sample Description Collection Datemme Volume (MGD) Laboratol;' Use Collected (Mark as Appropriate) F.t;t);\\',: ~:.:.:~; :\\~M~it{~~ ~t~~:.: ~;;:~Jt~~; S1art End . 1=~i;~;~;~~~~ f~l4~~:.Yes If Yes, No Trace ETSI.og Arrival Temp. By Time Appear-Inches Number f"Cl ance S-19,/a. s;Zo~lh x \\lQOS?b.o\\ -z.o, \\.0 't -~ "\\'il-'-, }{- SQN-101-TOX Comp C)IPsO ~ os-s-o ~-* 2(2.Sgal) 1'7gq, 1'11# 5-/11-1~ s--w-1~ x ~~(}Sll)4 t-~*c... ~ ~"'s

  • SQN*INT-TOX Comp

. P /,[)s a 1(2.5 gal)

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\\ C)?&J~e-Sample Custody - Fill In From Top Down ~ tu';)T"l>b "/. .~AIC /~CT SAHiPs..e~ Relinquished By (Signature): Date/Time Received By (Signature): ~\\'\\fQ.b 1.,) ~ ~~\\"TIOt..i, -:rn..t ~~ Oat~ 1ine,w Ai'-L r.~~Wi Ii Id ~4 \\\\/~ r;~zo~/b-Jo f'/0 E ~ff If U'/,,~ Sot-1\\t. 0.:s~ Q 04.J /,(, / tJw. ( 8 'i:.' ~ l::>a..\\...JU,.-.\\ ~~ f) "-,ff / ~~\\(,. ~ o:;,.... -~ o ~l'/t:l.*°'ilJ ~ ~\\,. l\\v,../ ~ os.-to "'"' '1. 7.S E" b~ Instructions: Clients should !ill in all areas except tl}osc in the ;'Laboratory Use block. 13iomoniloring samples are preserved by storing t~ern at 6°C and shipping them in ice. The hold time for each sample is 36 hours from the time of collection. Therefore. µlease collect and ship in such a way that the laboratory will receive the samples with ample time lo initiate testing within that time frame. Samples shipped overnight on Priday via FedEx or UPS must be marked for Saturday delivery or they will not arrive until the following Monday.. /

r\\ Whole Effluent Sample Receipt Log Page_:to

  • sample temperature performed using sample Receiving Thermometer: SN 130580085 Date Time Received Received
  • samplo Project Sample Sample name and description State Comments Received Received by from Temp. (

0C) number number 05-20-16 1225 J. Sumner TVA Courier 2.0/1.0 11480 160520.01 TVA - Sequovah Nuclear Plant-101 TN 05-20-16 1225 J. Sumner TVA Courier 1.8 11480 160520.02 TVA* Sequoyah Nuclear Plant-Intake TN SOP G4 - Exhibit G4.2, revision 01-03*12

I I I I I I I I Page I of7 Chronic Whole Effluent Toxicity Test (EPA-821-R-02-013 Method 1000.0) Species: Pimeplzales promelas Client: Tennessee Vallev Authoritv Facility: Seguovah Nuclear Plant NPDES #: TN0026450 Project#: Dilution oreoaration i1Zformatio11: Dilution prep(%) 10.7 21.4 I 42.8 Effluent volume (mL) 267.5 535 1070 Diluent volume (ml) 2232.5 1965 1430 Total volume (mL) 2500 2500 2500 Test oreanism iJzformation: Organism source: In-house culture Age: < 24-hours old Spawn date: Q":>-\\1..-ll... Hatch dates and times*: OS-lie-I~ \\\\.,tie 85.6 100 2l40 2500 360 0 2500 2500 \\ll b'Si-1"'\\*l\\o. t>S-Z.<.:> Transfer vessel information: pH= \\."-\\(: s.u. Temperature= ""\\..'-\\. '= oc Average transfer volume: 0.1749 mL County: Hamilton Outfall: 101. Comments: Each concentration was UV-treated for 2 minutes to remove patho!!:eriic Interferences. Test informatio1Z: Randomizing template: ft~\\) . Incubator number and ,~ shelf location: Artemia CHM num6er: CHM882 Dryillg i11fornzatfrmfor weight detennilzation: Date /Time in oven: OS*1.'1,,*1'- *~ Initial oven temperature: '°~*c Date I Time out of oven: ()'i-'l":. *l'- \\.~"O Final oven temperatlire: I'.!\\"( Total drying time: 1.'\\-\\1.o" 11 < I DttUy feeding a11d re11ewa' information: Day Date Morning.feeding Afternoon feeding Test initiation, Sample nu.Pbers used MHSW I renewal, or batch termination used Time Analyst Time Analyst Time Analyst Outfall 101 Intake I 0 05-17-16 ~OS~o A{ I \\,,CO M \\~~~ Y\\ U.. c:,$l\\o-C\\ l\\:>C15'6.~ os-1~-11,,~ I J. IJ ' 05-18-16 ()\\QO \\~()() ',tt \\.'l..~ XI l\\.QS.11,,.()\\ 11:.Cl~t~.(ft. OS.*1~*1(,6 I 2 05-19-16, v . IJ' ~f rn\\..Jc..... J-i I.J. 00 Lt '1..~2' lloCS I~- 6 ll.. ()<::..lex... 0\\. os.-11.Ht..6 3 v u~ 05-20-16 OK\\~ V1 \\'-\\\\S, \\ 1.'-\\0 V1 l\\oo~ \\S. C>~ li...os. \\Ii. al.. os-L(.-1 li:> 4 05-21-16 C.>. ll\\,\\S }{ \\~\\ , )A l lc.OS1.o*"1. Oli.*~*llo I\\ Of I~ 11 I lioOS"'?.o.o \\ 5

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05-22-16 or.:,~ ~ \\ '-\\. ~() \\1..SO Y( \\loQS '2.0- o\\ \\lo~"2l)-CJ'l.... o~*l*H'-A 6 05-23-16 Oi'lS II 11. \\:;'\\~ -M \\~S x\\ . l\\oCl~l.0-0\\ \\ (e Cl:i. 7.,Q - 01,.. o~* IC-LbA 7 .,~ \\"2.'!> '5 ~\\ 05-24-16 Colllrol information: U\\l-~o;-.._ A.:ccp1ancc criteria Summmy uf test e11dooi1tts: % Monality:

01.

~ 20~1, 7-day LC;n > l('/'\\7 A vernge weight per initial larvae: o_ '-\\~L. NOEC 1r-o? Average weight per surviving larvae: C.'-\\f-1.... ~ 0.25mgtlarvae LOEC '>I C()I ChV '> JIY\\7. IC1s '>"1001.. Page 26 of87 "SOP AT20 - Exhibit A T20.3, revision 11-01-14

J ~,-T"8 1 'J ] 1 J 1 1 ) J J 1 1 )~....--. Page 2 of7 Species: Pimephales promelas Client: TV A I Sequoyah Nuclear Plant, Outfall 101, UV-treated Date: 05-17-16 Sun*ival and Growtlz Data Day CONTROL 10.7% 21.4% A B c D E-F G H I J K L 0 10 ' 10 lO 10 10 10 10 10 IO 10 lO 10 l f o lo 10 10 ltl lO I 'Q lO (0 co ID ro 2 l \\) to 10 f D lO lQ 10 f 0 lQ 10 to 10 3 !() 10 { t> ID I() I Q IQ ft to IQ lb 10 4 I~ IC) I(} IO f IJ ]() lb 10 10 IQ /() I() 5 It:> 10 lD IQ I{) ID IO to I{) IO II;:) 10 6 l () f b tQ I(} lt) t \\::) t t> ID I \\J f D LO re 7 to **10 ID IO 10 ID lO ID ID lb ID rD A =Pan weight (mg) Tray color code:: .~tb-TlL Analyst: Date: Qi:\\-'UO-lb llo.()b 15.1'3 t"\\.t'O 1~3 IS.Sb lb.'3b lbJ'f 15.~ l,b.-:;1 f'),qcf lb~5 \\l-1.58 B - Pan+ La/lac weight (mg) tC\\.1q. Analyst: Al ~.1t. l'\\.()3 j.).145' ;).\\.3" l}..).) 'A01 d,O.b1 ~'*"~ ~o..<., ~

l,t>.J.1 Date:

~-:-~-l~ C = Larvae weight {mg)= B-A t11-r:r- ~-<<'- Hand calculated. ~ ~ . "{:'2.\\. ~.~S s.s7.. ~ s.ss ~.'\\~ s.01 s.os 1..\\.1{'.) <..1'-\\ S.I.~ '-1.10 s.\\tr.:. Annlyst: Weight per initial number of larvae (mg) = C /Initial number oflarvac Hand calculated. ~.\\)- ~,_., zy ~ rP ~ ""~ ~ /\\.Q ~ if ~ ~ ~ ~ C? ~ ~ ~ '° Analyst: " o* o* . t>" Q" 't)' ()* ei* \\Y o* c* ~- C)' Average weight per . Per~nt reduction (k"-\\&1... II o.S~ initial number.of from control {%) - \\ S*:11~ o.~~ -n.\\oi. lanac{mg) Comment codes: c = clear, d = dead, fg =fungus, k = kiHed, m = missing, sk = sick, sm =unusually small, lg= unusually large, d&r =decanted and returned, w =wounded. Commellts: Page 27of87 SOP AT20 - Exhibit AT20.3, revision I l-01-14

Page 3 of7 Species: Pimep/1ales promelas Client: TV A I Seguoyah Nuclear Plant, Outfall 101, UV-treated Date: 05-17-16 Survival mzd G1*owth-Data Day 42.8% 85.§% 100% M N 0 p Q il s T u v w x 0 to 10 10 lO lO 10 10 lO 10 LO 10 10 I 10 10 ID. I 0 ro lD tu (0 f D 10 IC I() 2 1D ID 10 10 10 10 to 10 co LO 10 'O 3 10 ID 10 J{) '() ID ID 10 IQ 10 IQ (0 4 It:> 10 IO to IO 10 10 'O IQ re IQ ro 5 IC> l \\) Lt) to to l {) /0 tD lD IQ I (J LO 6 J\\) 10. JO. It) J\\)

  • o I()

ID IQ LO 10 ID 7 JO IQ (0 t {l ID I() l \\) LO lb lO IC IO A= Pan weight (mg) Tray color code:: M ~ ~.ni~ l5.S, fb.3\\ lb.b"t 15.fo1 i~.'fl, 1s~10 lb.40 \\b;~\\ l~.~'t 1s.31 \\'S. z.q 15/~t Analyst: Si,~ Date: Q'-4*'.t~-na B =Pan+ Larvae weight (mg) ~(>.~~* ~l.'f7 'c}.l.1lt )g.i.{° Analyst: Nb Jl3\\ Date: Oy.},,b-lle;

).0.'5' ~l;li w.~ l~*~7 ~b.J~ J'l.&7 ~~*1l C = Larvae weight (mg)= B-' A Hand cakulaccd.

s.o'\\ S.l\\a S~J\\,\\ s.1.'{ L{.~'\\' 4.SS "f.18.:ts"l.. 9~S~ "\\. l.'l. '\\.\\. 2d I{.'\\\\ ~ Analyst: Weight per initial number o[Jarvac (mg) = C / lnitinl number oflarvac. ~ b'V "v'b ~ !)-. 'O tr.. 4 "~ ~4> "bl\\/ Hand calculated. ~ V>o ~ £?. of ~ §: ..)... ~ ~ .)\\ ~ Analyst: o* ti* io~ t)" t>" o* -~. 0 ~* 1::1* \\): \\:)" A**erage weight per Percent -reduction - ct.\\ 1. s.~1.

o. \\.\\i..'-1
3. g.1.

initial number of from fontrol (%) 0- S-Z..i.o O/.\\Slc lan*ac(mg) ~ Comment codes: c =clear, d =dead,. fg =fungus, k =killed, m =missing, sk =sick. sm =unusually small, lg = unusually large, d&r = decanted and returned, w =wounded. Comments: Page 28 of87 SOP A "[40- Exhibit AT20.3, revision 11-01-14

I I I I I I I I I I Page4 of7 Species: Pimep/zales promelas Client: TVA/ Seguovah Nuclear PJant, Outfall 101. UV-treated Date: 05-17-16 Survival a11d Growtlz Data Day 100% Intake Control - Non-ta*eated y z AA BB cc DD EE* FF. -~G.. :),m 0 10 IO 10 10 I~ l() to lC l 10 lo JD IQ /\\) ID ID fl) 2 10 CQ It;, I tJ It) l () l\\) co 3 to 10 10 10 /() IQ IQ lQ 4 '~ ro tD lD ra lG lO ra IQ 5 ID lb I lb f b t () lb to l {J 6 ID } () f O lb Lb f O ID 10 7 ~ '~ \\SI-\\* "l.U. 10 tb { l) l'D iD l '{) 10 I{) A - Pan weight (mg) fll\\~U\\t(I.... ~ Tray color code:: b.1..~ l5.Cb \\5.ee> 15.c'.\\'1 l5.'\\-b 15.'3'l lL\\.qb Analyst: ~~ Date: °"'"'*2.irlb

  • c;..J fl'4*!fo-I!.

B =Pan + Larvae weight (mg) Analyst: l\\J& ~O,C10 lt\\~ 14.\\3 Jt\\.1\\8 ~\\.l'\\ dbtqs- ~\\.Ol\\ it ~14 Date: 05,~*llt, C = Larvae weight (mg)= B-A Hand calculated. ~.1& "I.lob ~.as t.l.olo $~1~ s.~s "i.loS. (..u Analyst: ~ Weight per initial* number oflarvac (mg) =CI Initial number of larvae 0 l,D. '7 "'Cb Hand calculated. ..... 'b Sf ~ ~ ~ CJ' ~ ~ "\\,g Analyst: r;;,* '\\)" t). C>" <Y Cf ~* . o* A\\'erage weight per Percent reduction 0.4n-1Y..$ 7.. o.s~o Net"" initial number of from control{%) Affu~* lan*ac(mg) Comment codes: c ='clear, d =dead, fg =fungus, k =killed, m =missing, sk =sick, sm =unusually small, lg = unusually large, d&r =decanted and returned, w = wounded. Comments: J] JJ SOP A T20- Exhibit AT20.3, revision l l-01-14 Page 29 of87

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(" 11* l!J 1o11n I) 10 ID ll,9J t-: 10 ffJ 15.86 10.1-1. I' Ill 10 16.:16 1; 10 10 l<i.H II Ill 10 15.60 IO 10 l6J7 11,4% 10 IO -15.99 I\\ Ill JO 1r... 1s f, IU HI 14,58 ~* Ill Ill ll:l7 42,8% N In 10 16.JI 0 10 II) IG.62 I' IO Ill IM7 <} 10 10 14.ol6 ij$.6')l, JI JO 10 IS.70 s 10 10 16..10 T 10 10 IG.JI u ii) 10 16.J.I l00% \\' IO 10 ll,}7 \\\\' 10 10 IS,l9 x Ill 10 lj,IJl \\' IO 10 rn.22 HIO"l. (nU1h(' 'l 10 10 ll.06 ,\\,\\ IO

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IS.68 Jiit l<I l{I .15.92 01HfMll IOI: MSD'* D111111tll's ~JSD v11l111*.: O,n705 ('.\\ISO* PMSIJ: 14,6 l!!.!nk Dunnrll4! l\\ISD vttlU!! 0,062J PMSO: ll.9 TVA I Sequoy11h Nuclenr Pinnt, Outfall 101 Ma~* 17-24, 2016 Pimcp/111/es promcl11s Chronic Whole Effluent Toxiclly Test El'A-821-lt-02-0IJ, Method 1000.0 Qunlily Co11trol Verlfici1tlon of OJttn Entry, Caleulntions, and Statlstlc11l Analyses Nol for Co11111li1tnN /\\~s:cssnh!nl, lnlt.?m:tl Laboratory QC 11~l'Jn+l.;1m1r-J.Jn1e"d)!l1ltr11Jll \\\\'clt,hl/S11r.l,lni,:

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  • "rlR,l1ltniiU nA'*R nt1l'l\\hu11r1:i:n:rC'(nr1~*

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  • l,21.

. 0.421 0.~82 11 l

  • OAil 19.0J

~.Sl 0:4gl 0.485 !1.45 5.S2 0,5l2 0,5S'1

?l.J2 l.46 O.l~6 U!i4Ct ll.21 5.85 0.585 o.m 7.1 0.585

'l:?.07 l.93 o.~!JJ 0.5?.l 20.67 5,07 M07 1),507 21.ili 5.05 0.505 0.505 21J.69 UIJ 0.470 o.m Jl,8 0.470 21.59 6.lol 0.6lol O.lilol

m.21 5,6}.

0.563 .O.M l0,6(o l:O.'l 0,509 0.509 21.*17 !i:Jr, 0.516 0 5!6 4.9 (I.SIG 21.76 l.1*1 ll,ll4 0:514 21.ll S,M 0,j64. O.S6°I JS.HS

  • l.'J!J 0.*1)9 0Al9 20.25

{SS l).olSl 0.456 l.6 OA$S 21.18 4 78 o.. 178. O,ol78 20.83 4.12 1).452 OAS2 20.87

    • 1:!1 0,4jJ 0.. 153 J0,19

. 4.82 IJ.4S2 o..i8J 19.l7 4.28 OA28 0461 6,! UA:!R 20.82

  • 1.91

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  • o.40S o..ios 19,98
  • 1.06 0.406 IJ.*!06 Minint111u S1~nll1<;ml Dill"oo:rn:c P*m:nl r.im<muni Sli:ninC0111 DilT*l'ale*

P(Ojrlf n11111b*r1 ___________ 1_1_~1JO_ Mnn1unh11l ,\\lt>lnurl"hl/ C11flncfr111nf l'rtHnfrtdudfnn(lllm I'/,) tn111111nu111htt 1111bl/11a 1Ut1'""'"*il ,~1ntrd t'/*) lan:u:(ltr~f f<Ul"ill*llo*t..,l<1r10"*ffl l'l*I rno.o MMO M Nol UJIJllitnblr 100.U 0.4~l 11.2 Nol np1dic111ik 100.u II.SSH 7.1

  • 15.7 100.11 O,SJft f 1.8

-JI.* 100.0 0,526 '4,9 .!J.I lllU,O (1;~56 J,6 $.~ 100.0 U.4M 6.1 3.ll

!Oii.ii 11.412 8,J 14.S PMSD 1umwurta(l'5lpre<iiio<I '[110 l'MSD " ill< mlnm1u1u PCl"""l dill"cr<tl<< b"ll'c'<m 11l.i ***lfOI""" ""'""I 11111 CIUI b* dHl.ln:d.m1i11ico!ly 6i!llliRCILOf In. 1'11010 dllu

    ICU)' l<JL La11ct rMSD boWld dc1orn1incol by USCM ( I01h porccnliloJ = 12!\\ Upper rMSD bolUld ~<lcm1in*d by USEM (~Olh por"nhl*) "JO% lo1.wr and upparPMSD bound'- ~\\'C'fO 1k1q1mmcd from lhll l01l1 Md 91lth rmccntila. r~spucuwly. or PMSD d;n;i llcttu Ilt'N:i WITT ln1~1fabor~1ory V:1rmhiliJY SHIU)* (LJSEl1A, 2001.1; USt!PA, lf'lO lbJ USEl'A lOlllo, lOOI~ l'in*l l\\cpofl lnl"labaratO<)' Vanobillly S1udyoffl'ASho~-1~m1 Cluoni~ ;in~ /\\Ciiio Wllol< Emu,.,,1Toklt1ty r.. 1 MoihodJ, Volume$ I M~l-AppMdi< EPA*821*D.Ol*oo.I :urd EPA*82l*D-lll*UUS US linv11on1111:111~I Prorccunn As*'nt)', ("1n<tnn.i11. 011 "\\ En"'runmmsa\\TatTnp SaluJh:ll,,,:, bu:.. Start Date: 511712016 TVA I Sequoyah Nuclear Plant, Outfall 101 May 17-24) 2016 Statistical Analyses l..ruv"I Fish Growth and Survival Test-7 oay Growth Test ID: PpFRCR Sample lD: TVA I SOn Outfall 101 End Date: 5124/2016 lab ID: ETS-Envir_ Testing SoL Sample Type: DMR-Oisct>arse Monitoring Repon Sample Date: May2016 Protocol: FWCHR-EPA-B21-R"02*013 Test Species: PP-Pimephales promelas Comments: Ccnc-0/o 1 2 3 4 Control-NON 0.5730 0.5550 0.5650 0.6280 Control-UV 0.4700 0.42!0 0-485{J 0.sS20 10.7 0.5460 0.5850 0.5930 0.5070 21.4 0.5050 0.4700 0.61.40 0.5630 42.8 0.5090 0.5160 0.5140 0.5640 85.6 0.4390 0.455{) 0.4780 0-4520 100 0.4530 0.4820 0-4280 0.4910 lnt3ke 0.3780 0.4600 0.4050 0.4060 Transform: Untransformed 1-Tailed Isotonic Conc-o/a Mean N-Me:;in Mean Min Max CV% N t-Stat Critical MSD Mean Control-NON 0.5803 1.2038 0:5803 0.5550 0.6280 5J5'31 4 Control-W 0.4820 1.0000 0-4820 0.4210 0.5520 11.220 4 0.5259 10.7 0.5578 1.1572 0.5578 0.5070 0.5930 7.096 4 -2.589 2.410 0.0705 0.5259 21.4 0.5380 ,_, 162 0.5380 0.4700 0.5140 11.811 4 -1.914 2.410 0.0705 0.5259 42-8 0.5258 1.0908 il.5258 0.5090 0.5640 4.882 4 495 2.410 0.0705 0.5258 85.6 0.-4560 0.9461 0-4560 0.4390 0.4780 3.559 4 0.889 2.410 0.0705 0.4598 100 0-4635 0.9616 0.4635 {).4280 0.4910 5.189 4 0.632 2.410 0.0705 0.4596 Intake 0.4123 0.8553 0.4123 0.3780 0.4600 8.338 4 Auxitia!)I: Tests Statistic Critical Skew Shapiro-Will<'s Testindicates normal distribution (p > 0.05) 0.95958 0.916 0.1797 Bartlett's Tes! indicates equal variances (p = 0.31) 5.99112 15.0863 The control means are*signifrcanll:t dilferent{e = 0.02) 3.i0995 2.44691 H~othcsis Tost !1-tail. O.DS) NOEC LOEC ChV TU
    • MSDu MSDe MSB MSE F-Prob Dunnell's Test
    ~00 >100 0.07052 0.1463 0.0071F. 0.00171 0.01072 Treatments vs Control-UV Line..r Interpolation (200 Resamples) Point SO 95% CL(Exp) Skew 59.744 9.339 18:409 78.003 -1.2144 75.797 ICOS IC10 IC15 IC20 IC25 IC40 IC50 >'lOO 1.0.,..------------~ -"oOO >100 .. 100 >100 0.9 0.8 0.7 0.6
    0.5
    ~ O.~ ~ 0.3
    . 02 0.1 0.0 O-.c>-~--c.---
    -0. 1... _ -0.2 -0.3 +-.,.....,~~-.--r-~~~~-~...-i 0 OoSQ-R<U!iponse Plot 0.7..-----------------------. 0.6 0.5 ~ ~ OA ~03 0 0.2 01 O+---....----.----.------~----.----l Page 31 of87 i5 ~ ~ 0 0 0 0 so Dose 0/a 1-tail, 0.05 tevel of significance 100 150 N-Mean 1.0000 1.0000 1.0000 0.9997 0.8742 0.8742 Kurt -0.0457 df
    5. 18'
    \\ Envlrnnroenbl Testing Solution.s1 lri<:~ Start Date: 5/17/2016 TVA I Sequoyah Nuclear Plant, Outfall 101 - Intake May 17-24, 2016 Statistical Analyses Larval Fish Growth and 5.urvival Test~7 Day Growth Test ID: PpFRCR Sample ID: Tl/A I SQn Outfall 101 - Intake End Date: 5/24/2016 Lab lD: ETS-Envir. Testing Sol. Sample Type: DMR-Discharge Monitoring Report Sample Date: May 2016 Protocol: FWCHR-EPA-821-R-02-013 Test Species: PP-Pimephales promelas Comments: Cone-% 1 2 3 4 Control-NON 0.5730 0.5550 0.5650 0.6280 Control-UV 0.4700 0.4210 0.4650 0.5520 10.7 0.5460 0.5850 0.5930 0.5070 21.4 0.5050 0.4700 0.6140 0.5630 42.8 0.5090 0.5160 0.5140 0.5640 85.6 0.4390 {).4550 0.4780 0.4520 100 0.4530 0.4820 0.4280 0.4910 Intake 0.3780 0.4600 0.4050 0.4060 Transform: Untransformed Cone-% Mean N-Mean Mean Min Max Control-NON 0.5803 '1.2038 0.5803 0.5550 0.6280 Control-UV 0.4820 1.0000 0.4820 0.4210 0.5520 10.7 0.5578 1.1572 0.5578 o:so10 0.5930 21.4. 0.5380 1.1162 0.5380 0-4700 0.6140 42.8 0.5258 1.0908 0.5258 0.5090 o.ss40 85.6 0.4560 0.94!31 0.4560 0.4390 0.4780 100 0.4635 0.9616 0.4635 0.4280 0.4910
    • intake 0.4123 0.8553 0.4123 0.3780 0.4600 Auxiliary Tests Shapiro-Wilk's Test indicates normal distribution (p > 0.05}
    F-Test indicates equal variances (p = 0.48) The control means are significantly different (p = *o.02) Hypothesis Test (1-tail, 0.05) Homoscedastic t Test indicates significant differences Treatments vs Control-UV CV% 5.631 11.220 7.096 11.811. 4.882 3_559 6.189 8.338 1-Ti;liled N t-Stat Critic;i.I MSD 4 4 4 4 4 4 4 4 2.177 1.943 0.0623 Statistic Critical Skew Kurt 0:94504 0.818 OA7058 0.02157 2.47521 47.4683 3.10995 2.44691 MSDu MSDp MSB MSE F-Prob df 0.06226 0.12917 0.00973 0.00205 0.07236 1, 6 Dose-Response Plot 0.7 0.6 0.5 ~ 0 0.4 Cl ~0.3 c.... 0.2 0.1 0 z 0 z
    g c: c u
    Page 32 of87 '=? d g c 0 f.J c> <'.i.,. CXl 0 0 1-tail, 0.05 level of significance l l l l l l J .1 _J J J j J Page 5 of7 Species: Pfmeplza/es promelns Date: 05-17-16 Client: TV A I Seguoyab Nuclear Plant, Outfall 101. UV-treated Dail CltemiSt. r: Concentration CONTROL UV-treated 10.7% 21.4% 42.8% 85.6% 100% 100% Intake Analyst Paramt:fer ff{S.U.) DQ(mgtL) Conduc1ivity ( hos/cm) "'Alita linity (moCaCO,;/L)
    • Ha.rdncss (m° CaCOi/L}
    • Tem erature (0C).
    Conductivity (µmlios/cm)
    • Alk.-ilinily (mgCaCOYl.)
    • Hardness
    . (ma CaCOj/L)
    • TR' citlorim: (nig!L).
    • Te~perature ee>
    H{S;U.l DO (m!rlLl Cnncluctivity {µmhos/cm)
    • Alkalinity (maCaCO,;/L)
    • Hardness (nio CaCO:;/L}
    • TR. chlorine (mg!L}
    "Tern er.iture (°C) Day .(Analysl identified forcacli.day, erformed H. D.O. llnd conductivity measurements only.) 0 1 . 2 1fiina1. lnitfal Final
    • Temperatures perfom1ed a1 lhc time of test initiation, renewal oncm1ination by the analyst identified in tlic Daily Renewal Information table located on Page I.
    iinicy, hardness and total residual chlorine performed by the analyst identified on the bench sheet specific for each analysis and transcribed to this bench sheet -A-~* Tola! residual chlorine was pcrfom1cd*on non-treated Outfall l 01 and lntakc samples. Page 33 of87 SOP AT20-ExbibitAT20.3, revision l l-01-14 l l l l l J Concen-tration CONTROL UV-treated 10.7% 21.4% 42.8% 85.6% 100% 100% lnf:1ke Page6 of7 Species: Pimep/utles promelas Client: TVA I Se uovah Nuclear Plant Outfall 101. UV,.;treated Date: 05-17-16 Analyst Parameter H {S;U.) DO(n o L) Conductivity (µmhoslcm) "'Alka!foity (m° CaCO;/L) "Hardness (ml! CaC03fL) Conductil'ity (µmllos/cm)
    • Alkalinity (mgCaCO:;/L)
    "llartlncss (mg CaCO,;IL)
    • TR chlorine (mg/L)
    Conducti\\'ity {1unhoslcm)
    • Alkalinity
    {ml!. CaCO;/L) "H:mlntss (mg CaC03/L) "'TR chlorine {mg.IL)
    • Temperature (°C)
    Day {Analysl identified for each day. pcrfom1cd pH. D.0. and conductivity measurements only.) Initial Final Initial Initial Final Initial Final .--.,-,,<nneraturcs perfoni1ed al the lime oftest initiation, renewal or termination by the analyst identified in ti~ Daily Renewal lnfonnation table located on P:i!!.c I. '":."Zl1;iilit "ty. hardness and to!al residual c!Jlorine pcrfom1ed by !be analyst identified on the bench sheet specific for each analysis and 1.r.mscribc:d to this bench sheet """ b:r-****' . Total residual chlorine was pcrfom1cd on non-treated Outfall IO I and Intake samples. SOP AT20-ExhibitAT20.3,revision ll-01-14 l l l l ~l l .1 J J J Page7 of7 Species: Pimephales promelas Client: TVA I Sequoyah Nuclear Plant, Outfall 101; UV~treated Date: 05-17-16 An'alyst Concentration
    far.ameter
    'HCS.U.). Control Non-treated DO (mg/L)
    • .* C<induttMty (µmhos/cn:i)
    Concen-tration Control Non-treated
    • Alkalinity (mg CaCO;;/L)
    • Hardness
    . {mg CaCO,;IL}
    • Temperature (°C)
    Parameter DO(mg!L) Conducthitr (µmhos/cm)
    • Alkalinity (mgCaCO.;/L)
    • Hardness (mg CaCOJIL)
    Analy~t
    • Temperature {°C)
    In.itial Day (Analyst identified for each day, perfom1ed pH, D.O. and conductivi measurements only.) 0 1 2 Final Day (AnalystidentifiedJo;. cach-day,.perfofll)Cd pH,* D.O.. and conductivity measurements only.)
    3.
    4 5 6 Final
    • Temperatures performed at the.time oftest initiation, renewal or termination by ihe analyst identified in the Daily Renewal Information 1able located on Page I.
    Alkalinity, hardness and total residual chlorine,perfom1ed by the ana!:1*st identified on the bench sheet specific for each analysis and transcribed to this bench sheet by:*_ Page 35 of87 SOP A T20- Exhibit AT20.3, revision 11-01-14 I ~ Envlronmenta1Tosllng50Jullon1, Inc, Conccnlrullon l'nrnm~ter
    • lnll (SU) llOlml!ll.l
    Conrrol,
    • ** Cond11c1M1v Cumbosfcml Non*trente~
    Alknliuily <mwt. caco;i llnrdncs~ {mg/L CnCOJI Temucrntnrc !"Cl 1111 !SUI \\ OOC111!!1Ll Contr<1I,. ConductMtv h1mhos/cm) uv.1re11tetl AlkRlihlly (mglL CnCOJ) llurdncss (mR/L C11CO,) i*fnmernture !"Cl 11111 fSlJl I0.7% DO<m,,/L\\ Conduetil'lty (Jimhilslenil Tcmuernture.("CI nil !SUl 21.~% 00{1111!/Ll ComiudMlv Cumllosleml 'l'cn111eri1tur~ l"Cl nil CSU! -12.81Vr1 DO linl!/i.l Con1luc1M1v <umllos/cml TcmJl~rnlurc (Cl
    • 11111 ISUl 8S.6'V*
    DOCm!!ILI Couduclivitv lumhos/cml Temnet'llturc !"Cl nll CSU\\ 00 (m11ILI ConlludMtv lumhos/cml 1011*y,, Alknllnity hnR/I. CnCO,J llnrdnm (mg(L Caco,i*
    • Totnl n~sldu11I Ch1otlne lmrill.
    'rcmmcruturc 1°CI 11111 ISUI DOln111/L\\ ConductMlv <umlm!fcnil IUO':f., lllluhe Alknlinlly (mg/!, CnCOj) ll11nh1~* (mR(I. CaCOJI
    • 'J'otlll ~esidual Chlorine lnu!lL
    '1'~11111cr111u1*c r"Cl TVA I Sequoyah Nuclear Plant, Outfall 101, UV-treated May 17-24, 2016 Dnv O lnllflil . -7.31 7.8
      • 318 61 88 24.7
    • - 7.44 1;s 321 -
    61 88. 24;3 7.31 7.8 30.7 *.: 24~8. . 7,31 1;9 290
    ?4~8
    .7.29 7;9 .2M. 24.8 . 7.'28 7.9 202 .. 24.9 1.28 VI 186 60 .. 72 <0.10 lS.11 7.:!S 7,8 1911 64 68 <O.IO 2S.O Pimep//t1le,y pmme/(IS Chronic Whole Effluent Toxicity Test EPA-821-R-02-0JJ, Method 1000.0 Daily Chemical Analyses Dnv l Dnv 2 Dnv3 Duv 4 Finni lnlllal Fina I lnillRI lllnnl I nil in I l?lnal lnlllul 1.46
    • '***7.39
    -7.1:2
    7_30 7.24
    ., 7,61 1.01
        • 7.50 7.9 7.8 7,8 7,8 7.8 7.8 7.8 7.8
    -313
    • 307 310 322 62 61 88 86 2*1.4 24.8 24.()
    24.7 24.5 24.7 24.6 24.8 . 7.63
    • 1.64 7;01
    '7.22 7.24 ., 7.60 * '6.97
    • 1.2s 7.8 7,9 7.8 7.8 7.8 7;8 7.8 7.8
    • 319.
    J(J3 297 297 .* -~ 63
    • 6:L 88 88 24.:?
    24.8 24.6 24.8 24,G 24:7 24-4 24.7, 7.58
    • 1.6S 1.03 7.23 7.:24 7.6l
    . :6.95 7/J.S 7,8 7.9 7,8 7.8 1;a 7.8 1;8 7,g 307 292 290' 287 24.5 24.9 24.7 24.8 24.3 24.7. 24.S 24.8 7.61
    • 1:65 Ml
    .. 7;23 7.25 . 7.59. .6.99 7.25. 7.9 7.9 7.8 7.9 .1.8. 7.8 7.9. 7.8 288 *:* 280 280.
    m 24.5 24.9 24.7 24.ll 24.3 74.7 24.7
    ?4,8 7;S6.
    7.64
    • 7.03..
    7;:ij 726 7.59 6,95 .7.l4 7.9 '.7.9 m 7.9 7.S 1.9 - M .,;g 2Stl 2SS **.*,** '.!S2....... 2SI '. 24.S . 24.!l 24.. 7 24;8
    2'1.5 JO 2li,.:7
    -24.8 7.S.2
      • 7.64
    -6,96 7.22 7.18
    • 7.60
    . 6.90 . 7.23 7,9 '.8,0 1;s 8.0 7.8 7.9 t9 7.8 206. 205 201 203 24:6 24.9 24.S 24.8 24.7 24.8 24.4 24.8 7.53 7;63 7.06 7.20 1.30 7,$9 6.9.8 7.23 8.0 s,o 7;8 8:0 7.9 7,9 7,9 1.9 184. 186 184 183. 64 62 . 68 72 ...;;O.IO <.ll;IO 24.6 2.4.9 24,S 24.8 .24.7
    i4.8 24.4 24.8 7.63 7.66 7.06 1.18 7.38 7.62 6.97 7.23 7.9 8.0 7.8 8.0 7.9 7.9 7.9 1.9 196 197 199 196
    .64 68 72 80 <0.10 <0.10 34.3 24.8 2*1.6 25.tl 24.S 24.7 24.8 24.7 Nole. I olnl residual chlorrnc wos 11crfom1~d (Ill ll01Mrnot~d Oullnll I 0 I and hrlukc samples. 1:1nul ,7.48 7.7 24.S 7.36 7.8 24.4 7.JS 7.8 24.6 7.34 7.8
    i4.3 7.28 7,9 24.l 7.28 s;o 24.7 7.31 8.0 24.4 1.30 8.1 24.4 Project nuhlbcr: ______
    1_14_8_0 l)ay 5 l11ltlnl 7.61 7.7 320 24.7 7.63 7.7 304 24.7 7.62 7.7 29*1 24.7 7.62. 7.8 279.., 34.7 7,61 7.9 256. -* 24.7 7.61 1.9 207.. 24,7 1.60 7.8 191 24.8 7.611 7..9
    zoo*,
    24,8 Dnv6 Fiunl lnlllnl 1:1nal 7,00 7.6S 7.07 '1.7 7.7 7.8 299 24.S 2<1.5 24,J 7.03 7.40 7.34 8,0 7;8 7.8 30S 24.4 24.8 24,6 7.04 7:39 7.32 7.9 7.8 7.9 295 24.6 24.9 24.4 7.03 7,38 7,32 7,9 7.9 .7JI
    ?86 24.6 24.9 24.4 7.00 7:-35 7.32 7.8 8.0 7.9 2S7' 2.\\.6 24.9 24.4 1.00 7.34 7.32 7.9 8.0 7.!l
    ?Oil 24.3 24.9 24.6 7.07 7,3'.I 7.33 7.7 7:9 7:9
    .\\92. 24.6 24.9 24.:2 7.11 7.33 7.31 7.9 8.0 1.9 205 14,5 24.9 24.6 File: sqn101_051716chem.xlsx Entered by: J. S~er Reviewed by: l l _J . l _ ] _ J ~ fT < 'l":~j!:J ~. Page I of7 Chronic Whole Effluent Toxicity Test (EPA-821-R-02-013 Method 1002.0) Species: Ce1*iodaplmia dubia Client: Tennessee Valley Authoritv Facility: Seguovab Nuclear Plant NPDES #: TN0026450 Project#: \\ \\l.\\~O Di/11tio11 pref}(lrat/011 informatio11: Dilution prep (%) !0.7 21.4 Effluent volume (mL) 2675 }35 Diluent volume (mL) 2232.5 1965 42_8. 1070 1430 Total voli.lme (inL} 2500 2~00 2500 Test Orf{anis_m source inftJri11ati.<m: 85.6 2140 360 2500 Organism age: < 24"hours old Date and limes organisms were. born . ~~l\\*\\\\o ()~?Jo,,, between: Cullure board: 0S* 1ll*\\\\..A Replicate number. I I 2 I 3 I 4 I s I 6 I 7 I s I JOO 2500 0 2500 Q~\\S !) I 10 Culture board. cup number: "1 I \\\\ I\\~ I l"'l 11.1. l'"i.I.\\ fl""\\ 1'1."\\ I~ 13\\ Transfer vessel information; I pH= "1..sc..s.t:L Temperature=,_.. \\.&'~C ' Average transrer,volumc (tiiL): I o.Of:HnlL Dnily re11ewal information: Day Date
    • Test initiation and feeding, MHSW County: Hamilton Outfall: 101 Commell/S:.
    .. Test 11Zformatio11: . Randomizinincmplate color: Incubator number and shelf locatioit: YWTbatch:
    • Selenastn1m batch:
    Sample numbers used renewal,and, f eedin,g, or batch used Outfall 101 Intake termination time 0 05-17-16 OS..18-16 2 05-19-16 3 05-20-16 4 05-21-16 5 05-22-16 6 05-23-16 7 05-24-16 O~.P L.6\\ 05tiCl6 Q'w\\*11-\\\\o Analyst Control infon11atio11: Summary of test endpoints: Control-I Control-2 Acccp!am:c criteria %,of Male Adults:
    61.
    07.
    S:20'}1;,
    7-day LCso '/ HD1 % Adults having 3*d Broods: ' I t:bl. 1007. . ~SO% NOEC IM1 * % Mortality: D1-D1. $20% LOEC > Jf'L\\t Mean Offspring/Female: t.(\\.O* l..°i*~ <!: I :5.0 offspring/female ChV "> /(}f:\\ 1. %CV: s.t17. Co. I.\\ 7. <40.0% IC2s
    > 1001.
    Page 37 of87 SOP ATI I - Exhibit A Tl 1.2, revision 11-01-14 I l l l l l l __I .I _J J
    _ f{f.. '1 iq;;-~ I~
    Page 2 of7 Species: Ceriodaplmia dubia Client: TVA I Sequovah Nuclear Plant. Outfall 101 Date: 05-17-16 CONTROL-1
    • Survil)a/ a11d Reprodli.ction Data Repiicate number Day I
    2 3 4 5 6 7 .8 9 10 l Young produced 0 D a 0 0 0 0 u q 0 Adult mortalit)' \\...._ L. L. \\......_ L '-=- L 2 Young produced 0 b D Ci 0 ('") ~ ri 0 ('J Adult mor!ality
    • ~
    \\,__ '- \\.._ '- \\__ \\...._ \\.._ \\___ '- 3 Young proclueed 0 0 0
    • o
    .f°'.* (") 0,
    a.
    0 D Adult mortality L L ~ '- L \\.... \\... 4 Young producecl '-\\
    • ~
    ~ ""\\ \\;..l '4" ~* '-\\ '5 '-\\ Adult mortality \\ \\_ '--- \\.,,... \\.....,-_ (_ '- L 5 \\'oung producccl \\:::, \\~ \\1:... lO '\\\\ \\\\ n \\.,_: \\'1-. co Adu!~ *mortality \\._ \\_ \\..._ \\.._. L.. \\.._ L \\-..-- L L G Youn~ produced ' 0 0
    • O 0
    D .6 M b 0 0 Adult mortalit)' \\_ \\_ \\..,._ L L "\\.._ "\\.,,_ 7 Young produced \\\\o "~ \\~ .\\~ \\""L. \\~ \\'"b \\'"1...:.. \\£._ \\:S Total young pro~uccd, i..i ?_-=\\ '?,)"°!) "'2..-"'\\ ~~ '2..C\\ "l. ".'\\ -z... ""\\ ""l..i 1..'\\ Final Adult Mortality \\.._ \\......_ \\;..;..._
    • ,L-
    \\.._ \\....__ X for 3rd Broods. -'-/"_ ~- '::)<::_ I "')<:... )<:_ ")C._ ?<.'...,_ h'ou:* Adult moru>lny (!; = hvo; D = dc:d), SB: spfil br"!Jd (sins!c broo!l spill botwc:cn two days). CO - c:uzy over (olr<pnns c;uncd o)'c:r\\\\ith adult clu;ing lrilnsfcr). C01ice11tratioll: % Mortality: r D1 Meaii.OffsprmgtFemale: I -,~.o CONC: 10.7% Survival aJZd Reproduction Data* Rcplieatc number Day l i 3 4 5 G 7 8 9 10 1 )'oun*~ produc:ctl (\\ 0 0 0 0 6 0 0 ' 0 (") Adult mortality \\ L \\.._ L
    • L*
    L L: '- L 2 Young produced ("\\ () {), () 0 0 0
    • a*,
    f) 0 Adult mortality \\ L \\.._:.. \\_ L L L L \\...._ L 3 Young produced
    • n 0
    ("i 0 0 f"I 0 0 0 .()
    • Adult mortalit)'
    • L '-
    L L L \\._ \\........ \\..... \\......:.._ 4 Young produced I-\\ L\\
    s.
    Lt
    • ~
    ~ ~
    • u;
    \\..\\ s AdulJ niorr.Jli.ty \\.._ L \\.._ L. L.. L "\\.... 5 Young pro~uccd \\ '"L. \\~ \\~ 10 \\'.:>' "- n.... \\ "L. l\\ \\L.... Adu If mortality
    L-L-
    \\......... \\....._ L \\...._ \\........_ L G Young produced C1 {') 0 u 0 0 0 a 0 G Adult mortalit)* L L L L L..... ~ \\. \\...__ L \\..:__ 7 Young produced \\ !::. \\'Si \\ '- \\$ - t5 \\~ \\ '-\\ \\'"-\\ lS Totnl young produced. 'l..C\\ ~..,_ ~'-\\ 2..9. ~a ~\\ -i.. '\\ ~t°) L.'1 ~'- Final Adult Mortality
    x.
    'L ~ )<.._ x x.. X- 'L y: y Note: Adult rr.ort:iility IL - lh*c. D - dcJ.d), SB= split brood (singl~ br~d Splitbctm:cn m:O do;}~}. *co-= am* O.?r (offscuin~ c:urlCd D\\'Cr with ;,duS: du.ijr-'! tr:rnsrcr). Co11ce1lfratio11: % Mortality:
    07.
    Mean Offspring/Female: ~(I~ % Reduction from Control-I: -'-l.S7. Page 38 of87 SOP AT 1 l - EXhibit ATI 1.2, revision 11-01-14 l 1 l l 1 . I l . I _] l _J J J l J J o rP m,:;g t5FJ
    . L
    ~l
    • ~.::~--;
    Species: Ceriodaolmia duhia Client: TVA J Sequoyah Nudear Plant, Outfall l 01 Page3 of7 Date: 05-17-16 CONC: 21.4 o/o Survival and Reproduction Data Renlicnte *number Day . l
    z 3
    4 s G 7 8 9 10 1 Young produced r"\\. h l'\\. a b () 0 0 0 () Adult 111orrality L L \\....- \\._ \\..._ \\._ 2 Young produced f'\\ n 0 D 0 0 0 . ("\\ () 0 Adult morfality "L-* \\._ L ~ '-- \\....__ L 3 Young produced 0 0 0 0 a 0 a 0 0 0 ,i\\dult mortality \\..... \\.;.... \\..._ ~ '-- \\..... "\\....__ 4 Young produced ""-\\. ~ '-.\\ '-\\ '-\\. '-\\ ~ cs. s Adult ~ortalily * '\\.....,- \\.._ '-
    • l..._
    L. 'L "--- '\\.._ \\....__ 5 Young produced "'-. \\\\ \\"'1-l"\\ rt.. 1.0 \\Q \\ '1- \\ 1-11... Adu!~ mortality ~- '- \\._ \\._ 6 Young pr0duced C) 0 u u 0 0 0 0 0 n Adult mortalify L.. '- \\....__ \\..._ \\...... L 7 Young produced \\~ \\~ \\CS
    • .\\\\
    \\ "-\\ \\\\o \\~ \\\\o \\'Sa \\~ Tot:il young produced ~\\ ~ ~\\ ~s. .,3,C) "l..C\\ "l. ""\\ ~"L ~L...,3,Q Final Adult Mortality L \\..... \\_; L ~ ovct o ~onn'- QttJ CVl:r\\Vl:I :l ti anm:&r.lm er. Nate Adult m6rtafilY (L"' lr.'e. 0 ~ dead), SB - spl11 brood {sms!e brood split bOl\\"""1\\ two do.y*}, CO ~ Cl<l'/ f !IS h d ltd r.) Co11ce11tratiu11: % Mortality: C\\1. Mean Offspring/Female: '30.I % Reduction from* Contra I-J : -S.1:\\7. CONC! 42.8% S11rvi11al.and Rqirod11cti01z Data ~.. -.*:. Renlicatc number Day i
    z
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    • o 0
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    • \\...._
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    01.
    Mean Offspring/Female: 3-i. '2.. o/o Reduction from Control-I: -t\\.07. Page 39 of87 I SOP ATl l - Exhibit AT! l.2, revision I 1-01-14' l l l l _ J I J ~ tj~ 14'.?dl £'!!!_ _::. 1 .) ~~lr'CllMJ7:;"0Sclul~bc. Page 4 of7 Species: Ceriotlaplmia <luhia Client: TVA/ Sequovah Nuclear Plant, Outfall 101 Date: 05-17-16 CONC: 85.6% S1i1"Vival mid li.eprodi.1ctio11 Data Day I Young pl'.oducetl Adult mortality 2 Young produced Adult mol'.tality
    • 3
    , Young pl'.oduced Adult mortality 4 , Young produced Adult*mol'.tality 5 Young produced Adult mortality G Young produced Adult mortality 7 Young pl'.Oduced Total young produced Final Adult Mortalil)* - l 2 o a \\ \\ "1-L \\.R '\\ L 0 \\._ 3 a \\_ 0 L \\\\.o . Rer>licate'number. 4 5 G 7 a o o-* -o L.. ~ \\..._ \\__ .() o D n \\.._ \\_ \\._ \\_ D n 0 .[') \\..___ \\.__. 0 L \\ s' 0 L \\-<\\. \\ "':l,. \\"'5, \\-:::, '-a "- \\'.\\ 8 0 L.. 0 '- '--\\. \\ e_: 9 IO 0 \\0 \\\\ "'?:>\\ ,Var<: Adult.mori*fi1y (L; li"C, O; dcod).. SB-0 split bro!)d(sin£lc brood lJllil botwoon two clays), CO 0 crrv ov<r.(ii!TSalinc corricd ovcr\\vith >dilli dUrioJ: uansf<r).
    • Cmici!irttntiou:
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    Mean Offspring/Female: 3Y.1 % Reduction from Control-I: -t'I. "17. Page40of87 SOP ATI l -Exhibit ATl 1.2, revision I I-01-14 v l l l l l J J i J l I j ~ PtF lE!~21 fPJ
      • .~:~.-.
    Species: Ceriotlaph11ia tlubia 1 Client: TV A I Sequoyah Nuclear Plant. Outfall 101 CONTROL-2 Sun*ival mu! Reproduction Data Replicate number Day 1 2 3 4 5 6 7 8 1 Young.pr9duccd
    n.
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    • Total young produced
    'l.., £.(.. "1& I,;~ ~\\ ~ ?l\\ 2'1 Final Adnlt Mortalitv "\\;_. ~ '-- ~ '- \\.._ '- \\._ X for 3rd Broods .'L:_ ~ **x.. 'L: ~ "'- ~ ')<:. Page 5 of7 Date: 05-17-16 9 10 0 0 n 0 \\_ \\._ 0 0 L 45 '\\ L \\b \\~ \\..._ (\\ 0 \\.._ \\. \\'5 ~~ :,-'L L \\._ '}<'-.. ~ Nau: 1\\dull mo1101Tity (L.::: live. D ":'cli::ad). SB c s,pfitbrood (smstebrood s;iJ:t bctwcen \\\\VO d;,,ys). CO= ~ny ovcr(clTspnn.s c.:i:mcd over w11h :idult dunns lr3nsfcr}. Co1Zce11tratio11: % Mortality: I 01. Mean Offspring/Female: I 21-~ CONC: 100% Intake Surviv.al alld Reprod11ctio1Z 1Jata Renlicatc number Day 1
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    . "38 1 ll 0 ,142 l9J Tnlnl (I 0 ll 43 118 0 ISi Jl2 k::.~ 'V"~t r I Environmental Testing Solutions, Inc. Conccnfrn lion (%) I 2 3 Confrol-t 33 29 30 10.7% 29 31 34 21A% JI )ll 31 42.8% 32 34 32 85.fi'V.1 34 33 34 IUO% 34 JS 36 CorlCrul - 2 27 26 28 100% 11111111~ 34 35 31 OutfnU IOI: llunnctt's MSU l'llluc: 1.908 l'MSD: 6.6 ~ llu1111c1t's MSU 1*irluc: 1.611 PMSD: 5.5 TVA I Sequoyah Nuclear Plant, Outfall 101 May 17-24, 2016 Chronic Whole Effluent Toxicity Test (EPA-821-R-02-013, Method 1002.0) Cel'iod"plmia dttbill Chronic Whole Effluent Toxicity Test EPA-821-R-02R013, Method 1002.0 Quality Control Verification of Data Entry, Calculations, and Statistical Analyses 4 29 29 35 32 32 33 29 28 MSD= l'MSD'" Project numbcr: __________ 1_1_4_80_ Replicnk number Sun*h*ul " 1\\\\*cr*ngc reproduction Cndrkic111 of PcrC4:11l rcdnrliUn from (%) ( offspringll'crnalc) \\'uriollon ("/.) 11r.1olrd contruls (%) 5 6 7 8 ? 10 27 19 '11 28 19 29 llJIJ 29,0 5.9 Not llf>l'licnblc 28 31 29 JO 29 32 JOO J(l.J 6.2 -4.5 30 29 27 32 32 30 1110 30.7 6.9 -5.9 33 33 29 30 32 35 1011 32.:? 5.4 -11.0 36 31 35 32 29 31 1110 32.7 6.5
    • 12.8 37 35 34 37 33 33 IOO J4.7 4.5
    -19.7 31 30 31 29 30 J2 IOO 29.J 6.4 Not 11p11licablc 31 29 30 29 32 32 100 31.Z 7.2 -6.5 Minimum Signilicont Dilfonmcc Pcn:cnt Minimum Sig11ilican1 Difference PMSD is 11 mcusurc oftest precision. The PMSD is the minimum percent difference between the comrol and treatment that cun be declared stnllstically signincunt 111 u whole cfllucnl to~icity test. Lower PMSD bound dctermmcd by USEPA ( l01h pcrccntllc) "" 13%. Upper PMSD bound dctcnninad by US EPA (90'" percentile)= 47%. Lower 1md upper PMSD bounds were determined Imm the I Oln nnd 90lh pcrtcntilc, respectively, of PMSD data from EPA's WE.T lnlcrlabomtory V11rinbil!ty Study (USEPA, 2001a; USEPA. 2001b). l lSEPA. 20l! Io. :wo I h. Finni llopm1' lntcrlaborJtory Varinbilily Study oJ"P.PA Shon-tcnn Chrome nnd Acute Whole F.ITiucnl Toxicity Tc~t Method~. Volun1~s t and 2*Appcmk". 1.iPA-821-B-O 1-004 and El'A*B2 l-D-O f *005. US Enviro111n~11tal Prolccllon Agency, C111c111nul1, Of I. G
    • Start Date:
    TVA I Sequoyah Nuclear Plant, Outfall 101 May 17-24, 2016 Statistical Analyses Ceriodaphni;t: Survival and Reproduction Tcst-Rapro*ductiori: Test 10: Cd.FRCR Sample ID~ 1VA rSQN Outfall 101 End Date: 511712016 512412016 Lab ID: ETS-En~ir. Testing Sol. Sample Type: DMR-Discharge Monitoring Report Sample Date: May 2016 Commenls: Conc-o/a Control-I Control-2 10.7 21.4 42.8 85.6 100 Intake 33.000 27.000 29.001) 31.000 32.000 34.000 34.000 34.000 2 29.000 26.000 32.000 30.000 34.000 33.000 35.000 35.000 Protocol: FWCHR-E?A-821-R-02-013 Test Species: CD-CeriC>daphnia dubia 3 4 5 G 7 8 9 10 30.000 29.000 27.000 29.000 27.000 28.0.00 29.000 29:000 28.000 29.000 31.000 30.000 31.. 000 29.000 30.000 32.000 34.000 29.000 28.000 31.000 29.000 30.000 29.000 32.000 31.000 as.ooo 30.000 29.000 27.000 32.000 32.000
    m,ooo 32.000 32.000 33.000 3:;.000 29.000 30.000 32.000 35.000 34.000 32.000 36.000 3i.. ooo 35.000 32.000 29.000 31.000 36.000 33.000 37.000 35.000 34.000 37.000 33.000 33.000 32.000 28.000 31.000 29.000 30.000 29.000 32.000 32.000 Transfonn: Untrnnsformed 1-Tailed Isotonic Conc-o/o Me;in N-Mean MG:.n Min Max CV"lo N
    t-Sbt Critical MSO Mean Control-1 29.000 0.9898 29.000 27.000 33.000 5:861* 10 31.600 Conlrol-2 z9.309 1.0000 29.300 28.000 32.000 6.446 10 10.7 30.300 1.0341 30.300 26.000 34~000 6.233 10 -1.558 2.287 1.908 31.600 21.4 30.700 1.0<478 30.700 27.000 35.000 6.876 10 -2.037 2.287 1.908 31.600 42.B 32.200 1.0990 32.200 29.000 35.000 5.436 iO -3.835 2.287 1.908 31,600 85.6 32.700 1.1160 32.700 29.000 36.000 6.455 10 -4.434 2.287 1.908. 31.600 100 34.700 1.1843 34.700 33.000 37.000 4.516 -io .5,931 2.287 1.908 31.600 tntake 31.200 1.0648 31.200 28.000 35.000 7.215 10 Auxiliary Tests Statistic Critic:il Skew Kofmogorcv D Test indiCates normal dis!ribution (p > 0.01) 0.78405 1.035 0.3,1775 Bartlett's Test indicates equal variances (p = 0.94) 1.25092 15.0663 The conlrol means are' not skini!icantlJl different (E! = 0::;11 0.37338 2.10092 H:i:Eothosis ToS: (1-tail, 0.05) NOEC t.OEC ChV TU MS Ou MSD!! MSB MSE F-?rob Dunnetrs Test 100 >100 1 1.90809 0.()658 40.88 3.48148 1.0E-07 Treatmenls vs Conlrol-1 Linear lnt8,-Pol3tion {ZOD Rosamples) Point SD 95o/oCL Skow >100 >100 ICOS IC10 IC15 IC20 IC25 IC40 JCSO >109 1.0 ~------------~ >100 >100 >100 >100 0.9 0.B 0.7 0.6
    g 0,5 g 0.4
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    ~ 0.2 0.1 0.0.............. ___.:>----<l-0 -0.1 -0.2 -0.3 +-~~~~~~~-~~~~-i 0 Dose-Rosponse Plot ~ 25 " E 20 Q. ii: 15 \\(l 5 0 ~~----,N,---~~---~,..---..,---~~r---0.,.------j~ ~ ~ 6 ~ ~ ~ 0 i 0 0 u u Page44 of87 50 Ooso% 1-iail, 0.05 levet of stgnmcance 100 150 N-Moan 1.0000 1.0000 1.0000 1.0000 1.0000 l.0000 Kurr: 0.02026 dr
    5. 54
    TVA I Sequoyah Nuclear Pla~t, Outfall 101 - Intake .May 17-24, 2016 Statistical Analyses '.) Enltlranm"'""ITestlng S..linlum. Inc. Ceriodaphnia S.ul"l(ival.and Reproduction Test-Reproduction Start Date: 5/17/2016 Test ID: CdFRCR Sample JD: End Date: 5/24/2Qi6 Lab!O: ETS-En11ir. Testlng Sol. Sample Type: Sample Date: May 2016 Protocol: FWCHR-EPA-821-R-02-013 Test Species: Comments: Cone-% 1 2 3 4 5 6 Control-1 33.000 29.00Ci 30.000 29.000 27.000 29.000 Control-2 27.000 26.000 28.000 29~000 31.CiOO ~0.000 10.7 29.000 32.000 34.oob 29.000 28'.000 31.000 21.4 31.000 30.000 31.000 35.000 30.000 29.ooo 42.8 32.000 34.000 32.000 32.000 33.000 33.000 85;6 34.000 33.000 34.000 32.000 36.000 31.000 100 34.000 35.000 36.000 33.000 37.000 35.000 Intake 34.000 35,000 32.000 28.000 31.000 29.000 Transform: Untransformed Conco..."fo Mean N7Mean Mean Min Max Control-1 29.000 0.9898 29.000 27.000 33.000 Control-2 29.300 1.0000 29:300 26_000 32.000 10.7 30.300 1.0341 30,300 28.000 34,_ooo 21.4 30.700 1.0478 30.700 27.000 35.000 42.8 32.200 1.. 0990 32.200 29.000 35.000 85.6 32.700 'l.1160 32.700 29.000 3*s.ooo 100 34.700 1.1843 34.700 33.000 37,000 Intake 31.200 1.0648 31.200 28.000 35.000 Auxiliary Tests Shapiro-Witk's Test indicates normal distribution (p > 0.01) F-Test indicates equal variances (p = 0.61) The control means are not significantly different(p*= 0.71} Hypothesis Test (1-tail, 0.05) Homoscedastic t Test indicates no significant differences Treatments vs Control-2 .*cv% 5.861 6.446 6.233 6.876 5.438 6A55 4.516 7.215 7 27.000 31.000 29.000 27.000 29.000 35.000 34.000 30.000 N 10 10 10 10 10 10 10 10 Statistic 0.96445 1.42056 0.31338 8 28.000 29.000 30.000 32.000 30,000 32.000 37.000 29.000 t-Stat -2.045 MSDo MSDp 1.61122 0.05499 Dose-Response Plot TVA I SON Outfall 101 - Intake DMR-Discharge Monitoring Report CD-Ceriodaphnia dubia 9 10 29.000 29.000 30.000. 32.000 29.000 32.000 3~.000 30.000 32.000 35.000 29.000 31.000 33.000 33.000 32.000 32.000 1-Tailed Critical MSO 1.734 1.611 Critical Skew Kurt 0.868 0.01697 -0.7541 6.54109 2.10092 MSB MSE F-Prob df 18.05 4.31667 0.05577 1, 18 .§ 25 t> 1-tail, 0.05 level of significance 't1 20 e c.. ~ 15 10 5 '§ c 0 0 Page45of87 m N 0 0 l l l l l l J J J J Species: Cerio1l11p/111ia dubia Client: TVA I Sequovah Nuclear Plant, Outfall 101 Dail* Cltemistr : Concentration CONTROL 10.7% 21-4% 42.8% 85.6% 100% 100% Intake Analyst. Parameter* H (S.U.) DO (m21L) Conductivity (µmhos/cm} "Alkalinity (ma CaCOJIL) DO (mg!L) ~onductMty (~tml1os/crn) '.'Alkalinity (mg CaCO,;IL) ~Hardness (ing CiiCO,;IL) ":TR chlorine (mg/L) DO (m.g/L) Conductivity {µmhoslcm) "Allmlinity (mg CaCO;/L}
    • Hardness (ini; C~C03/L)
    • TR chlorine (mg/L)
    • Tern* eraturc (°C}
    6'-\\ \\~ ~!S IL- "- 0.1 D 1.s.a Initial Final Page 6 of7 Date: 05-17-16 measurements only.) Initial Final Initial Final
    • Temperatures perfonned at the time of test initiaiion, renewal or 1cm1i11ation by the analyst identified i11 the Daily Renewal lnfommtion table locntcd on Page I. Alkalinity. hardness and total residual chlorine perfom1ed by Lite analyst identified on the bench sheet specific for eacl1 analysis and lranscribed 10 Ibis bench sheet by: +*
    Page 46 of 87 SOP A Tl] - Exhibit ATJ I.2. revision I 1-01-14 l l l l l l J J J J j J Concen-tration CONTROL 10.7% 21.4% 42.8% 85.6% 100% 100% Intake Page 7 of7 Species: Ceriodaplmia dubia Client: TV A I Se uovah Nuclear Plant. Outfall IOI Date: 05-17-16 Day {Analyst identified for each day, performed pH, D.O. and conductivity measurements only.} Parameter H (S.U.} DO(m!?IL} Conductivity (µmhos/cm)
    • Alkalinity (ma CaCO;/L)
    • Hardness (me CaCO;/L}
    Analyst "'Tern erature {"C} H{S.U.} Conductivity (µmhosfcm) DOCmg/L) Conductivity (µmhos/cm)
    • Alkalinity
    {mg CaC03/L)
    • Hardness (mgCaCO:;/L)
    • TR chlorine (mg{L)
    • Tern erature (°C}
    H (S.U.) DO (ma ) Conductivity {~1mhos/cm} '"Alkalinity {m2 CaC03'L)
    • Hardness (mo CaC03/L)
    "TR chlorine (mg/L}
    • Temperature r'C)
    Initial Final Jnitial Final Initial Final Initial
    • Temperatures perfonned at !he time oftesl initiation, renewal ortem1ina1ion by the analyst identified in Elle Daily Renewal lnfomialion table localed on Page I. Alkalinity, hardness and total residual chlorine perfonned by the analyst identified on the bench sheet specific for each analysis and transcribed to !his bench sheet by:
    ~. Page 47 of 87 SOP ATU -Exhibit AT! 1.2, revision 11-0I-1"1 Final ..) Ehvlronmental Testing Solutions, Inc. Conectllr11tion l'nromrlcr Onv.O
    • . *
    • Initial*:
    11111 CSU) 7.31 DO(me/1,1 1.11 Conductlv!ly (mllhQs/cml 31i! C11111rol Alkullnlh* (mg/L CnCOJ) '61 llnrdnm (n*wL CnCOJJ 88 Tcmn~ruturc 1°Cl .24.7 oil fSU\\ 7.32 I0.7'X, DO (n'ullLI 7.8 Conduclivlty Cnmboslcml 312 1'onmcn11urc ("C) 24.7 lnll ISUI J.31 21A% OOCml!/Ll 7.9 ContluclivllY,.,,;;hos/oml 291 Ton111er"tur~ ("C) 24.7 Ull CSIJ1 7.29 -12.8% DOfm11/LI 7.9 C~ilductlvltv (umhos/cin) "261 Tomnoruturc C"C) 24.7 1111 ISUI 7.28 85.6'1.. DO (11111/Ll 7.9 - CoillluctMtv fllmhos/cml 205 Trmncrature t"Cl 24.9 1111 ISUI 7.26 DO fm11/Ll 1.9 Coilduclil'lll' lnn1hos/~ml 184 llJU'ilu AllMlinlty (nlg/L CliCOi) 64 lfardnm (nig/L CuCOi) 76 - Totnl Rositlunl Chlorine lml!/Ll <0:10. 'rcmriCl'lllUI'~ ("C)
    • 2S.0 oH (SUI 7.28 DOlnm/J,l 7.B CunducUvltv (umhus/cm)
    JOO IUll'Y., lnl;iko Alknllnlly (mg/L-CuCOi) 68 llnrdnm (1t1g/LCaCOJ) 72 Tolill Rosldunl Ch!Drl11e Cnirl'IL l <0.10 'l'cmncrnlurc (°C) lS.0 TVA I Sequoyah Nuclear Pinnt, Outfall 101, Non-treated May 17-24, 2016 Cerioc/11p/111i11 duhia Chronic Whole l!;fnuent Toxicity Test EPA-821-R-02-013, Method I002.0 Daily Chemical Analyses Davi
    • Onvl Dn,*3 Dnv4 Plnul:
    • Initial -
    Plnol
    • lnlllnl -
    ,. Fhml
    lnllldl
    • - Tnlllal -
    • 1;1nnl 1.53 7.39' 7.21 1.30 7.56 7.64 7.23 7.SO 1.S6 7.8 7,9 7.8 7.8 7.8 7.8 7.R 7,8 7,7 313 307 310 31~
    - 61 61 88 86 - - 24.G ,24.8 .. 24.1..... 24,8 . J4.S 24.8 . J4.9 24.9 24.9 1.52 7.S2 7.18 7.22 7.S4 7.58 7.22 7JO 7.S.9 7.8 7.8 7.8 .7.8 7.8 7.8 7.8 7.8 -7.7
    !70
    .301 2Cil '.191 14.8 24.9 24.6 24.9 24,9 24.7 l4.9 25.0 25;0 7.St 1.S4 7.18 7.24 7.54 7.60 7.21 7.lO 1.59 7.9 7.9 7.8 7,8 7.9 7.8 7:9 7;8 7.8 .287. 2111 280 274 .24.8 24.9 . 24.6 24.9 24.8 . l4.8 .l4.7 -* 2S.0 2~J 7.SI 1.SS 7JS .7.22 753 7.60 - 7.2[
    • 7.18 -
    7.59 7.9 7.9 7.8 7.9 7.') 7;8 7.9 7.9 7.7 . lS8 -
    !47
    '.lSl 251 24.8 24.9 24.6 25.0 24.8 24.s 24.7 25.0 2s.o --7.SI 7;54 - '7;16 . 7:20 . 7.S[ ,,7,59 '7.21 . 7;26 7;59 7.9 7,9 7.7 t9 7;3 7.'8 7.9 7.9 -7;8 lOI 203
    ?01.
    l02 24.5 !!4.9 14.8 lS.O '25.() 24;8 14.7 25.0.
    • 2U 7.SI 7.Sl
    _7.IS 7.17 1.SI 7.SS 7.20 7;26 7.S9 7.9 1.9 .7.7 8.0 7:9 7.9 7.9 7.9 1;9 182 184 183 - 186 ,66 64 12 76 <U,lO ...0.10 24;9 2S.O 14.7 "25.0 24.8 2U 24.7
    is.o 14.8 7,Stl 1.S6 7.16 7,21 1.53
    . 7.58 7.12 7;28 7.58
    .** '7;9
    ' *1,g 7.8 ..,., 8.0 . '7:9 '1,9 8.0 ~ ' 7.9
    • 7;9 197 200 188 199 73 73 12 76
    ... 0.10 <0.10 24,9 . lS,O 24,5 24.9 24.8 24.9 24.8 24.9
    24.8 l*rojecl nu111bcr: ______
    1_1.i_s_u Day!i lnlllal llinBI 7.61 7,21 7.7 7,8 320 24.7 24:.4 7:63 7.21 7.7 7;9 294 - 24.8 24.6 7.64 1.20 7,7 - 7,9 279 2U 24.6 .7.64 7.19 7;3 7.9. .253 24.8 24.2 1'63. 7.19 7.9 8.0 210 24.a 24,4 7.63 7.18 7:9 a:o 191 24.S 24.4 7.62 7.18 - 7.9 8.0 196 24.il 24.4 Do\\*6 lnlllel Finni 1.65 7.13 7,7 7.8 299 24.8 25.2 7.47
    • 1.11 7;8 7.S l93 24.8 25.0 7.46 7.08 Ul 7.9 284.
    24.8 lA.8 7.45 7.11 . s:o 7.9 2GO
    ?4.9 24.8 7.44 7;05 a;o 7.9 208 14.9 24,8 7;40 7.06 8.1 8;0 191 lS.0 l4.8 7.40 7.11 8.[
    8.0
    ?U4 24.8 lS.I File: sqn101_051716chem Entered by: J. SuZfer Reviewed by. -6lf-
    I I I I I I I I I I I I I ) Enviranfnent:ii~ Tcning Sarutlons, tnc. Total Residual Chlorine (OIUON-1977) Matrix: Water, RL = 0.10 mg/L Meter: Accumet Model AR25 pH/Ion Meter Page I Page o~f ~l~ Analyst I tVb J Iodide reagent: l.trJQ. l J.:l.. Date analjze~ f)fi /3-..f\\t: 0$-11'1 ~ Acid reagent: _.:tNA I 'l! c_a_li_b_ra_u_o_n_: ___ N_-_ 6 05 1 '_~..,...---------------r----------------i------~--------------."°"\\, 0,1{) mg/L I.00 mg/L mV Change (suggested ranl'!C = 26 to 30 mV) Reference standard number Millivolts (mV) Note: For samples with a residual chlorine of> LO*mwi-. tlie samples must be diluted to be w!thin tlie calibration range. Lb I d d a oratory colltro sta11 ar : Reference standard True valoe (TV) Measured value (MV) % RS = MV I TV x 100 number (mgll.,) (mg/L) (acceptable range= 90 10 110%) * 'S;N5S. 11.{1.fS-050 ().S~ ~ } Ol.f *ti % recisio11: Sample characteristics Residual chlorine (m11;/L) %RPD ={(S - D) /l(S+D)/21} x 100 {acceptable range=+/- 10%) ...J. Dupljcate s l ampi e measi(remeuts: Sample Sample ID number
    _;__~, > "
    , Rea2entBlank \\lbt:6\\".l-;Q2-C.,\\I._ 00\\ \\boQ'1-.C>3 ~ CXY.:> \\ \\D D'5U1i.() t \\~f\\J<~t-J lO\\ \\loDSlb.()2.. I.L lt-lTf\\(e_ S/ ,O.Oll'f
    ,.**~*.'.-*.
    DL.o.ot>r97 J 1-----66 os-17/'q_ Sample charactcristies Residual chlorine (mg/L) ~::::f' ~*.. ~ *. ***-::i"'* *. ;.._._-.,_ - _,.,_ /e>. D/t/t Orct11t;(_, lf".. dv, PrtrHc.}e.J '(_ b, ODOtQ l( fct.11, c..lovc.t-1 1 1 Pa.r1-J'"'~t t..tJ.dOS'tfb ft)() lo Jor, C.le.ccr <t).D~} fJ'l/f fQ.,,, vi< -.r <D.Doj~~ NC. 05171 ~ Note: All samples were analyzed in-excess of EPA recommended holding time (I 5 minutes} unless otherwise noted_ l b a oraton* coutro standard: Reference standard True value {TV) Measured value (MV) % RS = MV I TV x JOO number (mg/L) (mg/I.) (ncccpt!lblc rangl' = 90 to 110%) IA/.iJ. /\\./ \\16"" 0.50 0 ~S'"~ft. JDl.J.,-. Reviewed by,...... Date reviewed 05 \\ 31 t f Page49of87 SOP CB - Exhibit C8.1, revision 01-0l-!3 I I I I I I I I I I I \\ Environnu:~I Tes:it19 Solutions,. Inc.. Total Residual Chlorine (ORION-1977) Matrix: Water, RL = 0.10 mg/L Meter: Accumet Model AR25 pH/Ion Meter Page lD Page __ l _of_\\_ Analyst I Nb Date analyzed t-'().'-'-.~---1-f--t-=~---; Iodide reagent: ~:tfV~tl-~"""i}.;....::),_=-------i Acid reagent:..__ lN_A. __ 7_4__._\\ __ __, Calibratioll: O.IO mgiL l.00 mg/L mVChange (su~cstcd ranee= 26 to 30 mV) Reference standard number .IM.i 11.i"l' ~tut..t,J!Jtr Millivolts (mV) 571. ~ 'lf't..f ).7#~ Note:: For samples with a residual chlorine of > 1.0 mg/L, the samples must be diluted* to be w1thm the calibration range. Lb l t I a ora orv COlltro sta11t art : Reference standa*rd True value (TV) number (ing/L} .tfV!.t I l/!./s" 0.50 recisio11: Sample ID Sample characteristics Sam le measureme11ts: Sample number Sample ID - Measured value (MV) (mg/L) o.s-og Resid.ual chlorine. (mg/L) . s LP.01~ %. RS= MV ITV x 100 (acceptable.range= 90 to 110%) JO(~{. '.fr; %RPD = {(S - D) /l(S+D)/21} x 100 (acceptable range=+/- 10%) ~----./VI OS/14_ Sampie characteriStics Note: All samples were analyzed in excess of EPA rc.:ommended holding time (15 minutes) unless othcm~sc noted. l b { a oratory contro stmulunl: Reference st:md:i.rd True \\*alue (TV) i\\*Jeasured vali1e (_MV) % RS =' MV I TV x 100 number (mglL) (mglt.) (:1cc:cptable range= 90 to l l0%) Ifvi.s.. 14<.{S-0.50 0*4'f~ qq.~ fo Reviewed by I~ Dale reviewed ;.; \\9 { 4' Page 50 of87 SOP CB-Exhibit C8.l, revision OI~OI-13 ) Envlro1nmmtotTcsllng Solo11Dns, Inc. \\ Analyst Total Residual Chlorine (ORION-1977) Matrix: Water, RL = 0.10 mg/L Meter: Accumet Model AR25 pH/Ion Meter Page L { Page.J__ of_l _ Date analyzed ~~~=--:o.f:;:-~~;-1.-JUJ~ Iodide reagent: I ~ ?~). Acid reagent:.:tf'/Q. 141 Calibration: 0.10 mg/L 1.00 mg/L mV Change (suggested range= 26 10 30 mV) Reforence standard number ~ /"l'i" TM! N'{S"" Millivolts (mV) .!:j/(). 7 !> '1't, g
    i~. /
    Note: For samples with a residual chlorine of > 1.0 mg/L. the samples must be diluted to be \\VJ!hm the cahbrauon range. L b I a oratory contro stm1 d i arr.: Reference standard True value (TV) !Vleasured value (MV) % RS = MV I TV x 100 number (ing/L) (mg/L) (acceptable range= 90 10 I !0%) .+/-Nis J4l4S-o~so 0*53(, ID1.).% D I' l up rcate samp e prec1st011: Sample Sample ID Sample characteristics Residual chlorine %RPD = {(S - D) /[(S+D)/21} x 100 number (mg/L) (acceptable range=:!: 10%) D ~/(. 'Tt11, C}rqr1 P'(rf/r1 SLo. o~ a, \\ln{\\S'l\\.D\\ 'u~~mww, I Duplicate .. - ~. ~*.-,.. ' DL'.'o. o;t.(oO /116QSl.lh ..1
    • -,* "*i.
    . *. ~ s, l amp e 111eas11reme11ts: Sample Sample ID Sample characteristics Residual chlorine number (mi;/L) -~""""'~>:..-***.,. Rea!!ent Blank ""*w** ' --i-._...,..*. L~.olr,.o~ \\( llf°'6U.o l \\\\J~\\S.Q~\\O\\ Pii~ t¢/\\ 1 lie~, ~a_f'tldc1 .C::.6. 0 J ~ s- \\\\0620.()2. ~\\ \\~Tl"\\~ A..le let.A, Clc<.Af 1 p a.r I-} r,/ c. S. L_tp.oof./ Pl/ ~ i--- ~- ~ t...-- / V& o~-J,Tr~ r--.. !vore: All samples were analyzed m excess ot EPA. recommended hold mg ume ( 15 mmutcs) unless otherwise noted. Labort1forl' control standard: Refiffence standai-d number Page 51of87 True,*aluc (TV) (mg/L) 0.50 i\\'le~tsurcd value (MV) {mg/L) % RS= MV /TV x 100 (acceptable range= 90 to Il 0%) JO.'J.7f Reviewed by 1 \\JV Dace reviewed ()'5'Z01v SOP C8-Exhibit C8.l,revision 01-01-13 l l l l l 1 l J ~ f;:~FI a*.~\\El (~ I- ~-""*\\ I .*...... i ~
    • ---~
    ) Env1nmmcntalTestlng Soluttom.. Inc.. Analyst I, 3t.() Date analyzed QS-1..'Z.-{ \\0 Titram 11ormali
    • pH of Deionized Titrant Begin water reference standard ml
    = 4.5 S.U. number number Laborato colltrolsta11dartl: Reference standard True value .Sample number (TY) volume (mg CaC03/L) (ml) lNS5t t..\\l'-\\- 100 _mo Sample volume (ml) (00 _) oupl!catc (J3) Matrix s ike recovery: Reference standard Spike va_lue Sain pie number (SV) volume (ma CaC03'L) (inl) 1 "1 ~s \\'-\\ \\ '-\\ so oo Page Alkalinity (SM 2320 B:.1997) Matrix: Water, RL = LO mg <::;aCOs/L Titrate samples to pH=4.5 S.U. Time initiated ~--0_0_'1""'3~--1 Time completed ~--~' 0~'-~--- Normality (JV) ofH2SO~ pH Factor or Multiplier End Total = (5 mi Na2C03 x 0.05)/E = (N x 50000)/ l 00 ml sample =Nx500 ml mJ = 0.25/E (E) . {acceprable range= o.0180 - 0.0220) Begin End Total ml ml .ml H.. 'O ih'? q.~ Begin End Total ml ml ml t,\\.3 2-bA" 5.kJ-' Z.b.Gl '32-5 5.b Begin End Total ml ml ml lb~ 3~.-t (Q.5 -Multiplier tO*l-Multiplier (0.1} J MultipHer 10.q. IO. 1- . Alkalinity (MY). % RS=MV /TY x 100 (mg CaC03'L) (acceptable range ='90 to l10%) (02- . I 02 -D'1o Alkalinity %RPD= (mg CaCOJiL) {(S
    • D).ll(S+D)/21} x 100 (acceptable range = +/- 10%)
    o5*2.1*lb Spike alkalinity (A) {mg CaC03/L) 110 _su) r Sample alkaliµity (B) (mg CaCOJ/L) Me;tsured spike value (MY)' MV=A-B % R=MV /SVxlOO (acceptable range =75to 125%) ( m_g CaC03'L) 100 -O~VJo s l amo e 111eas11reme111s: Sample volume Begin End Total Alkalinity Sample number -Sample ID (ml) mt ml nil Multiolier (me CaC03'Ll 06\\e>l((JA 'ffil-\\SvJ
    • t !JO 31_.'-I-1.(3., 5,-.:t 10.7-ln f 06\\t.\\\\v R 4-3.(. H~.e, 5,7
    . Cril 05 1 ltJ l \\P 0-0 5-B S-~ C.o'}, 6S*'f"\\-\\\\..~ 011-lsw \\)V.\\ 5.~ I' *'5 6 lb l O.S.-\\lo-\\~ I 2- \\l.S f'=J..'4-S.Cj ~1 O.~:H&* l"' A_ J 3
    • iJ 11-.tf-1-3-"l.. 5:6 ln J..
    I \\Q()S,f1. Q \\ .dr r-..../11 ~-hM.r, \\ '50 Z3.1. 'l.b.'f ?>.2. l2) l.n0 \\"" ~S,\\'\\.() \\ . Ill) \\ 2-1 i.t:i.4 30.0 3.\\a I 7 '\\:io'5.'""L\\-Q\\ J J ..L 3&.f.O '1~0 ""' a, 30.0 Page 52 of87 Reviewed by: Date reviewed: I OS*1-1.-tC.. SOP C6 - Exhibit C6. L revision 01-0 I -l 3 l 1 l J j gff"";'f'1~ c-_~_, ) Environmcnt;atTcstin9 5DIUtlan~ Inc. Analyst I ~ . Date analyzed 0$. z:i.* I~ Alkalinity (SM 2320 B-1997) Matrix: Water, RL = 1.0 mg CaC03/L Titrate samples to pH= 4.5 S.U. Page LJD Page 1... of 'f-Time initiated 'P=- I Time completed ~SW OS-1.1..*\\; Titra11t 11orma/itv am/ mu/tiolier detw!11i11atio11: -n' n~ Normality Deionized Titrant checK water reference standard 4.SS.U. number number L b I d i a oratorv co11tro _ sta11 art. : Reference standard True value number (TV) (mgCaCO.i!L) INSS l~l't 100 Duplicate (B) atnx sp1 *e re,cpverJ1: _ Reference standard Spike value number (SY) (rn1tCaCOJIL) 11'1 SS l 4l"t l_OD ~u,,;"* ml Sample volume (inl} 100 Sample volume (mil o.o Sampfo volume (ml) 50 Normality (N) ofH2SO~ pH Factor or Multiplier .... _.. _) (5 ml Na~~<?3 x 0.05)/E - (N x 50000)/ 100 ml sample ml ml V*- =Nx500 (E)
    • (acceptable range 0.0180 - 0.022U) -
    . Begin - End ml. ml . 3'-f;O 115.b Begin End ml Begin End ml ml .t*_'L 1q.3 -~ OS* 2.'2.-l ~ Alkalinity (MV) % RS= MV I TV x 100 Total Multiplier. (mg CaCO.VL) (acceptable range ml =90 lo 110%) q,~ {0.1- /03 /03.(J VJ() Alkalinity %RPO= Total Multiplier (mg CaC03/L) {(S
    • D) /l(S+D)/2)} x !00 (acceptable range== 10%)
    10.~ s J D Spike alkalinity (A) Total Multiplier (mg CaC03'L) ml n., I (1.) 10..:1 Z.60 Sample alkalinity (B} Measured spike value (MV) % R = MY I SV x 100 (mg CaCO.i!L) MV=A-B (acceplable range (me CaCOJIL) =75to125%) ISO 110 JI 0. 0 '10 s l amp e 111eas11r;em.~1ts: Sample volume Begin End Total Alkalinity Samole number Samnle ID_ {ml) ml ml ml Multinlier (me CaCOJIL) tt..tie;. l ~. o'-{ 1-rv' A A.t..F v o t:; 0 t<l3 _ 1~.o ~-~. (t.J 1o:=t ~ .j l 2-1-.e> 4~cn i I \\o<IS \\&°* 03 lf'IT 13.0 /VO -Hf~ \\\\..,Ob'\\.~.~<. W Dcnll c_yt, IUO -z:~.0 33.q Co.I tnS l \\or-E;.1~
    • CS\\
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    \\\\.o<;;l~-O<t Pm \\.\\l.-i 45.3 3,q
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    -;.o b*I ?J.1 II (o~ Date reviewed: I.Oy-z,-,,.tb Reviewed by: Page 53 of87 SOP C6-Exhibit C6.l. revision 01-01-13 l l l l l l l l 1 i J I J 1 J J ~ r~: ~~()? r:;_ I I \\~ - _. El\\\\')rtionmea1.,1TcstlngSo!utTons..rnc. Alkalinity (SM 2320 B-1997) Matrix: Water, RL= 1.0 mg CaCOs/L Titrate samples to pH=4.5 S.U. Page 41 Page.3 of i.1-Tllne initiated r:s:: ~ Time completed S 0 :.z:z. T." rtra111110rma/i1J* a11d multiolier determination: Normality Normality (N) of H2S04 pH Factor or Multiplier .--- v Deionized Titrant check-Totat (S ml Na2C03 x 0.05)/E = (N x 50000)/ JOO ml sample iseg111 water reference standard
    • ml ml ml
    =O.ZS/E =Nx 500 4.SS.U. number number (E) (acc~ptab~ n n120) *r---_ WJ Lb ti a oratonr co11tro/ sta11dar, : Reference standard True value Sample Alkalinity (MV). % RS= MY I TV x 100 number . (TV) vol ii me Begin, End Total Multiplier (mg CaC03'L) (acceptable range: (mg CaC03'L) (ml) ml ml. mL =90 to 110%) INSS P*h '-\\
    • lOO 100 (o.\\
    16-~ q,7 10.1 /Oaf I o'f. 0 'Jo D l" I up.rcate samri. e f}recisio11: Sample AlkaJinity %RPO= Sample Ample ID volume Begin End Total Multiplier. (mg CaCO.i{Ll {(S - D) /f{S+D}/21} x !00 number Tv * (ml) ml ml ml {acccpt:iblc range=.:!: 10%) ~n....,* 15.CO s tot \\ \\o tlS.""'U:l.Q 3 so 1~.'b 3.0 2) 1n;:r ..\\.. Dup!lcate (B) l 1q,.~ '2..l-B ?,.O ~ J, D lo"\\ ~.~Y.:1.h k atn-.. spi e recove.rv: Reference standard, Spike value . Sample ~* -. . Spike alkalinity (A) number . (SV) volume Begin End Total Multiplier (mg CaCO.i/L) (mg CaCO.i/L} {ml) ml ml ml JtJ SS \\111'-t JOO 50 110.~ 'U7*1-9--'1 ('J..-) lO*T I~ Sample alkalinity (B) Measured spike value.(MV) % R = !\\'IV I SV x !00 (mg CaCQ3'L) MV=A-B (acceptable range (mg CaCOJIL) ==is to 125%) \\QI.} \\Olo lO(o.0"7o
    s. ample mensuremellts:
    Sample volume Begiri End Total Alkalinity Samole number Sample ID : {ml) ml ml ml Multinlier (m~ CaC03'L) \\ \\:.C<;;.1la.0\\ r\\t l\\S& J U \\J l 50 i&.'T z_q.S z~e ft\\, 10:+ {n0 i \\lo O'S.\\~. GS I 7_ Z..'t. '=> 3'l..? 3.0 C8t.f- \\ \\ocS..., r-..al.. J 3 31..'7 35.'-\\ tA fl)t- \\\\o~\\\\,.O"L 'TJA-SG.~ ~~ ' 35.L\\- ?JB.b 3.2-CD8 l\\oDS H;. o\\o I z.. 3e.~ 4-2-0 3.'f 1-3 1 loO'S. -z.ti.OL-j 3 4-2.0 ~5.Y.. 3.'-f
    J-3 l \\.., hC:.\\ lo. 0 L-rf\\/'ACC\\N\\\\.t\\1.hJ t qs.'1-L\\-S.q...3. 0 lo+
    11.cos,~. O"=> ( Z- \\_ 0-0 3.0,3.0 ~---(jt1-* 1 3 3.0 (o. J..- ?, :z. ~ ln9i 1\\o:.OS<.O. <1L-I Date reviewed: I ()') *£"2.*lb Reviewed by: Page' 54 of 87 SOP C6-Exhibit CG.l, revision Ol-Ol-13 i l l l l l l 1 I J J I _] J ~r~'"'r"F'l~ ~ -,. -* ~* *1
    _,'2>-,
    - -*_I - ~:-:::../ Page l.\\-Z... Page i..f of t .J Etnti"1n111mWTe$dngSolall*1U.ln<- Analyst I w Date ana!Yzed. OS *z.'2--\\ l,o Alkalinity (SM 2320 B-1997) Matrix: Water, RL = 1.0 mg CaCO:;/L Titrate samples to pH=4.5 S.U. .Timein.iti~ ~ Time completed, 11" l* d /[C ti ttram 11onm11ty.<m 11111 Ill* l/!T t eter111mat1011: )~ Normality Norma{ity (N) ofH2SO~ pH Factor or Multiplier Titrant check . Begin Ei,,d Total = (5 ml Na2C03 x 0.05)/E = (N x 50000)/ 100 ml s:imple D water ~~nee standard ml ml ml =0.25/E. =Nx500 =4.5 s.u. n ber number. (E) (acceptable range= o.01so - 0.0220). Laboratory co11trol Stai.~: Reference standard Truev~' Sample Alkalinity (MV) % RS= MV /TV x 100 number (TV) volume Begin End Total Multiplier (mg CaCO,y'L) (acceptable r:inge (J11g C;i<;03'.L) '-.(ml) ml ml ml =90to110%) 100 ~. D11plicate sample pfecisio11: Sample B~ Alkalinity %RPO= Sample Sample ID volume End
    • TQtal
    .Multiplier (mg CaC03'L) {($- D) l!(S+D)/2l} x IOO number (ml) ml '-.ml ml (:lcceptablc range=+/- 10%) s Ouplieatc (B) ~ D lYlatrixspike recoverv: Reference standard Spike varue Sample ~ier Spike alkalinity (A) number {SV) volume Begin End Total (mg CaC03'L) (me CaC03'L} (ml),. .nil ml ml "\\ '\\.. Sample alkalinity (B) Measured spike value (MV) ~MV/SVxlOO (mg CaC03'L} MV=A-B ptablc range (mg C:IC03'L) 5to1:?5%) l amp. e 111eas11re111ents: .... Swos iz lb Sample volume Begin End Total Alkalinity Samole number SamoleID (ml) ml ml ml Multiplier (m~ CaC03'L) ~.7 l.IMA MW:.vJ 100 (o. i.. 1'2.0 s.e 10.1-fo'i.- It{):;.2'. ~to 6 j t ,,.1.0 lt-b 5.(o J, ~o r-_*~ I
    • h. ~
    ~~-11 lb Reviewed by: ~)\\I-"=..,__, Date reviewed: I OS*"t.t.*ll.P Page 55of87 SOP C6-Exhibit C6.L revision 01-01-13 l l l l 0 fih t=~-~::~ ~ Q
    i t**1-
    • 1-I
    --~ - ) Envl:c:iamcnta1 Tcstln9 ScJucJcns.. Inc.. Analyst 11{~
    • Date analyzed O!j'- a.J -ffl Hardness (Sl\\12340 C-1997)
    RL = 1.0 mg CaCO.;/L
    • r:
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    • c 1 rtrallt 1wr11u1 rtJ' mul mu/11p rer fo eterm111at1011:.
    Page 11 Page_l _of 'i Time initiated t-'~-f O ____ _ Time completed _ l l.J.t{O ~--------' Titrant Normality check Begin End Total Normality(!\\? ofEDTA pH Factor or IVIultiplier reference standard ml ml ml =0.2/E = (N x 50000)/ 50 ml sample number number (E) {acceptable-range= o.inso -0.0220} =Nx 1000 .tJ\\R 7DS' t'l'JSS JLJq~ o.o {o.o /0*0
    o. o~oo laboraton* co11trol standard:
    Reference standard, True \\*alue Sample number (TV) volume Begin End Total Multiplier (ing CaCO.VL) (ml) ml ml ml l1V!.1 I~ o.\\. 40 ,50 /O*O Jd..O ~.c; . )..o,O D l" l up rcnte samv, e precrsron: Sample Sample
    .sample ID volume Begin End Total Multiplier number (ml) ml ml m:I OS \\°6LIJ}b mttsw Sf;
    /l.o.,,.t{ ~.q* ~o.o .J Duplicate ~B)
    • t J~.q 4-b.a Y.. ~
    .L I,. (1.-J, "k atrrx SPI e recoverp: Reference standard.. Spike value Sample number ' (SY) volume Begin End Total Multiplier (mg CaC0.3'L) (ml} ml ml ml trv.ss Ji.tol L.tC? 50 . It.. y J.i.'1 ~-"f J.ti.6 ample meas11remellts: Sample hard.ness {B) (mg CaCO.VL) Measured spike value (MY) MV=A-B. (mg c:iCOJIL) d.().0 Hard.ncss (MV) ~RS= MV /TV x 100 (mg CaCO.ll'L} (acceptable range =90to110%) t.f 0 100. 0 % Hardni!Ss %RPD= (ing CllCOJ/L) {(S-D} /l(S+D)/21} x 100 s as D ~g llb <>JMI~ Spike hardness (A) {mg C11COJIL) rJb or~ 11~ -{~i l}o %R=MV/SVx 100 ~ Sample vo!Ume Begin End Total Hardness Sample number Sample ID (ml) ml ml ml Multiolier (mit CaCOJIL) TV=ND !31ank s-o 6.o c.a t?-o to~O AJ.D (should be = 0 mg CaCO;/L) lfl6.\\ e -/lo Q n-\\l+sw J~.s ~'7, I L.J.3 g~ 0$-\\'-\\.'l'lab ml--1sv.J u\\J \\ ~i.I '31.5' l.f.'\\ ~g C>~* \\'le.\\ lei - l
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    ~ I fuo Note: If > 15ml oftilrant is used,. sarnple musl be diluted. Reviewed by: '\\ Page 56 of 87 1...----PI~~__. Date reviewed I O ~-1.\\-1'° SOP C7 - ~xhibit C7. l, revision 01-01-13 l 'l 1 l J J l ! l .....) ~ r~c! '~r\\2W (~ =*~ -,_ - .) E'mrJrcnmcntafTeulngiSafuth:lns.lnc.. I. Analyst I f/(, Date analyzed. 06'-~J~ Jt Tt 1 1
    • r 1trmrt 11or111a rty a,11t. 11111 tID 1er t. etermmat1011:
    Hardness (SM 2340 C-1997) R.L = 1.0 mg CaC03'L Page 10 Page ~ of_l. ...... / __ _11me inlliated I~ 1 11 Time completed Titrant Normality check Begin End Totnl Normality (N) ofEDTA pH Factor or Multiplier reference standard ml ml ml =0.2/E = (N x 50000)/ 50 ml sample number number (E) (acceptable r:rngc = 0.0180 - 0.0220) =Nx 1000 ~ tf D5J.J J b Lb I l
    t.
    a orator_y co11tro stnllt. (lrt.: Reference standard True value Sample Hardness (MY) %.RS=MV /TV x 100 number (TV) volume Begin End Total Multiplier {mg CaC03'L) (acccplablc rnngc (mg CaC03'L) (ml) ml. ml ml =90 10 110%) .t111ss le.to~ 40 50 ~o~ ~D ~*CJ ':l..~.o l-fo Joo.o !§ D l. up, 1ca1e sample precrsiim: Sample Hardness %RPD= Sample Sample ID voluinc Begin End
    • Total Multiplier
    {mg C"1C03/L) {(S-D) /[(S+D}/2t} x 100 number (ml) ml ml ml l<-1 Pm o3 ~
    • l~.. o. 'J-).1 s.1 q..o.o s 1/0 Duplicate (B) i
    ~1-1 33.C\\ 5.7 J. D Ho /y{, D§J.I /ly ' ntrrx sp1 e recovery: Reference standard Spike value Sample Spike hardness {A) number (SVJ volume Begin End Total Multiplier (mg CnCOJiL} (mg CaCO.l/L) (ml) ml _.ml-* -ml ** 1. il(,0.5'",&.11' ' !Nts I 14(}.). I l..1-0 so ')7:7 .)~..:._ ~,... -*- J...0.0 -lie /S-0
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    . r;. os~fl4 (should 'be= 0 mg CaCO~/L)
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    • 1 ll'A Duplicate (B)
    • ,I
    ' atnx sp1 e reco~*ery: Reference standarcl' S,pil<e val~e number . (SV) (me CaCO.J/L) !"N~ 1qo' go ml ml Sample volume (ml) 50 Sample volume (ml) Sample vplume (ml)
    l.f) ml
    =0.2/E = {N x 50000)/ 50 ml sample (E) (acceptable range= 0.0180 - 0.0220) =Nx 1000 Begin End Total Multiplier ml ml ml l~-1 ~.I d.-o d,_,...,.... Begin End Total . Multiplier ml ml ml. Begin* -End Total . Multiplier ml ml ml
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    • (Jlcceptablc range
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    • Sample hardness (B) lV!easured spike value (MV) o/o R =:'MV I SV x 100 (l)Ig CaC03'L)
    MV;=A-B. (aci;eptnble range (mg CaC03'Ll =75to125%) /Oo ~6 JOf>.O % s, l amp e measuremellts: ~: Sample volume
    • Begin End Total Hardness Sample number Samele ID (mJ) ml-ml ml Multiolier (mg CllCO.VL)
    Blank TV=ND (should be = 0 mg CaCO.y'L} IY& ~a.rt~ \\61§:.1&. Ol\\ ~1/.A ol+r= Pm: ~s ~7.J -*3D.::o ~.'i ~) j.p,o J ;}..O - t\\tD An1Ji '.30..eo )l..fu. l.~ 16c -\\0'-l \\\\,.,(\\~\\k* 10 \\6 l::>S \\\\o.o\\ 'RA S~..J ' '3~-fc S'q S" f, I.'\\
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    • ~A
    - _ (.mU. ml .ml \\\\ol::i~\\,11.(l\\c:, SQ~\\ NI a. -t'")r O*q, J.8 ~ Duplicate (B) i ~ 3.'1. Mi 'k atnr: sp1 e recovery: Reference standard Spike value Sample number (SV)
    • volume Begin End (mg CnC03/L)
    (ml) ml ml INSt ltfO~ go ~5' J.a S:t. .Time initiated~- ~G oS'd.IJ~ Tune completed r-- ~ ~------=---' Normality (N) ofEDTA pH Factor or Multiplier =0.2/E = (N x 50000)/ 50 ml sample (acceptable range= 0.0180- 0.0220) =Nx 1000 "IJ' o5~J I~ Hardness (MV) % RS= MY /TV x 100 Total Multiplier (mgCaCOJJ'L) (ncccpt:iblc range ml =90 to ll0%) ~.o ~o.o Yo {00-07o Hardness %RPD= Total Multiplier (mg CaC03'L) {(S-D) Jf{S+D)/21) x 100 ml J.R. 9-\\~G.O s 7). /.g I~~ D 7"J.. -11G. 05').I I~ Spike hardness (A) Total Multiplier (mg CaCO,JL) ml ~.~ ~) ~O.D J~ Sample hardness (B) Measured spike value (MV) % R = MV I SV x l 00 (mg CaC03'L) MV=A-B {acceptable r:ingc (mg CaC03/L) =75to 125%) /).. -]'/; 'i7.S% s l amp. e measureme11ts: Sample volume B'egin End Total Hardness Sample number Sample ID (ml) ml ml ml Multiplier (mg CaC03'Ll TV=ND Blank NboSJ.1/W. (should be = 0 mg CaCO,.IL) \\\\o~S-Z.o.Q"L. --rv A&~ k\\ 1 }\\ff" 3 ~5'* $-~ 7.S" l. " ~~) d,.e>.O 7'2. L 1.. 1'C. l\\... en... NA~~~lMrOV I 7.!J tt.}.. \\.7 ~$ \\lo~S.\\~* o\\o I ~ t).l. JJ.o J.g 7;J.. l\\o ~ S""ttl,()L J 3 'i:.-* /1. t:> 13.o ~.() l'O:: ro l'lS.*-z.\\-16A t'\\ i.l<\\U f'F..*'2.l*tl. A sc. /3.o J7r5" 4-~ qo 05*1.\\*lb (J... tH!<..~ <> S* ll-ll. & .J.. n.s-d.1.1 '1*'1 ~ -- .... t: l iC~llli ~ Note: If >!Sm! oflitranl is used, sample must be diluted. Reviewed by: Page 59 of87 Date reviewed j O~\\.\\* \\~ SOP C7 -*Exhibit C7.l, revision 01-01-13 Page 60.of 87 Seq~oyah Nuclear Plant Biomonitoring May 17 -24, 2016 AppendixD Reference Toxicant Test and Control Chart \\ u
    i:::
    b.O -U"l N u ra "C I r--. .. r' Pimepha/es promelas Chronic Reference Toxicant Control Chart Organism Source: In-house Environmental Testing Solutions, Inc. 0.9 0.8 0.7 0.6 0.5 1.4 1.2 1.0 0.8 0.6 0.4 1.4 1.2 1.0 0.8 0.6 0.4 USEPA Control Limits(+/- 2 Standard Deviations}
              • ~******~**********
              • ~*************-
    .-*****oc* USEPA Warning and Control Limits (7Sth and 90th Percentile CVs) -._._,.. -~~.. ~**--... -.--**--*--*-* Laboratory Warning and Control Limits (10th and 25th Percentile CVs)
                                                        • ~***********
    Test date 7-day IC25 = 25% inhibition concentration. An estimation of the concentration of potassium chloride that would cause a 25% reduction in Pimephales growth for the test population. Central Tendency (mean IC25) Warning Limits (mean IC25 +/- SA.10 or SA.75) Control Limits {mean IC25 +/- SA.25; SA.90' or 2 Standard Deviations) ,/ ~ Environmental T<!Stlng Solutions, Inc. Test number l 2 4 5 10 ll 12 H 14 lS l6 17 l8 19 20 Telt dat~ 03*0\\*16 03*02'16 03*03-16 03-04*16 OHH6 04*04-1& 04.{}S-16 05*10*16 05*17*!1; 7-day IC,. CT (~/~ KCI) (g/l KCI) 0.74 0.67 0,70
    • 0.58 0.65 0.81 0.70 0.61 0.69 0.72 0.69 o.78 0.70 0.7S 0.71 0.64 0.70 o.os 0.08 0.10 0.09 0.09 0.08 0.08 0.08 Pimephales promelas Chronic Reference Toxicant Control Chart
    .* Sl~tc and.USEPA - laboratory . laboratory USEPA ' Control Llmlh SA.IO Warning limits s.... Conuot Limits s..., W~rnlng Limits CT*2S .CT+lS
    • CT-54.10
    . CT+SA.11 CT* S,,,, cr+s *.,, cr.s..,. cr+s._,, 0.60 O.Bl 0.08 0.62 0.79 0.15 0,56 o.ss 0.27 0,44 0.97 a.so o.sz 0.08 0.58 0.74 0.14 o.sz 0.80 0.25 0.41 0.91 a.so 0.90 0.08 0.62 0.78 0.1S o.ss 0.85 0.27 0.43 0.96 0.49 O.B7 0.08 0.60 0.76 0.14 0.54 0.82 0.26 0.42 0.94 0.52 0.86 o,oa 0,61 0.77 0.14 0.54 0.83 0.2G 0.43 0.95 0.53 0.87 o.os 0.62 0.79 0.15 o.ss 0.65 O.l7 (),43 0.97 o.ss 0.87 O.OB 0.62 0.79 0.15 o.S6 0,SG 0.27 0.44 o.98 0.54 0.86 0.08 Cl.62 0.78 O.!S o.ss a.es 0.1.1 Ma 0.97 /Var*: 7*d IC.,* *1-<fay 25% lnh1b1!1on conceolrillt1n. An esllm*tlah of the cnnceoiration of pot.sslum chloride that would t1U*e ~ 25% reduction In P1111ephales arowt~ for the test pOjlulation. CT* Centrol tendancv (mun IC,.}, S ~ Standard deviation of the IC,. value~. USEPA s... Con11ol lhnl1S CV CT*S.,. cr+s *.,. 0,32 0.39 l.02 0.o7 0.30 0.36 0.96 0.12 0.31 0.38 l,01 0,14 0.31 0.37 0.99 0.14 0.31 0.38 1.00 0,12 0.32 0.39 1.02 0.12 o.az 0;39 J,()3 11.ll 0.32 (),39° 1.02 0.11 Loborotorv ~onuol and Warning limits l~borotory <antral and worning limit~ were established using th* mndar<I deviation of the IC" values corresponding to the 10th and 25th percentile cvs. Thou rang~' are more stringent than the (onttol and warnlnE limitt recommended by USEPA for the test m*thod and endpoint.
    s. 10 * ~tondard deviation corresponding to th~ 10"' percentile CV. is. 10 *0.12)
    SA.u. = 5Landard daviatlan corresponding to the 25' 11 percentile c.v. (SAJ\\ ~ 0.21} USSPA Control and Warning Umlts s.,,,: Stond~rd devlallon corr.!sponding to the*7S11' P"reentile CV. ( s,.,1 = 0.38) s.,,.* Stllndard d*vlu1on CQ(r&ponalng to the 90"' perce~tlle CV. (Sui!* 0:451 CV* C0<!1fic1ent of V*rl*!lon of ther IC,. ~a!ues. mi EPA. i"OCIO. Un<ftnl.'lndln~ arid l\\ctnL111tina lor ~e1hod V~rt:l11llty In Whola ~HluunToxlaly /lppl!caucms ll/\\dor lhf!N~Uam1IPcl1ut.:1n~ Db~har11t Elln!lniuon t'(1)grJ;m, EPA-Bl3*1t.*OO-QOJ. US £nvlronmenl.ll ProJ~CllDn A&cnct, llndnr1111i, Ott. \\ Qi" .J::. IV ~ 0 ra (.::> r; 0 .... *c: c....... 0 bl> u E - -~
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    if: 0.... cu 0 u ~ Cl V'l 2
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    Pimephales promelas Chronic Reference Toxicant Cont.rol Chart I L Precision of Endpoint Measurements Organism Source: In-house Environmental Testing Solutions, Inc. 1.00 0.75 0.50 0.25 USEPA Acceptance Criteria (> 0.25 mg per surviving larvae) 30 10 0 . 30 20 10 .Kentucky Acceptance Limit (c:: 30.0%) USEPA Upper PMSD Bound (90'h percentile< 30.0%) ~~-*---~ ...... ~**************~-................. Test date Control Reproduction; Coefficient of Variation (CV}, or Percent Minimum Significant Difference (PMSD} PMSD is the minimum significant difference between the control and treatment that can be declared statistically significant. Central Tendency (mean Control Growth, CV, or PMSD) Control limits (mean Control Growth, CV, or PMSD +/- 2 Standard Deviations) Page 63 of87 I n1*..,d*nd O'lllewc:db'I msumncr a{ Test number l 2 3 4 s 6 7 B 9 10 11 12 13 14 15 16 17 18 19 20 Testdate 03-01-16 03-02-16 03-03-16 03-04-16 03-05-16 04-04-16 04-05-16 05-10~16 05-17-16 Control Survival (%) 100 100 100 100 97.5 100 1.00 100 100 Precision of Endpoint Measurements Pimephales promelas Chronic Reference Toxicant Data Control Mean Growth (mg/lasvaeJ 0.569 0.753 0.67i 0.591 0.630 o.461 0.647 0.541 0.507 CT for Control Growth (mg/larvae) 0.661 0.664 0.646 0.643 0.612 0.617 0.608 0.597 OJ CT I%) for Control Growth CV (%) 7.9 1.3 4.6 5.8 5.0 3~1 4.5 8.0 5.2 5.9 5.3 12.3 6.3 7.0 6.4 1.8 5.9 Note: (V = Coefficient of variation for control growth. Lower (V bound determined by USEPA ~lO'h percentile)= 3.5%. Upper CV bound determined bv USE PA (90'1' percemlle) = 20%
    • MSO ~ Minimum Significant Difforence PMSO = Percent Minimum Significant Difference MSD PMSD er
    (%) forPM50(%) 0.07 11.8 0.07 8.9 10.4 0.09 13.4 11.<1 0.0!;! 13.5 11.9 o.os 8.1 11.2 0.04 8.6 10.7 O.l:i 17.6 11.7 0.06 11.3 11.7 0.04 8.6 11.3 PMSD is a measure of tes~ precision. The PMSD *is the minimum percent difference between the control and treatment that can be declared s1atistically significant in a whole effluent toxicitV test. Lower PMSD bound determined by USEPA (10'" percentile) = 12%. Upper PMSD bound determined by USEPA (90"' percentile) = 30%. CT':' Central Tendanc)' (mean Control Growth. CV, or PMSO} US EPA. 2000. Understanding and Accounting for Metttod Variabi:iry in Whole Effluent T oxicitV Applications Under 1ne Nationol l'ollutant Dischar!le Elimination Proi;ram. EPA-833-R.()0-003. US Environmental Protection Agency, Cincinnati, OH. US EPA. 200la. 200ib. Final Report: lnterlaboratory Variability Studv of EPA Short-term Chronic and Acute Wllole Effluent Tr.xicicy Test Methods, Volumes l ;md 2 Appendix. El'A-821-B-01-!){)4 and EPA-821-B*Ol*ODS. US Environmental Protection Agency, Cincinnati, OH. Page 64 of87 ~l l l - 1 1 . j .J l .J l _J
    re ~*,
    * ';3 (c c
    Page 1 of6 Potassium CJiloride Chronic Reference Toxicant Test (EPA-821-R-02-013 Method 1000.0) Species: Pimepllales pronzelas PpKCICR Test Number. 2. Dili,tioll preoaration infomimiou: Comments: KCI Stock INSS number: rNSS l"\\\\. "'\\ Stock preparation: 50.gKCl/L: .. Dissolve SO g KCl in i-L Milli-0 water. Dilution prep {mg/L) 300 450 600 750 900 1050 Stock volume (mL) 6 9 12 15 18 21 Diluent volume (mL) 994 991 988 985 98'2 979 Total volume (ml) 1000 1000 10.00 tpoo 1000 1000 Test orf!anism ilzfm:matio1~: Test information: Organism source: In-house culture Randomizing template: fv~~ Age: <24-hOurs old Incubator number and IC.. shelf location: Spawn date: oS*\\'1.,,-\\\\c> Artemia CHM number: CHM882 Hatch dates and times: <:iS* l\\o* l\\. \\\\.t)~ Dryillg i11formationfor weight lb O'i*f"M\\c 0~1-c determination: Transfer vessel information: pH= -,.~ s.u. Date I Time in oven: 6~-1..~*\\'- \\~ Tempe_rature = '"l.1..\\.6. oc Initial oven temperature: 1.oc * <- Average transfer volume: O.l749rnL Date I Time out of oven: r~.,c...11o 1:.:CO Ffaal oven temperature: loo *c.... Total drying time: 1.. '-\\,-\\.\\C '3.JL(.. Daily feetliug anti renew.at biformatiolt: D:iy Date Morning feeding Afternoon feeding Test initiation, renewal, MHSW or termination batch used Time .Analyst Time A,nnlyst Time Analyst 0 o~.,,.\\lo
    • 'as~o Vi
    \\.l...DC) M \\:,oo X{ O~.1'-\\*tlGR I C>~-\\l*° mce k \\~l'\\Q .( ll.:CO \\A CJ~*l'-l-tlc & 2 U' u ~ OS*\\'\\~\\\\. . cnqS. k1 \\'"\\()~ \\l..00 \\,/ t'l.~* l'-'*lt. p... 3 (>c;*").I)* \\ \\,;;, u* l.' U" O~\\S vi. \\'--\\, \\/':; \\of \\l..00 OS-\\l.a-1\\.. 4 u l4.\\S uj{ \\"Leo }{ ~-1..\\-1'\\o QS,\\.~ ~~ Cl~- 15Hlo F\\ 5 ..., j,,{ ~ t4 nC.1.1.*l \\. O&~D \\J 1L\\~o l"Z.JO O<;: -Id* H. A 6 }f \\"!:I"\\ s '"'?. r.\\S nc:.~ i-i.-n.. /<\\""'\\'-\\. C.... .M 6'.5.*~. \\l.o p.. 7 (1i*1,.!.\\,.Lf.- \\l u n.{)'-( \\\\ Co11trol infoJ"mation: Acceptance crilcri::i Summary of test endpoints: % Mortality: ()7 S20~'0 7-day LC50 °t\\'1.1 Average weight per initial larvae:
    o. '5.cr1 NOEC
    <.::iot'i Average weight per surviving larvae: tJ_ ~en.
    0.25 mgilarvac LOEC
    ,"2,()Q ChV < ::i.oo IC2s f.QY O ~ '1. Page 65of87 SOP AT2l -ExhibitAT2I.I, revision 11-01-14 J _ _j J J i j Oree*-!~~ - 1'(~_ : t- ;_ -..... __ t-Page 2 of6 ~ .) E=menr~l"t~s.1od=W:. Species: Pimeplzale's promelas PpKCICR TestNumber: 2 Survival a1Zd Growth Data Day Control 3.00 itig l(CIIL 450mgKCl/L A B c D E F G H: I J K L 0 10 10 10 IO lO lO ro IO 10 10 10 10 I to lO IQ IQ lf.) IO to /0 lO {() tO lO 2 10 lO lC) IQ lG l Cl LO ( C) IQ lO I() IQ 3 ID ro to ro to /0 10 10 to lO to co 4 to (0 tO 10 lO to IO {0 CD lO lQ lG 5 to lo lQ H) 1't), l~' 10 lO l () lO IC co 6 10 l\\) l()
    10.
    <D /Q 10 IQ IC 10 { () I?) 7 /fj ID IO ID f D 10 10 10 ID ID ID lO A= Pan weight (mg) L.lA-v l.n g-e~ Tray color code::. lS."L'l r~.01 1351 l?.~1 l'i.10 \\b.O~ l.b.Ll9 lS°.~1. lfo.oct 15.63 (5.~Cf lh.lb Analyst: $}W. Date: Q~-;z.~.. \\'~ B =Pan + Lar\\'ac weight (mg).. Analyst: Alb
    • IJ.O.'~), p.\\.CJ'\\ 1g.!)1 ~.S-lt Je\\."Tl ~o;o~ ~(Ml '-.O~Dq ~0.0~ It\\. f&~ 11\\.'IO Jl\\.'f}.
    Date: f)5-a~-~ C = Lanoac weight (mg)= B-A '*. . c.I.'1fs. '5.<rL s.o& s.V\\ 1.1.01. ~.a.s q.~ '-'* '1..1. s.~~ 2>-&~ '-\\.'2.l 3.ib Hand calculated. ~ Analyst: Weight per initial number of lar\\'ac (mg) = C I Initial number of lan*hc ~"b °"' :r N /:') ~~ ~ S:. Vj~ ?' ~~ ~* '1'.JrV Hand calculated. e}+ ~
    y;
    ~ '? /"j . o* o* o* '\\)' Analyst: <;:;)° ~* 0 Q Q~. o* c* o* .-\\ vcragc weight per initial :' Percent Ill u.'-\\ 7. number of lnn'ac (mg) reduction O.Scr1 Q.'-106 l'\\.8 i 0*~"~ from conrrol (%) Comment codes: c =clear, d' =dead, fg = fungus, k = ~i!led, m =missing. sk =sick, sm =unusually small, lg= unusually large, d&r = d~canted and rer:urned, w = wounded. Comme11ts: Page 66of87 SOP AT2l -Exhibit AT21. l, revision 11-01-14 l l l 1 I .1 l J .J Page3 of6 Species: Pimep/zales promelas PpKCICR Test Number: 2 Sw*vival and Gro.wtlz Data Day 60Q me-KCl/L 750 mgKCl/L 900 m~ KCl/L M_ N 0 p Q R s T u v w x 0 lO 10 IO IO 10 10 10 10 JO JO 10 10 1 (O f O to to I\\> /{) '\\'g\\ lD l ()' (0 (0 q*J.. 2 JO lO ro /\\) IQ to °\\ lO q*J... t\\ \\ <l e(J.. q 3 {O 10 - to (0 10 co q iO °\\ l'iP'I tli s'J.. 4 lO to to (0 lO '\\ to '\\ l q l tO 5 '. qil 1() IQ ID /Q IO 'l IQ .., 2.( \\,.'.,\\ '\\ 8 6 .q 1c.\\ c: \\ 1q °' 10 to lb IQ &\\ ro '° 1 7 '\\ '\\~ '1. 'i 1.J s~ 14_ lO (Q 10 \\..,. ~ (o A = Pan weight (mg) Tray color code:: UlVtndtr .,-:30 lb:~1 lbX~ t't.3\\' 1-;.c;,s '~-qq 1~~~ ISoct lt.\\-.~3 l '\\:t.1 lb."\\~ lb..;1. Analyst: 0'-4:*~~1b Date; B =Pan + Lan*ac weight (mg) 1~.&1 tlo.t.( 1lt..n 1g.r.~ Analyst: A/b )t\\~'l,. lO.,\\'
    • ~.'Al lt\\ *. 11 I'\\. I\\~ 1i.1~ lb.~~
    J'l.33 Date: 125-~S"-Hi C= Larvae weight {mg)= B-A Hand ealculatctl. j! 3.~'\\ '-\\.lo1. ~.,1 tt.sti 3.0b ~.'l.() 0*~ ~CS!) "l."llo l,..~\\ "2..l.1... t_.S\\ Analyst: Weight per initial number oflarvac (mg) = C /Initial number ofl:ln*ac 0..... 'V t:- ~ ~o 'Vt> ~p -~\\/) 1:;"' rV' ~\\.. Hand calculated. ~ ~* ~* 11:7 l".::i rv IV Analyst: o* p* 0. o* o* o* t>" o* o* t:)' 0 c* A\\'cragc weight per initial 'Percent number *or l:irvae {mg) reduction o.'-\\l S n.-~1. 0.:,11 .3'\\-5 1. o.1..'-lS S\\.11. from control (%) Comment codes: c =clear, d = dead. fg = fungus. k = killed, m = missing, sk = sick, sm = unusually small, lg = unusually large, d&r = decanted and returned, w = wounded. Comme111s: Page 67of87 ~OP A TI I -Exhibit ATil.I, revision I I-01-14 l l 1 I . l J J J ~~'"'filt;~~ r c Species: Pimeplzales promelas PpKCICR Test Number: 2. SzuviJ*al aml Growth Data Day lOSOing KCl/L y z AA BB 0 lO lO 10 10 I 10 11A ID ID 2 q'.l 0\\ t\\,J.. f"- 3 &,J. C\\ °' t\\ 4
    • ~
    Ill\\. 0\\ 1 -zJ. I 8 5 ~' 10., ~ 10\\ '-\\ l (.g {o 6 ~ s74 ~~ s
    • .\\
    7 ,~"- '1.~ l ~.....
    ~
    ~
    \\ = Pan weight (mg)
    Tray color code:: LO..vt:t'ldt.Y lS.";\\ 15,,qq \\SAl \\bSS Analyst: ~. Dale:
    • O~:t-'1.'~-110 -
    B =Pan + Lar.vac weigh! (mg} J~.Slll lb.5'0 n.fal. Analyst: Alb u;.1, Date: 115"-.lS-llt.. C =Larvae w~.igbt (mg)= ll-A Hand c.'llculatccl. o.1.& o.&S o.s'\\ \\.(l1 Annlyst: ~ Weigl!~ per initial number orlar.vac (mg) = C /Initial number of larvae ~ ~,s- ~ H:md calculat~d. 0 0
    • ~
    Q \\j Analyst: 0 0 r;;:;f A**crngc weight per: initial
    • Pcrcci:it numbc.r oflarvac (mg) reduction O~O&tJ
    &4. ~7. j from control (%) Comment codes: c = clear, d = dead, fg = f~ngus, k = killed, m = missing, sk =sick, sm = unusually small, lg = unusually large, d&r = decanted and returned, w = wounded. Comments: Page 4 of6 Page 68 of87 SOP AUf -Exhibit AT21.l,revision I l-01-14 ~**, *r** ~ I I \\ Environmental Testing Solutions, Inc, Co11ral\\ll*Uut1lmtJLKCll Control 300 450 600 750 900 1050 Ounnelt's MSO 'll;,lue1 PMSOI Rcplft1r* A ~ c D E. F G H I J ~ L M N 0 p Q R 5 T u v w x y z AA BB 11111!1lnvmbtrof Flnalnun\\buot IU1"H 111011 10 10 10 10 10 10 10 10 10 ID 10 10 10 10 10 10 10 10 10 IQ w 10 10 10 10 9 10 IQ 10 10 10 10 10 9 )O 9 lO 9 10 9 JO 6 ID G JO s lO 6 JO 2 JO 1 10 l 10 l 0.0438 a.6 A.=~1tnw.,r1hl(in1J 15,24 lG.07 13.SI IS.37* 15.70 JG.aa 16.48 15.82 16,09* JS,83 15.G9. 16,'16 16,30 16.37 16.12' 14.31 13.65 15,99 IG.49 15.09 14,53 14.27 15.44 16.52 l5.3t
    • 15.99 IS.9l 16.SS MSD*
    PMSD* Pimepha/es promelas Chronic Reference Toxicant Test EPA-821-R-02-013, Method 1000,0 Qualfty Control Verification of Data Entry, Calculations, and Statistical Analyses ft111'1ftd.HV11 l..11\\IH'Hfllhl(mtl= W*l1hl I $u~hdnt ¥itl1Mt111ll ~-A nu1nt.11afl11v.. *1in1J 20.J2 4.98 o.~98 21.09 S.02 0.502 18.59 5,08 o.soa* 20,56 S.19 o.srn 19.72 4.01. 0.402 l0.06 3.98 0.39B 20.51 4.03 0.40l 20,04 4.22 0.421.' 20.02 3.93 0.393 19,GG 3.83 0.383 19.90 4.21' OA21 19.9Z 3.76 0,376 19.99 3.G9 G.410 l.0.99 4.62 0.462 19.89 3.77 0.377 IS.Bl 4.50 0.450. 16.65 3,00 0.333 19.19 3.20 0.356 u.n 3.43 0.381 18.12 l.Ol 0.337 15.99. l.46 0.410 16.SH 2.ll 0.385 18.66 2.22 0.444 19.33
    ?.81 0.'168 15.99 o.68 0.340 16.84 0.85 0.425 16.50 0.59 0.59Q 17.62 1.07 O.l57 Minimum Si&OIJlcant 01fferenco Porcenl Minimum Significant Olfforonco Mun'llrH'l1!1l/SunMri1 (otffl.dtnl of vul.1llqn Wtltllt(lt1U11t11utnbtrol nu1ri~1rorl.1rv11 (1111l)
    IM.iu""M"'~ni.1111 l**VHCmll .. ~... i..**r1..... 1 tKI a..i~a 0..107 ~.8 a.soi 0.508 Q.519 o.~02*
    • 0.406 l.6 0.396 0.4Dl 0.422 0.393 0.393 5.0 0.383*
    0.421 0,376 0,369 0.425 9.1 0.462 0.377 D.450 0.300 0.352 6.2 0.320 0.3~3 0.303 0.246* 0.4i7 8.6 0.23! 0.222 0.281 0.058 D.428 26,7 o.oe5 0.059 0.107 Tntnu111ber: ____________ _ Test dam: _______ M_av:...1_1_*2_4;..' 2_0_1G_ M11n1u1\\IW1l(NI M11n w111Mflnlllal Co11fhtr*nl ol t1nhU11n Porc*nl udurtlon foim numb11af/1t\\IH IKI ~ntrnl '"~ (mr) 100.0 0.507 l.B Nol oppllcobl* JOO.O o.qo5 2.6 19.8 100.0 0,393 s.o 22.4 97.5 D4lS 11.6 18.2 90.0 0.317 5,2 37.S S7.5 0.245 10.6 51.7 20.0 0.080 26.S 84.3 PMSO I** measure of tesl prochlan. Th* PMSO Is !he minimum percent dllfertnai betwoon lh* con1rot 1nd uuunent 1ha1 can be dfflared sl.lllnlcallv sl1nlfi**nt In* whole olOuont lMlcltv ten. lower PM5D bound ~elermlned by'USEM (lOlh pan:ontll1J
    • 1211.
    Upper PMSD bound determlnod byOSEPA (!IOlh porcenlOeJ ~ 3°", Lowor and upper PMSO bound* woro dat.ormln*d from the lOlh *nd 901h porcenlil*, rcsp2t11vol~, ol PMSD d*I* from EPA'I WET lnlorlabor.uory Voriabllity Study (USEPA, 20Db; USE PA, 200lb). USEPI\\. 2001*, lOOlb. Final Ro port: lotorlabot~tory VarfabllltV Sludy of EPA Short*term Chronic and Acute Whole Effluent ToxltllV Toti Method" Volum01 l ond l*Appondl)(. EPA-821*&*01*004 1nd EPA*B21*B*Olo005. US Envlronmont*I P101cc!lon AJlency, Clnclnnall, Oil. Start Date: Em! Date: Sample Dale: Comments: Conc-mg/L D-Conlrol 300 450 600 750 900 1050 Conc:*m!i!/L D-Control 30() 450 600 "750
    • 900
    • rnso 5117/2016 512412016 1.0000 1.0000 1.0000 0.9000 0.9000 0.6000 0.2000 Me:tn 1,0000 1:0000 1.0000 0.9750 0.9000 0.5750 0.2000 Auxlli:i!'.l Tests 2
    1.0000 1.0000 1.0000 1.0000 0.9000 a 6000 0.2000 N-Mean 1.0000 1.0000 1.0000 0.9750 0.9000 0.5750 0.2000 Lam! Fish Growth and Survival Test-7 O:iy survival Tes! ID: PpKClCR Sample JD: REF-Ref Toxicant Lab ID: ETS-Envir. Testing SoL Sample. Type: KCL-Polassium chloride PTotocol; FWCHR-EPA-821-R-02-0*13 Tes! Species: PP-Pirnephales promelas 3 4 1.0000 1.0000 1 0000 1.0000 1.0000 1.0000 1.0000 1:0000 0.9000 o.9ooo 0.5000 0.6000 0 1000 0.3000 Transform~ Arcsin Sgu:ire Root Rank 1-Tai!od Number Mean Min
    • Max CV%
    N Sum Crill cal Rese 1..0120 1.4120 1.4120 0.000 4* 0 1.4~20 1.4120 1 :4120 0.000 4 18.00 10.00 0 1.4120 1,4120 1.4120 0.000 4 18.00 10,00 o 1.3713 1.2490 1.4120 5.942 4 16.0.0 10.00 1.2490 1.2490 1.2490 0.000 4 10.00 10.00 4 0.8609 0.7854" 0.8861 5.847 4 10.00 10.00 17 0.4572 0.3218 0.5796 23.087 4 ,o:oo 10.00 32 Statistic Critical Skew Sh2piro-Wilk's Test indicates non-normal distribution (p "'= 0.01) 0.73545 0.896 -0.. 9854 Egualil:z: or variance cannot be confirmed Hyeothesis Test f1*1ail. o.o~ NOEC LOEC ChV TU S!eel"s Many-One*"Rank Test 600 750 670.82 Treatments vs D-Control Maximum Likolihood-Probit Total Numbor 40 40 40 40 40 40 40 Kurt* 4,14077 P:;rameter Value SE 95% Fiducial Limits Control Chi-Sq Critie;il P-value Mu s*1gma ltcr Slope 12;7978.. 1.91248 9.04925 16.54S2"
    • o l.8'2817 9.48773 0.76732 2.96364 0.07814 3
    Intercept -32.928 5.54199 -43.986. -21.87 TSCR 1.0 Point Pro bits mg IL 95% Fiduci:tl limits EC01 2.674 605.149 511.556 55s:sn 0:9 fl EC05
    3.355 684.091 606.329 734.542 6.8 EC10 3.718 730.3 "*662.93. 775.211 0.7 EC15 3.964 763.229 703.338 804.683" EC20 4.158 790.455 736.489 829.706 O.&
    c EC25 4.326 814.585 765.413 652.639 &. 0.5 EC40 4.747 878.707 838.123 919.06 EC50 5.ooo. 919.688 880.08 967.024 J: 0.4 EC60 5.253 962.579 920.241 1021.8 D.3 EC75 5.674 1038.35 984.774 1127 D.2 EC80 5.842 1070.05 1010.26 1173.27 ECB5 6.036, 108.22 1040.18 1230.33 o.; EC90 6.282 1158.19 1078.42 1306.91 QO EC95 6.645 1236.42 1136.74 1430.46 EC99 7.326 1397.71 1252.89 16.97 14 10 100 1000 10000 Dos" m9/L Dose-Response Plot 09 08 .. 0.7 ~ 0.6
    i
    "' 0.5 Ci 0'1 .... 0.3 0.2 01 0 0 0 ~ ~ u 6 Page 70 of87 ...... ~.~ ( ~
    • ~-..
    Star1 Date: 511712016 End Date: 5124/2016 Sampia Date* Comments: Conc-mg/l. 0-Conlrol 300 450 600 750 900 1050 0.4980 0.4020 0.3930 0.3690 0.3000 0.2460 0.0680 2 0.5020 0.3980 0.3830 0.4620 0.3200 0.2310 0.0650 Statistical Analyses uival Fish Growth :ind Suivival lest-7 Day Growth Test ID: FpKCICR Sample l D: REF-Ref Toxicant Lab ID: ETS-Envir. Tesiing Soi. Sample Type: KCL-Potassium chloride Protocol: FWCHR-EPA-82~-R-02-013 Test Species: PP-Pimelihates promelas 3 4 0.5080 0.5190 0.4030 0.4220 0.4210 0.3760 0.3770 0.4500 0.3430 0.3030 0.2220 0.2810 0.0590 0.1070 Transform: Untr.insfojmcd 1-Tailed Isotonic Conc-mfi!/L Me:Zn N-Moan Moan .Min Max CV!.> N l-St:it Critical MSD 0-Control 0.5_068 1.0000 0.5068 0.4980 0.5190 1.804 4 '"300 0.4063 0.801'7 0.4053 0.3980 0.4220 2.539 4 5.260 2.290 0.0438 "450 0.3933 0.7750 0,3933 o.;wso 0.4210 5.026 4 5.940 2.290 0.0438 "600 0.4i45 0,8180 0.4145 ,0.3690 0.4620 11.846 4 4.628 2.290 0.0438 750 0.3165 0.6246 0.3165 0.3000 0.3430 6.237 4 soo 0.2450 0.4635 0,2450 0.2220 0.2810 10.597 4 1050 0.0798 0.1574 0.0798 0.0590 0.1070 26.489 4 A'<xiliary Tssts Statistic Criti~I Shapiro-Wilk's Tes! indicates normal distribution (p > 0.01) 0.95986 0.844 Bartlett's Test indicates egual variances {f:! = 0.03) 9.16723 11.3449 li)!f!Olhesis Test*l1 "t:ail, 0.05) NOEC *LOEC ChV TU MSDLl MSDp MSB MSE Dunnetrs Tast <300 300 0.04375 0.08634 0.01073 0.00073 Treatments vs D-Contro!
    • une:ir lntorpot:otion (200 Res;imptos)
    Point mg IL SD 95%CLjExp) Skew 1co5* 75.63 4.77 66.75 94.99 0.3228 1c10* 151.27 9.53 i33.51 189.97 0.3228 1c1s* 226.90 14.30 200.26 284:96 0.3228 1.0 IC20 353.68 ~43.72 236.32 782.57 0.0939 0.9 IC25 640.86 31 42 459.23 674.89 -2 5328 IC<:O ns.12 17.23 726.11 830.17 o.21oj 0.8 IC50 882.43 18.38. 832.BS 933,1.1. 0.1299 0.7
    • indicates IC estimate less than !he t.owesl concentration g 0.6 0.5
    ~ 04 e Cl 0.3 0 ~ 0.2 0, c 8_o.s ~ 0-4 0.3 o.z 0.1 Doso-Response Plot 0 g 500 1000 Dosem9/L 1-tail. 0.05 level of significance Mean. N-Me:an 0.5058 1.0000 0.4063 0.6017 0.4039 0.7970 0.4039 0.7970 o.3iss 0.6246 0.2450 0.4835 0.0798 0.1574 Skew l{un: 0 1319 0.30118 F-Prob df 2.5E-04
    3. 12 1500
    l ~ l l
    J
    .J J J I I "~~~ "'II 1;~{~ 'C'*, \\ EMPJtonmtt1alTcnlngS'*Uo1Uolac. Species: Pimeplzales promelas Daily Cliemisfly: Analyst Concentration Parameter pH{S.U.) DO{mg/L) Ci>nduclivit)' (µmhos/cm} CONTROL
    • Mkalinity (m~ CaCO;/L)
    • Hardness
    {mg CaCO;/L)
    • Temperature (
    0C) pH(S.U.) DO{mg/L) 300 mg KC!IL Conductivity* (µilihos/cm} *
    • Temperature (°C) pH {S.U.)
    DO{mg/L).. 450mg KCl/L Cc)nductivity (µmhos/cm}
    • Temperature ("C) pH{S.U.)
    DO(mg/L) 600mg KCl/L CO!ldUCfMl)* (µmhos/cm l
    • Temperature (°C}.
    • pH(S.U.)
    DO(mg/L) 750 mgKCl/L Conductivity {µml1os/cm)
    • T-emperature ("Cf pH(S.U.)
    DO (mg/L) 900 mgKCUL Conductivity C 11nhos/cm)
    • Tempernture (°C}
    pH(S.U.} DO(mg/L} l 050 mg KClfL Conducth*ity (µmhosfcm)
    • Temperature {0C)
    Page5 of6 PpKCICR Test Number: 2. Day erfonned H, D.O. and conductivit measurements only.) 1 2 ~ ~t /Yl L..1.\\-t
    • 1..
    Initial Final Initial Final Initial Final .. Temperatures perfom1cd at the time oftest initiation. rc11ewal or tcm1ination by the analyst identified in the Daily Renewal Information table located on Page I. .,., **.,.\\'\\ linity and hardness pcrfonncd by the analyst identified on the bench sheet sp~-cific for each analysis and transcribed to this bench sheet by: ~* F*"l~v. by 1Call-e11E.~~11a,,; Page 72 of87 SOP A T2_l - Exhibit A Til.f, revision 11-01-14 l
    • 1 l
    1 l l .1 . l J i I _J ) ~' --
    • ... _,_.-~
    ) EMllcftmtn!Jl~llll!ISd*llao"hlt. Species: Pimeplzales promelas Concentration CONTROL 300 mg KCl/L 450 mgKCUL 600mg KCl/L 750 mg KCl/L 900 mg KCl/L Analyst Parameter ,pH (S~U.) DO (mg/L) Conductivity (µmhos/crn) "AJlmlinity (mcrCaCO,;/L} "Hardness {m CaCOJILl "Temperature {°C) pH(S.U.) DO (mg/L) Conductivity (µmhos/cm) "Temperature ("C) pH{S.U.) DO {mg/L)
    • Conductivity
    {p.mhos/cm}
    • Temperature (oC}
    pH.(S.U.) DO{mg/L) Conductivity {µmhos/cm)
    • Temperature (OC) pH (S.U.)
    DO (mg/L} Conductivity C11mhoS/cm)
    • Temperature (oC) pH(S.U.}
    DO (mg/L) Conduc:thity ( mhos/cm}
    • Temperature
    ("C) pH (S.U.) DO{mg/L) Page 6 of6 PpKCICR Test Number: 2 Day {Analyst identified for each day, perfonned pH, D.O. and conductivity measurements only.) 3 4 5 6 J OSO mg KCl/L Conductivity ~{~w~n~lm~s~k~mL>~~-t-=::..:_-=-~~~~~~2:.l-~~~--J}~2:22::::.:c2.l_J:::.!.:::::.:::~[j.'2..~~L:S:j_:=..!.~~~I-_:_~-*~*~*-~**~*
    • Temperature (oC)
    Initial Final 1$.0 Initial Final t..~-D Initial Final Initial Final "'""""fem craturcs performed at the* time of test initiation, *renewal or tem1ination by the analyst identified in lhc Daily Re newel lnfom1ation table located on Page I. "'".. '"A'.lkali ity and hardness performed by the analyst identified* on the*bench sheet specific for each analysis and transcribed to this bcncll sheet by: -.:@ ~ Page 73 Of 87 SOPAT21-ExhibitAT2LI, rev~n ll-01-14 Ceriodaphnia dttbia Chronic Reference Toxicant Control Chart
    *....-J
    / \\ Environmental Testing Solutions, Inc. 0 u ~ z ...:J OJ> -- II) N u -
    i...
    Cl:! "O I t-1.14 Li2 l.10 . 1.08 1.06 l.04 1.02 2.5 2.0 1.5 LO 0.5 l.4 1.3 l.2 I.I 1.0 0.9 0.8 USEPA Control Limits (+/- 2 Standard Deviations)
                                                                                                                            • ~*******************~*** ************
      • ~*~*****~*-**************************
    USEPA Warning and Cont;J*ol Limits*(75th and 901h Percentile CVs)
                  • ~***************************************************************************************
    -* -**-*1-* -**-**- *-.. *-*0......:....1,*-*1- *-*T-:-**- *--*-**- *- *- Lab9ratory Warning and Control Limits (1 d 11and251b Percentile CVs)
                                                                                                  • ~***********************************************
    ___ _}_ - -
                  • ~*********************************~***********************************~***************,
    Test date 7-day IC25 = 25% in_!1-ibition concentration. An estimation of the concentration of sodiun1 chloride that would cause a 25% reduction in Ceriodaphnia reproduction for the test population. CentraJ Tendency (mean IC25) Warning Limits (mean IC25 +/-SA.JO or SA.75) Control Limits (mean IC25 +/- S A.25, S A.90, or 2 Standard Deviations) Page 74of87 \\ Environmental Testing Solutlons, Inc. Testnumbor 9 10 11 12 13 1~ 15 16 17 18 19 7.0 Test date 12*02-14 OJ.13*15 02*03-15 Ol-03*15 04-07*15 OS*OS-l S 06*09*lS 07'14*15 08*04-15 09-15-lS 10*06*15 11*03-15 12-08-JS 0!-l2*16 02*09*16 02-09*16 03*08-16 04*05*16 04-05*16 05*10-16 7-day JC,. {g/l NaCl) l,08 1.06 1.07 1.06 t.06 1.Q7 1.08 1.06 1.0~ 1.07 1.06 l.07 l.07 1.05 1.06 l.06 1.07 1.07 1.06 l.06 CT (g/L NaCl) 1.06 1.06 1.06 1.06 1.06 l.06 1.06 1.07 1.07 l.07 1.07 1.07 1.07 1.07 1.o7 1.07 1.07 l.07 1.07 1.07 s 0.01 O.ot 0.01 O,QI 0.ol 0.01 om 0.01 0.01 0.01 0.01 0.01 0.01 0.01 0.01 0.01 o.m 0.aJ O.ot 0.01 Ceriodaphnia dubia Chronic Reference Toxicant Control Chart Stat~ and USEPA control Umlls CT*2S CT+:!.S 1-04 l.04 1.04 1,04 1.04 1.05 1.04 1.05 1.05 1.05 1.os 1,05 1.os 1,05 1.05 1.0S 1.05 1.0S I.OS l,05 1.08 1.08 1.08 1.oa 1.oe 1.08 1.08 l.08 1.08 1.08 I.OB 1.08 1.oa 1.08 I.OB I.OB l.08 1.08 1.08 l.08 0.09 0.09 0.09 0.09 0.09 0.09 0.09 0,09 0.09 0.09 0,09 0.09 0.09 0.09 0.09 0.09 0.09 0.09 0.09 0.09 Laboratory Warning llmll* CT
    • s._,.
    Cl + S*.** 0.98 0,98 0.98 0,98 0.98 o.98 0.98 0,98 0.98 0.98 0.98 0.98 0.98 0.98 0.98 0.98 0.98 0.98 MB 0.98 1.15 l.lS 1.15 1.15 1.15 1.15 l.JS 1.15 1.15 l.lS .l.15 us 1.15 1.15 t.15 1-15 1.15 1.15 1.15 l.15 0.18 0.18 0,18 0,18 0.18 0.18 0.18 0.18 0.18 0.18 0.18 0.18 0.18 0.18 0.18 0.18 0.18 0.18 0.18 0.1.a Laboratory control LlmltJ S"- cr-s~ cr+S1.1s o.88 0.88 0.88 0.88 0.88 0.88 0.88 0.88 0.88 0.88 0.88 0.89 0.89 0.89 0.89 0.89 0.89 0,88 0.88 0,88 1.24 1.24 1.24 U4 1,24 1.2s 1.25 1,25 l.25 1.25 1.25 1,25 l.2S 1.2s . 1.25 l.25 1.25 1.15 1.25 1.25 0.48 0.48 0.48 o.48 0,48 0,48 0.48 0.48 0.48 0.48 0.48 0.48 0.48 o.48 0.48 0.48 0.48 0.48 0.48 Q.48 USEPA Warning Limits CT*S._n o.sa o;sa 0.59 o.S9 0.59 0.59 0.59 0,59 0.59 0.59 0.59 0;59 0.59 0.59 o.~9 0.59 0.59 o.ss o.59 0,59 1.Sd 1.54 1.54 1.54 1.54 1.54 l.54 1.54 1.SS 1.55 !.S4 1.55 1.5S 1.55 1,55 1.55 1.55 1.55 1.55 1,54 0.66 0.66 0.66 0.66. 0.66 0.66 0.66 0.66 0.66 0.66 0.66 0.65 0.66 0.66 0.66 0.66 0.66 0.66 0.66 0.66 /\\/ote: 7*d IC,.* 7*dav 2S~ inhibition concentration. An ulimalion of the concentration of sodium chloride that would cause a 25% raduction In Cerlodaphnlo reproduction for the te~I papulatlan. CT~ Centr~I tendency (rneon JC,.). S ~Standard deviathm Mtho IC1, values, laboroiory Control and Warning Limits USE PA Control limits cr-s..,. cr+s..,. 0.40 0.40 o.40 0.40 0.40 0.40 0.40 0.40 0,40 0.41 0.40 0.41 o.41 0.41 0,41 0.41 ll.41 0,41 0.40 0.40 1.72. 1.n l.72 1.72 1.72 1.72 1.72 1.73 1.73 1.73 1.73 1.7! 1.73 1.73 1-73 1.13 1.73 1.73 1.73 1.73 t*horatory control and warning lirn1ts were established using the sr~ndard deviation or tho IC,, values corro~ponding to the 10th ond 25th percentile CVs. The~e,.nges are more stringent than the tontrol ond w~rn111g l11111ts rncommcnded by USEPA lor the test method nnd endpoint. SA.lo* Standard deviation corresponding to lhc io" porcenule CV. (S.,0= 0.08) s._" = Standard deviation correspQndlng lo the 2Slh percentile CV. (s,,, = D.17) USEPA Comrol and Warning Lim!~ s,.,, = Standard deviation corresponding to the 75 1 ~ percentile CV. (s.,.~ 0.45) s..,0 = Standard deviation corresponding lo the 90 1~ percentile CV. (s.,0 = 0.62) ~ = Coefficient of variation or the !Cu values. US EPA. 2000. Und*rstond1ng and Accoununc lor Methon Variab11itv Jn Whol~ Elfluenl Toxicity Applioallons Under lh~ N~llonal Pollutant Oiscl!orgn Ehmln*llon Program. EPA*B33-R-00*003. Us Environmental Protection A!ency, cinclnnatl, OH. OI 0.01 0.01 o.oi O.Ol o.oi 0.01 0.01 O.Ql 0.01 0.01 0.01 0.01 0.01 D.01 0.01 0.01 0.01 O.Ql o.oi O.Dl Cl ,{f!C:~ Ceriod(tplutilt ditbia ) Environmental Testing Solutions. Inc. Chronic Reference Toxicant Control Chart Precision of Endpoint Measurements /' = 0 - +: d.l t) ei::I =... "C = 9~ Q. O{I d.l c 0:: --s.. 0 Q.. s.. ~ - = 0 0 - u 35
                                                                                              • ~**************************************~****
    30 25 20 15 Minimum Acceptance Criteria(> 15.0 offspring per surviving female) 40 Nortl1 Carolina Acceptance Limit(< 40.0%) 30 Kentucky Acceptance Limit(< 30.0%) 20 10 50
    • --* ~--~**~**-* -***-**.:...._**-**-**-**!"""- ---*-
      • -*---**-~~-**-**__..:,**-*... _,, __ -**-**-**-
    USEPA Upper PMSD Bound (90 111 percentile<47.0%) 40 IO 0 ~~~~~~~~~~~~~~~~~~~~ , \\,..\\\\ ~v' ~i.-"'. ~~-~- ~r,.,Jj \\\\;-i;s ~,,/~ \\)1*" ~<r.- ~c,- ,~- )v '-,.. ~v" \\)1.' ~,_.. .~Y, \\\\" ~tv ~r,- Test date Control Repr-oduction, Coefficient of Variation (CV), or Percent Minimum Significant Difference (PMSD) PMSD is the minimum significant difference between the control and treatment that can be declared statistically significant. Central Tendency (mean Control Reproduction, CV, or PMSD) Control Limits (mean Control Reproduction. CV~ or PMSD +/- 2 Standard Deviations) Page 76* of 87 0 Precision of Endpoint Measurements Ceriodaphnia dubia l *- Chronic Reference Toxicant Data \\ Environmental Testing Solutions, Inc. Test number 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 Note: Testdate Control Control Mean CT. OJ MSD Survival Reproduction CT PMSD CT for Control Mean for Control {%) (offspring/female) Reproduction (%) Reproduction (%) forPMSD(%) (offspring/female) CV(%) 12-02-14 100 33.1 6.4 2.0 6.2 01-13-15 100 32.7 32.9 3.8 5.1 1.8 5.6 5.9 02-03-15 100 32.5 32.8 3.9 4.7 1.8 5.6 5.8 03-03-15 100 32.4 32.7 6.0 5.1 1.9 5.8 5.8 04-07-15 100 32.3 32.6 4.6 5.0 1.8 5.5 5.7 05-05-15 100 31.7 32.5 5.6 5.1 1.8 5.8 5.7 06-09-15 100 29.7 32.1 2.8 4.7 1.4 4.8 5.6 07-14-15 100 30.8 31.9 3.0 4.5 1.5 4.8 5.5 08-04-15 100 31.0 31.8 3.0 4.4 1.6 5.0 5.5 09-15-15 100 29.4 31.6 4.0 4.3 1.7 5.9 s.s 10-06-15 100 29.6 31.4 4.8 4.4 1.8 6.1 5.6 11-03-15 100 31.7 31.4 6.5 4.5 2.2 6.9 5.7 12-08-15 100 30.6 31.3 4.9 4.6 1.9 6.3 5.7 01-12-16 100 31.2 31.3 3.3 4.5 1.4 4.4 5.6 02-09-16 .100 31.6 31.4 7.0 4.7 2.0 6.3 5.7 02-09-16 100 32.0 31.4 S.9 4.7 1.£ 5.1 5.6 03-08-16 100 29.4 31.3 5.4 4.8 1.7 5.9 5.6 04-05-16 100 29.3 31.2 6.0 4.8 1.8 6.1 5.7 04-05-16 100 32.3 31.2 4.9 4.8 1.7 5.2 5.7 05-10-16 100 31.6 31.2 5.0 4.8 1.6 5.2 5.6 OJ = Coefficient of variation for control reproduction. lllwer CV bound determined by USEPA {10"' perceritile),, 8.9%. Upper CV bound determined by USEPA (90 1 ~ percentile) = 42% MSD,, Minimum Significant Difference PMSD = Percent Minimum Significant Difference PMSD is a measure of test precision. The PMSO is the minimum percent difference between the control and treatment that i:an be declared statistical Iv significant in a whole effluent toxicity test. Lower PMSD bound determ.ined by USEPA {10'" percentlle),, 13%. Upper PMSD bound determined by USEPA (90'" percentile)= 47%. CT= Central Tendancy (Mean Control Reproduction, CV. or PMSD) USEPA. 2000. Understanding and Accounting For Method Variability in Whole Effluent Toxicity Applications Under the National Pollutant Discharge Elimination Program. EPA-833-R-00-003. US Environmental Protection Ageney, Cincinnati, OH. USEPA. 2001a, 2001b. Final Report: lnterlaboratory Variability Study of EPA Short-term Chronic and Acute Who!e Effluent Toxicity Test Methods. Volumes 1and2-Appendix. EPA-821-6-01*004 and EPA-821-B-Ol-OOS-US Environmental Protection Agency, Cincinnati, OH. Page 77of87 l l 1 Sodium Chloride Chronic Reference Toxicant Test (EPA.,.821-R-02-013 Method 1002.0) Species: Ceriodaplinia dubia Page I of6 CdNaCICR #: 188 Dilution preparation illformation: Conune11ts: NaCl Stock !NSS number. INSS \\'-\\"\\\\.. Stock preparation: ' IOOgNaCllL: Dissolve 50 g NaCl in 500 mL Milli-Q wai.cr. Dilution preo (mg/L} 600 800 1000 1200 f400 Stock volume (mL) ** 9 12 15 18 21 Diluent volume (mL) 1491 1488 1485 1482 !479 Total volume (mL} *. 1500 1500 1500 1500 1500 Test Orf(lllliSlil source i11formatio11: Test illformatio11: Organism age: I < 24-hours old Randomizing template color: fl.P~ Date and times org~nisms were born I 0-:.-1-0-L\\o 01.~o*o C>'\\~o Incubator number and shelfi between: location: t..&\\ Culture board: O'S-U"":.-\\\\. A Replicate number: I _2 I 3 I 4 I s I 6 I 7 : I s I 9 I 10. YWTbatch: Culture board cup numb~r: " "1 lio I t\\ I r2..l lc;.l l~ 1~11.lol"?..1: os-n-11,c, T ransfor vessel infommtion: oH=;: SL\\ S.U. Temperature= -is.\\ °C Selenaslntm batch: ~.'Z1--ft.. Average transfer volume (mL): 0.0121 mL Daily renew~! information: Da,y Date Test initiation and feeding, MHSW AnaI):st ren.ewal and feeding, or batch used terminatio.JI time 0 05-10-16 oS:.*08-lb -I 05-11-16 oSd:1\\-\\l.o A 2 05-12-16 3 05-13-16 4 05-14-16 ) 05-15-16 (> 05-16-16 7 05-17-16 Control infor11iatio11: Acceptance criteria Summary of test eudpoillts: % of Male Adult~:
    01.
    520% 7-day LC5u >1~0\\l 0.10 Adults having 3rd Broods: 1001.
    <:80%
    NOEC JLN.I % Mortality: r\\1. s20~~ LOEC J l"ll'l 0 Mean Offspring/Female: _._,,.lo ~ I 5.0 on:~pringlfernale ChV ~~-1. '-I %CV:
    s. 07-
    <=40.0% IC25 1ot.o. '5 Page 78 of87 SOP ATl4-Exhibit AT14. l, revision l l-01-14
    1.
    I I I I I I I I
    re-rr I
    ,* ~*,, -~~. ~*ti.uw.&111~~*~ Species: Ceriodaplmia dubia CONTROL Day I I Young produced 0 Adult mortality \\._ 2 Young produced D Adult mortality \\ - 3 Young produced 0 Adult mortality \\_ 4 Young produced -....\\ Adult mortality' \\_ 5 Young produced \\. "!l Adult mort:llity G Young produced ('\\ Adult mortality L.. 7 Young pro'duccd l-\\ Total young prod11ccd 3,-.\\ Final Adult Mortality \\c_ X Jor 3rd Broods x.:.._ 2 D \\._ D \\...- 0 L \\...\\ \\__ \\' 0 \\_ \\.:::, ~,.. I,,_ }(.. Page2 of6 CdNaCICR #: 188 Si1rvival and Reproductioll Data Replicate number 3 4 5 6 7 8 9 10 0 0 0 0 0 0 0 {) \\._ \\.._. L-0 ('.) n (") 0 0 (") 0 \\._ L L- \\._ \\.._ L L L.. 0 () f"J 0 0 0 0 0 L L \\.._ L.. L '-.\\. ~ '-\\ ~ ~ '-\\ ~ ""' \\;_ L L \\_ L. ~ \\-Z.. \\'~ q_ \\D \\\\ \\\\ \\~ \\""'L \\_ '- L L L 0 (\\ () 0 ('., n u 0i L. L \\.__ \\._ \\.._. \\"" \\~ \\s l& \\.S \\~ l:\\ \\\\o ~,_ ~"L b\\ ~' "'L'\\ ~o ~'-\\ ~\\ \\_. \\___ '- L- \\ )<. ")(. 'K ~ "><._
    K.
    ~ -,.c-Nore: Adu II mortality (L = hve. D =dead); SB = spltt brood (smgfe, brood split between two days), CO= carry over (offspring carried over with adult during transfe1'). Concentration: % Mortality: I
    07.
    Mean Offspring/Female: I 3\\.\\c 600 mg NaCl/L Sun1i_val and Reprod11cti01l Data Rcnlicate number Day I
    2.
    3.
    4 5 G 7 8 9 10 l Young produced 0 n (') () 0 0 0 n a () Adult mortality '\\._ '-- \\.._ L L \\.._ '- L- \\.... 2 Young.produced 0 C) 0 0 0 D 0 0 0 0 Adult mortality \\__ L L L L \\._ L L L L 3 Young produced () () n
    0.
    (\\ 0 0 () 0 D Adult mortality L L \\_ '-- L. \\_. L L_ G-L 4 , Young produced s '-{ \\;.\\ '-\\: s '-l -:z... ~."\\ ~ Adult mortality \\_ L L \\.._. L_ L L-c_ L_ 5 Young produced \\L. \\I... \\~ \\~ \\(_ \\~ I l \\'"L \\L_ \\ \\ Adult mortality \\._ \\._ L. '--- \\..._ '- L \\_ L L 6 Young produced ("\\ a 0 0 0 0 0 () t'i 0 Adult mortality L \\_ L L L L L L L L 7 Young produced \\k \\\\a \\ 'S \\\\ \\ 'S. \\'-\\ \\ &' \\cs.,, \\\\ Total young produced
    £
    ~2 ~'L ~"\\ ~'- .:=, \\ ~"'L ~o ~'- ~\\ Filial Adult Mortality L L L L L \\.._. L-L Note: Adult mortality (L =live, D =dead); SB= split brood tsmgk brood spill between two d3ys), CO= carry over (offspring
    • arried over with adult during tnmsfi:r).
    Conce11tration: % Mortality: lll. Mean Offspring/female: 32.. \\ % Reduction from Control: -\\.lo1. Page 79 of87 SOP AT14 - Exhibit ATI4.1, revision 11-01-14 Page 3 of6 Species: Ceriodap/mia dubia CdNaCICR #: 188 800 mg NaCl/L Survbial and Repl'oduction Data Replitate.number Day l 2 3 4 5 6 7 8 9 IO I Young produced
    • r-.
    A D 0 (\\ o* 0 Q 0 - (") Adult mortality 'L-L-* \\.__ \\..:.._ - \\_. '-- 2 Young produced () (J n 0 () 0 () 0 C) 0 Adult mortality L \\...._ \\_. '(__ L-L L-L-3 Young produced 0 a 0 0 0 ri b (') (") C> Adult mortality \\.._ '-- \\..,_,,. "\\._ '- 4 Young produced '-\\ ~- ~ ~.s ....x '-\\ ".\\ '-\\ ~ Adult mcirtallty \\. \\.:.-- L-L 5 Young produced \\!_ \\ \\. l '-\\ -- \\L. \\\\ \\L_ \\ 1.. \\~ \\,"?:I \\~ Adult mrirtalicy. \\.__ '- "\\._ \\;;... l 6 Young pr:!>duced (') {'J 0
    (J a
    0 {) a 0 0 Adult mortality L \\...;___ L \\._ -~ _, L ~ i Young produced \\..J,. \\\\ llo,., \\S \\~ \\ \\o \\S -- \\c \\S Total young produce(!
    0 "31\\
    ~~
    ,'1,..
    ~\\ ,..G\\
    • ~:iL
    ~\\ 2>t> '.?>\\ Final Adult.Mortality* \\_ '.\\,.__ \\._, \\_. '-- \\..,-- ': L-- \\. No1e: Adult mortahty' (L = hve, D =dead). SB_= sphtbrood (single-brood sphtbetween two days),'CO =carry o~er(offspring carried over with adult during transfer).. CollcelltrutioJZ: % Mortality: ll1. Mean OffspringfFemale: ~ % Reduction froip Control: ~*"a~, 1000 mg NaCl/L S1m1iv.al aml.Reprotluctioll Data Replicate-number. Day 1 2 3 4
    5.
    6 7 8 -9 10 I Young pr_oduced n CJ n -{j ('") () 0 () 'C) 0 Adult mortalit)* '\\.____ L \\._ L L L \\...._ 2 Young produced u ('.) D 0 O* D n D 0 0 Adult mortality ~ \\_ L \\._ L L.:: L-3 Young prpduced 0 D u 0 D
    0. 0
    -o. '-0 0 Adult mQ,rtalitY L L L-- \\_ '- ~ '--- \\_ L 4 Young pr~duci;d 3.. b '4 ~- "-\\ _ ~* q ~- ~ _, Adult mortality \\ L \\_ \\._ L 5 Young produced \\""L \\ t) \\0 l t) \\i_ \\~ l't) n l\\ I\\ A_dult mo*rtality L- \\._. \\_ \\._ L \\.._* L L L 6 Young pi;oduced 0 0 0 0 0 0 0 a D u Adult rnQrlality L .\\.....- L \\._ \\_ ~ \\._ \\_.. L L. 7 Young produced \\ L.\\ \\ '-'\\ ,c; \\\\ '?--.. \\\\c I'-\\ \\'-\\ ,~- \\lo Total young produced '-~ -i:.1 L..~ L..<::\\ -o::. "21(; £..& 2.1 30 final Adult Mortality L .L L L l \\..__ L Now: Adult monahty (L = !iv!!. D = dead), SB =split brood {single brood sp!il between two days), CO = carry over (offspring C3rried over wiU1 adult-during transfer), Co11centratio11: % Mmtality: Mean Offsf)ring/Female: % Reduction !Tom Control: Page 80 of87 SOP A Tl4 - Exhibit ATI4. l, revision l 1~01-14
    r=T*~
    ~*-,,; Page 4 of6 Species: Ceriodaolmia diihia CdNaCICR #: 188 1200 N Cl/L me: a S . al dR - IUl'lV an d uct1011 epro D t aa R~piicate number Day I 2 3 4 5 6 7 8 9 10 I Young proauccd-() .fl
    • ("")
    () 0 0 f) () ('"') ('s Adult l'l!orti!lity \\...._ \\_.., '-- \\.,_ L- '-- \\..__ \\__.. 2 Young produced ("} h (} ri 0 0 0 0 [") n Adult mortality c -\\._ \\.:.. L L-* L L \\ l 3 Young produced D a D ('\\. -"D -~ a a ("") (} Adult l'llortality \\..._ \\._ \\.__. \\.._ \\..- \\...- \\,_ \\,_ \\.__ 4 Young produced ~ "h -~ ~ I..\\ L_ '4 ~ Adult mortality \\,,.....-- \\_ \\...... \\._ '- \\......_ \\,__ ~ 5 Young produced \\.., i_ s., '-\\ L_ lo "' Adult mortality \\_., Le*- '- L \\._ L \\..._ L 6 Young produced. 6 t), 0 0 () 0 f"I 0 0 (') Adult inonality \\._...' "\\..., \\_ \\..- \\_ '-- \\_. \\_... \\.. 7 Young produced s
    • 5
    \\. i.:\\ 0 s \\ \\ '..\\ Total young produced \\~. \\\\ to l'-\\ g \\S \\S \\\\ \\.~ \\\\ Final Adult i\\'lortaiity L... \\...,... L \\......... \\......... \\. Note: Adultmortahty (L = hve, D =dead}, SS-= spin brood (smglebrood sphtbetween two days), CO= carry over (offspnng carried over with adult during transfer). Concentratioll: _ % Mortality: '""7. Mean Offspring/Female: - -* I.I.* ~ \\""2.\\ % Reditction.frpm Control: ~ fo \\.11. 1400 mgNaCl/L
    • Survival alld Reproduction Data
    -Replicate number Day I 2' 3 4 5 6 7 8 9 10 I Young produced_ 0 D {) 0 0 0 ('\\ 0 0 (") Adult. mortality L...: L L,. L._ '-- \\.._ \\,__ \\._ 2 Young pr9duced 0 0 --- 0 [J {")_ {) {)_ (") 0 {) Adi11t mott:ility \\_ L.. \\...._ L L L L \\..__ l_ 3 \\'oung.proQuccd _O
    0.
    ' 0 ("\\ [) 0 0 0 0 {) Adult mortalii)' \\..;..- x._ \\.__ 'L.. \\_ '-- \\._ L 4 Young produced' \\. ~ '\\ b \\ \\ D.,_ 0 Adult m9rtality \\.. - \\_ \\.....- \\_.. \\.__ L.. L \\.... L L 5 Young pr:ociuc~d. L -L.. 6 D ~ ~ ~ ' ~ I Adult mortality L.. \\._ \\_ \\.__ - \\..- L.. L L. L \\_ 6 Young P,roduced Q c ~ \\ a () () 0 () {) Adult mortality L L \\...... L L L L L 7 Young produced 0 L.... b 0 \\ \\ 0 0 0 0 Total young produced 3 lo '-\\ L\\ s
    s.
    ~ ~ ~ ~ I Final Adult Morlality L-. '- \\._.. L L. \\_.. L Note: Adult mortality (L = hve, D =dead}. SB= split brood (smgte brood splil between two days), CCI= carry 01*er (offspring carried over with adul! during 1ransfer). Concentration: I % Mortality:
    07.
    Mean Offspring/Female: i.f. 0 % Reduction from Control: .s1. ~1-I Page 81 of87 SOP ATI4-ExhibitAT14.l, revision l l-01-14 i CD ~ 0.... Cb "I_ r.. 1 __ - J Environmental Testing Solutions, Inc. Control Day ., __ Jlcplicntc numhcr I 2 J 4 5 6 7 I 0 0 0 -
    0.
    ' 0 - -.() 2 () () () 0 0 0 0 3 () 0 0 0 O* 0 0 4 4 4 4 3 4 3 3 s 13 13 '_ 12 13 -
    • 12
    . IO II 6 !l 0 0 0 0 0 0 7 17 15 16 16 15 18
    15.
    '1'01111 J4 32 32 32 31 31 29 600 mg NaCl/L Dny Hc11licntc**n11111bc1; I 2 3 4 5 6 7 I 0 0 0 0 () 0 .0 2 0 0 0 0 0 O' 0 3 0 0 0 0 0 o* *o 4 4 4 4 5
    -i -
    J 5 12 12 13 13 12 13-II 6 0 0 () 0 0 o,* 0 7 _I!; 16 15 17 15 14* JS Tolnl 35 32 32 .J4 32 ,JJ 3.2 800 mg NaCl/L ~ l>ny Rciillcntc number I 2 .l 4 5 6 7 I - 0 0 0 0 0 0 0 2 () 0 0 0 0 0 0 J () 0 0 () 0 - 0 0 4 3 3,:i -4 4,, 5 -12 ll 14 - 12 II 12 12 6 () 0 0 0 -
    0.
    0 0 7 l.J 17 16 17 15 - 13 16_ Tnlnl JO 31 33 J:Z JI 29 32 Verification of Ceriot/1tpl111ia Reproduction Totals 1000 mg NaCI/L -rrotnl 8 _9 10 --- Dny -- - Reolicntc number T11t11l I 2 3 4 5 6 7 8 9: JO 0 -0.. : O_, 0 I 0 0 0-0 0 0 0 0 0 0 0 () 0 () 0 2 0 0 0 Cl 0 0 0 0 0 0 0 0 () () 0 J 0 0 0 0 0 - () 0 0 0 0 0 4 4 3 J6 4 3 3 4 3 4 4 4 J J 3 34 II l3
    • 12 120 5
    12 ro IO IO 12 13 IO II 11 II 110 0 0 0 0 6 0 0 0 0 0 0 0 0 0 0 0 15
    17.
    16 160 7 1.4 14 15 17 13 16 14 14 1,3 16 l11G 30 34 JI .Jl.6 T11tnl 29 27 29 Jo* 29' 33 211 28 21*: JO 290 1200 mg NaCl/L TQtnl
    • 8 9
    10 D11y Re llic1itc.1111111bcr Totnl I 2 J 4 -5 6 7 II 9 JO. 0 0 0 0 .I 0 0 () () () () 0 {l 0 0 () 0 0 - o*
    o
    -2 '0 - - 0 1(). 0 'O - 0 0 {l -o 0 () o* 0 0 0 3_ 0 0 (I 0 0 '() () 0 0 0 0 3 3 3 38 4 J 3 3 2' J
    '.l 4
    2 4 3 30 12 12 - II
    121 5
    5 3
    -.6 - _8 5 7 4 2 6 4_: 50 0 0 -0 0 '6 0 iJ () 0 o_ 0 0 0 ff 0 0 15 17 1:7 162 7 5 s I 4 0 5- '7 7 3 4 - 41 -JO 32 31 321 T1!fal 13 II IO 14' -'8 15 15 ll l3 u 121 1400 mg NaCI/L Tollll 8 9 Ill Dny Rimile1ifo nnmb~r Toinl I 2 J 4 5 *- 6 7 8 ~ IO. 0 0 0 0
    r 0
    0 - 0 0 - 0 0 () - 0 () 0
    • o 0
    0 ; () 0: 2 .o
    • o -
    I) () 0 0 () 0 (l () () 0 ff 0 0 3 0 0 0 CJ 0 0 0 0 0 0 - 0 4_,_ -4 __, 3 37 A.,. I
    2.
    1 ' 3 - 2 I I 0 2 0 13 12 13 - IJ 1_22 5 2 2 0 0 .2 - 3 3 j I 3 19 0 0 0 () 6 0 0 3 r 0 0 0 0 0 Cl 4 15 - 13 15 151 7 0 2 0 0 I I 0 0 0 0 4 JI JO 31 310 Totnl 3 Ci 4 4 5 5 4 J J 3 40 -/: '~F" ) E:nvlronmental Testing Solutions, Inc. C1111cc111r111ii111 (111g/LNnCI) I 2 J C11111rol 34 32 32 600 35 32 32 81111 30 31 33 IUOO 29 27 29 12110 IJ II JO 1400 3 6 4 DunncU's MSD \\*nluc: 1.636 PMSD: 5.2 Ceriotlaplmia d11hi11 Chronic Reference Toxicant Test EPA-821-R-02-013, Method 1002.0 Quality Control Verification or Data Entry, Calculations, and Statistical Analyses 32 34 32 30 14 4 MSD= PMSD= Tesl number: CdN11CICR IH88. ...;......~~~ Test d111cs: _______ i\\_*1-'n~=-* _10_-_11_.._2_0 _16 Rc111icatc munllcl' Slll'\\*h*nl 1~vc1*agc l'c11roduciiim Cocrlidcnc or l'orcc1111*cd11cllon from s 6 7 8 9 IU (%) (offspring/fcmnlc) v*irintlon. ('~) con1rol (%) 31 31 29 30 34 JI JOO Jl.6 5.0 Not 11pplic11blc 32 JI 32 JO 32 JI
    • JOO 32.l 4.5
    -1.6 31 29 32 31 30 31 JOO Jl,0 J.7* 1.9 29 33 28 28 27 30 100* 29.0 6.1 8'1 8 15 15 11 13 II 100 12.1 18.9 61.7 5
    s 4
    3 3 3 1011 4.0 26.4 87.J Minimum Slgnl!icnnt Diflcrcncc Percent Minimum Signilicnnt DilTcrencc PMSU is u measure oftcstprccisinn. The PMSD is the minimmn 11crcc11L difference between the conlrol nnd lrcntnnm! lhal c1111 be declared stnlistically signifiumll in U Whole CfnllClll to:dc(ly lCSl. Lower PMSD bound determined by USEPA (I 0 11' percentile) = 13%. Upper PMSD bound dctcnnmcd by USE.PA (90111 p~rco111ilo) =- 47%. Lower und uppor PMSD bounds were daterinined from the I 0th nnd 90th pcrccnlihi. respectively, ur PMSD dntn from ~PA's WET lnlerlaborntory
    • Variability Study (USEPA, 2001 n: US GPA. 200 I b).
    USEl'A. 2001a. 2001 b. Final Report; lnlarlnborntory Variability.liludy ofGPA.'ihorl*lcrm Chronic and Acme Whole El'Oucnl Toxicity Test Mcl11ods. Volum~s I nnd 2-AppcndiN. EPA*821*B-01-004 nnd EPA-821-B*Ol*005. \\JS Envirnnoiontnl Pmlcction Af.1ency, C'incinnnti, OJ I. Statistical Analyses Cerlodaphnia Survival and Reprodilction:Test-Reproduction Star1 Date: 5/10/2016 Test ID: CdNaCICR Sample ID: End Date: 5/1712016 Lab ID: ETS-Envir. Testing Sol. Sample Type: Sample Date: Protocol: FWCHR-EPA-821-R-02-013 Test species: Comments: Conc-mg/L 1 2 3 4 5 6 7 a 0-Control 34.000 32000 32.000 32.000 31.000 31.000 29;000 30.000 600 35.000 32.000 32.000 34.000 32.000 31.000 32.000 30.000 800 30.000 31.000 33.000 32.000 31.000 29,000 32.000 31.000 1000 29.000 27.000 29.000 30,000 29,000 33.000 26.000 28.QOO 1200 13.000 11.000 10.000 14.000 B.000 15.000 15:000 g,ooo 1400 3.000 6.000 4.000 4.000 5.000 5.000 4.000 3.000
    • Transform: Untransformed Rarik Conc-m2/L Mean N-Mean Mean Min Max CV%
    N Sum D-Conlrol 31.600 1.ooao 31.600 29_000 34.000 4.992 10 600 32.100 i.0158 32.100 30.000 35.000 4.514 10 115.00 800 31.000 0.9810 31.000 29.000 33.000 3.725 10 93.50
    • 1000 29.000 0.9177 29.000 27.000 33.000 6,082 10 67.50
    • 1200 12.100 0.3829 12.100 8.000 15.000 18.866 10 55.00
    • 1400 4.000 0.1266 4.000 3.000 S.000 26.352 10 55.00 Auxilia!}'. Tests Statistic Kolmogorov D Test indicates non-normal distribution (p <- 0.01) 1.17686 Bartlett's Test indicates egual variances !E =- 0.22}
    6.9511 H}'f20thesisTest {1~tail, Q.05) Steel's Many-One Rank T~st Treatments vs D-Con!ro! Point mg/L SD ICOS 874"25 46.1457 IC10 1oois6 19.8204 IC15 1022.81 6.13206 IC20 1041.66 5,78404 IC25 1060.5 5;5587 IC40 111'(04 5.72513 IC50 1154,73 6.47952 4{) 35 30 .g 25
    > -e 20
    c.
    ., 15 a: 10 5 0 0 ~ 0 u 6 Page 84of87 NOEC LOEC ChV TU 800 1000 894.427 Linear lnterpolatfon 1200 Resamp!e~} 95%CL Skew 177.109" 977.261 0.1342 942.55:2 1015.95 -1.7201 1010.05 1033.73 0.0494 1029.75 1053.49 0.0998 1049.71 1071.74.0.1484 1106.83 1129,22 0.2907 1142..84 1166.94 0.3819 c 0 c.., a: 1.0 Q.9 0;8 o.7 0,6 0.5 0:4 0.3 0.2 0.1 0.() -0.1 Dose-Response Plot 0 0 0 0 0 0 0 0 0 N 0 REF-Ref Toxicant NACL-Sodium Chloride CD-Ceriodaphnia dubia 9 10 34.000 31.000 32.000 31.000 30.000 31.000 27.000 30.000 13.000 1"1.000 3.000 3.000 1-Tailed Isotonic Critical Mean N-Mean 31.650 i.oooo 75.00 31.850 1.0000 75.00 31.000 0.9733 75.00 29.000 0.9105 75.00 12.100 0.3799 75.00 4.000 0.1256 Critical Skew Kurt 1.035
    • o.26293 0;3891 15.0663 500 1000 1500 Dose mg/L
    Statistical Analyses Used for PMSD calculation only. Ceriodal'.lhhia Survival and Reproduction Test-Reproduction Start Date: 511012016 Test ID: CdNaClCR
    • Sample ID:
    REF-Ref Toxlcant End Date: 511712016 Lab ID: ETS-Envir. Testing Sol. Sample Type: NACL-Sodium chloride Sample Date: Protocol: FWCHR-EPA-821-R-02-013 Test Spedes: CD-Ceriodaphnia dubia Comments: Conc-mg/L 0-Control 600 800 1000 1200 1400 1 34.000 35.000 30.000 29.000 .13.000 3.000 2 3 32.000 32.000 32.000 32.000 . 31.000 33.000 27.000 29.000 11.000 10.000 6.000 4.000 4 5 6 32.000 31.000 31.000 34.000 32.000 31:000 32"000 31,000 29.000 30.000 29,000 33.000 14,000 8.000 15.000 4.000 5,000 5.000 Transform: Uritran:sformed Conc-mg/L Mean N-Mean Mean Min Max D-Control 31.600 1.0000 31.600 29.000 34,000 600 32.100 1.0158 32.100 30.000 35.000 800 31.000 0.9810 31.000 29.000 33.000
    • 1000 29.000 0.9177 29.000 27.000 33.. 000
    • 1200 12.100 0.3829 12.100 8.000 15.000
    • 1400 4.000 0.1266 4.000 3.000 6,000 AuxiliaryTest5 Kolmogorov D Test indicates non-normal diStributfon (P: <= 0.01)
    Bartlett's Test indicates equal variances Jp "' Q,22} Hypothesis Test (1-tail, 0.05) NOEC LOEC ChV. Dunnett's Test 800 1000 894.427 Treatmerils vs D-Control CV% 4.992 4.514 3.725 6.082 18,666 26.352 .TU 7 29.000 32.000 32.000 28,000 15.000 4.000 N 10 10 10 to 10 10 Statistic 1.17686 6.9511 MS Du 1.63597 Dose.-Respcnse Plot 40 35 30 ~ 25 u
    I "Cl ?Q 2 -
    Q. ~ 15 10 5 J 0 0.,, c:' 0 0 6 Page 85 of87 a 0 0 Cl <X> 0 0 0 0 0 N s 9 30.000 34.000 30:000 32.000 31.000 30.000 28.000 27.000 11.000 13.000 3,000 3.000 1-Tailed t-Stat Critical -0.699 2.287 0.839 2.287 3.634 2.287 27-256 2-287 38.578 2.287 Critical 1.035 15.0863 MS Op MSB 0.05177 1472.06 0 0..,. 1-lail, 0.05 level of significance 10 31.000 31.000 31.000 30.000 11.000 3.000 MSO 1.636 1.636 1.635 1.636 1.636 Skew 0.26293 MSE F-Prob 2.55926 1.4E-45 Kurt 0.3891 df 5,54 -I I I I I I I I I I I Species: Ceriodap/mia dubia Dail' Chemistry: Concentration CONTROL 600 mg NaCl/L 800 mg NaCl/L Analyst Parameter pJI (S.U.) DO {mgfL) Ccmductivity {µmhos/cm)
    • Alkalinity (m CaCDl/L)
    • Hardness i:naCaCOJ/L}
    • Temperature (0C) pH(S.U.)
    DO(mg!L) Conductivity ( mhos/cm) ~Temperature (°C) DO(mg/L) Conductivity (µmhos/cm) ~Temperature {"C) pH(S:U.) DO {mg.IL} 1000 mg NaCl/L Conductivity {µmboS/cm)
    • -Temperature (°C) pH (S;U.)
    DO (mg/L) 1200 mg NaCIJL Conductivity (limbos/cm)
    • Temperatm*e ("C) pH (S.U.)
    DO (mg/L) 1400 mg NaCI/L C:onductivity mhos/cm} "'Temperature {°C) Page 5 of6 CdNaClCR #: 188 Day erformed H. D.O. and conductivil measurements only.) 1 2 1.$.0 Initial Initial
    • remperacures performed at the time oftest initiation. renewal or termination by the nnalys1 identified in tl1e Daily Renewal lnfonnation cable located on Page I. Alkalini~y and hardness peTformed by the analyst irlentiiicd on che bench sheet specific for each analysis and transcribed to this bench sheet by; ~-
    Page 86of87 SOP A Tl4 - Exhibit AT14. l, revision 11-0 I-I 4 Page 6 of6 Species: Ceriodaplmia duhia Concentration CONTROL 600 mg NaCl/L 800 mg NaCl/L 1000 mg NaCJ/L 1200 mg NaCl/L 1400 mg NaCJ/L Analyst Pars meter pH (S.U.) DO (mg/L) Condudivily (µmhos/cm)
    • Alkalinity (mo CaCQ3/L)
    • Hardness (mo CaCQ3/L)
    • Temperature
    ("C) pH(S.U.) DO {mg/L} ConductMty ( mhos/cm)
    • Temperature
    {°C} pH (S.U.) DO (mg/L) Conductivity {µmhos/cm)
    • Temperature
    ("C) pH (S.U.) DO (mg/L) Conductivity (µmhos/cm)
    • Tem~rature
    ("C} pH {S.U.) DO (mg/L) Conductivity ( ml1oslcm)
    • Temperature
    ("C} pH (S.U.} DO (mg/L) Condm:livity {µmhosfcm)
    • Temperature
    ('C) Initial CdNaCICR #: 188 Dsy {Analysl identified for each day, erfom1ed pH. D.O. ilnd conductivity measurements only. Final Initial Final Initial Final Initial
    • Temperatures pcrfonncd at the time of lest initiation. renewal or terminalion by the ana)y5l identified in the Daily Renewal Information table located on Page I. Alkalinity and hardness performed by 1he analyst identilied on the bench sheet specific for each analysis and transcribed to this bench sheel by: -...,/(,,___
    Page 87of87 SOP AT14-Exhibit ATM.I, revision 11-0 l-14 2'-{. f Final}}