13339 Hagers Ferry Road

Huntersville, NC 28078-7929

McGuire Nuclear Complex - MG03A2

Phone: 980-875-5245 Fax: 980-875-4349

Order Summary Report

Analytical Laboratory

Order Number: J12080079

Project Name: WWTS - Biweekly (1)

Lab Contact: Jason C Perkins

Date: 8/30/2012

Customer Address: 3195 Pine Hall Rd

Customer Name(s): Bill Kennedy, Melonie Martin, Wayne Chapman, Tom Johnson

Mailcode: Belews Steam Station

Belews Creek, NC 28012

Phone: 980-875-5348

Report Authorized By:

(Signature)

Program Comments:

Please contact the Program Manager (Jason C Perkins) with any questions regarding this report.

Data Flags & Calculations:

Any analytical tests or individual analytes within a test flagged with a Qualifier indicate a deviation from the method quality 

system or quality control requirement. The qualifier description is found at the end of the Certificate of Analysis (sample results) 

under the qualifiers heading. All results are reported on a dry weight basis unless otherwise noted. Subcontracted data 

included on the Duke Certificate of Analysis is to be used as information only. Certified vendor results can be found in the 

subcontracted lab final report. Duke Energy Analytical Laboratory subcontracts analyses to other vendor laboratories that have 

been qualified by Duke Energy to perform these analyses except where noted.

Data Package:

This data package includes analytical results that are applicable only to the samples described in this narrative. An estimation of 

the uncertainty of measurement for the results in the report is available upon request. This report shall not be reproduced, except 

in full, without the written consent of the Analytical Laboratory. Please contact the Analytical laboratory with any questions. The 

order of individual sections within this report is as follows:

Job Summary Report, Sample Identification, Technical Validation of Data Package, Analytical Laboratory Certificate of Analysis, 

Analytical Laboratory QC Reports, Sub-contracted Laboratory Results, Customer Specific Data Sheets, Reports & 

Documentation, Customer Database Entries, Test Case Narratives, Chain of Custody (COC)

Certification:

The Analytical Laboratory holds the following State Certifications : North Carolina (DENR) Certificate #248, South Carolina 

(DHEC) Laboratory ID # 99005. Contact the Analytical Laboratory for definitive information about the certification status of 

specific methods. 

Page 1 of 28
Sample ID's & Descriptions:

Sample ID Plant/Station

Collection 

Date and Time Collected By Sample Description

2012016850 BELEWS 08-Aug-12 8:30 AM TRAVIS THORNTON FGD Purge Eff 

2012016851 BELEWS 08-Aug-12 8:30 AM TRAVIS THORNTON EQ TANK EFF. 

2012016852 BELEWS 08-Aug-12 8:30 AM TRAVIS THORNTON BIOREACTOR 1 INF. 

2012016853 BELEWS 08-Aug-12 8:30 AM TRAVIS THORNTON BIOREACTOR 2 INF. 

2012016854 BELEWS 08-Aug-12 8:30 AM TRAVIS THORNTON BIOREACTOR 2 EFF. 

2012016855 BELEWS 08-Aug-12 8:30 AM TRAVIS THORNTON FILTER BLANK 

2012016856 BELEWS 08-Aug-12 8:30 AM TRAVIS THORNTON Trip Blank 

2012016857 BELEWS 08-Aug-12 8:00 AM TRAVIS THORNTON BIOREACTOR 1 INF (HG) 

2012016858 BELEWS 08-Aug-12 8:00 AM TRAVIS THORNTON HG BLANK BIOREACTOR 1 INF. 

2012016859 BELEWS 08-Aug-12 8:00 AM TRAVIS THORNTON BIOREACTOR 2 INF (HG) 

2012016860 BELEWS 08-Aug-12 8:00 AM TRAVIS THORNTON Hg Blk BioReactor 2 Inf 

2012016861 BELEWS 08-Aug-12 8:00 AM TRAVIS THORNTON BIOREACTOR 2 EFF (HG) 

2012016862 BELEWS 08-Aug-12 8:00 AM TRAVIS THORNTON Hg Blk BioReactor 2 Eff 

13 Total Samples

Page 2 of 28
COC and .pdf report are in agreement with sample totals 

and analyses (compliance programs and procedures).

All Results are less than the laboratory reporting limits.

All laboratory QA/QC requirements are acceptable.

Yes No

Technical Validation Review

Checklist:

Yes No

Yes No

Report Sections Included:

Job Summary Report Sub-contracted Laboratory Results

Sample Identification Customer Specific Data Sheets, Reports, & Documentation

Technical Validation of Data Package Customer Database Entries

Analytical Laboratory Certificate of Analysis

Analytical Laboratory QC Report

Chain of Custody

Reviewed By: DataBase Administrator Date: 8/30/2012

Electronic Data Deliverable (EDD) Sent Separately

Page 3 of 28
Certificate of Laboratory Analysis

This report shall not be reproduced, except in full.

Order # J12080079

2012016850

Collection Date: 08-Aug-12 8:30 AM

Site: FGD Purge Eff 

Matrix: OTHER

Analyte Result Units Qualifiers RDL Method Analysis Date/Time

Sample #:

DF Analyst

INORGANIC IONS BY IC

Bromide 120 mg/L 5 50 EPA 300.0 8/13/2012 6:37:00 PM JAHERMA

MERCURY (COLD VAPOR) IN WATER

Mercury (Hg) 295 ug/L 5 100 EPA 245.1 8/16/2012 1:22:53 PM AGIBBS

DISSOLVED METALS BY ICP

Manganese (Mn) 9.20 mg/L 0.05 10 EPA 200.7 8/14/2012 10:50:00 AM MHH7131

TOTAL RECOVERABLE METALS BY ICP

Boron (B) 218 mg/L 0.5 10 EPA 200.7 8/22/2012 12:31:00 PM DJSULL1

Manganese (Mn) 9.75 mg/L 0.05 10 EPA 200.7 8/22/2012 12:31:00 PM DJSULL1

DISSOLVED METALS BY ICP-MS

Selenium (Se) 179 ug/L 10 10 EPA 200.8 8/14/2012 1:55:00 PM DJSULL1

TOTAL RECOVERABLE METALS BY ICP-MS

Arsenic (As) 230 ug/L 10 10 EPA 200.8 8/16/2012 11:16:00 AM KRICHAR

Chromium (Cr) 257 ug/L 10 10 EPA 200.8 8/16/2012 11:16:00 AM KRICHAR

Copper (Cu) 145 ug/L 10 10 EPA 200.8 8/16/2012 11:16:00 AM KRICHAR

Nickel (Ni) 222 ug/L 10 10 EPA 200.8 8/16/2012 11:16:00 AM KRICHAR

Selenium (Se) 5610 ug/L 10 10 EPA 200.8 8/16/2012 11:16:00 AM KRICHAR

Silver (Ag) < 10 ug/L 10 10 EPA 200.8 8/16/2012 11:16:00 AM KRICHAR

Zinc (Zn) 273 ug/L 10 10 EPA 200.8 8/16/2012 11:16:00 AM KRICHAR

SELENIUM SPECIATION - (Analysis Performed by Applied Speciation and Consulting, LLC)

Vendor Parameter Complete Vendor Method V_AS&C

TOTAL DISSOLVED SOLIDS

TDS 21000 mg/L 200 1 SM2540C 8/15/2012 4:29:00 PM TJA7067

2012016851

Collection Date: 08-Aug-12 8:30 AM

Site: EQ TANK EFF. 

Matrix: OTHER

Analyte Result Units Qualifiers RDL Method Analysis Date/Time

Sample #:

DF Analyst

MERCURY (COLD VAPOR) IN WATER

Mercury (Hg) 206 ug/L 2.5 50 EPA 245.1 8/16/2012 1:25:13 PM AGIBBS

DISSOLVED METALS BY ICP

Manganese (Mn) 8.89 mg/L 0.05 10 EPA 200.7 8/14/2012 10:54:00 AM MHH7131

TOTAL RECOVERABLE METALS BY ICP

Boron (B) 220 mg/L 0.5 10 EPA 200.7 8/22/2012 12:35:00 PM DJSULL1

Manganese (Mn) 9.71 mg/L 0.05 10 EPA 200.7 8/22/2012 12:35:00 PM DJSULL1

Page 4 of 28
Certificate of Laboratory Analysis

This report shall not be reproduced, except in full.

Order # J12080079

2012016851

Collection Date: 08-Aug-12 8:30 AM

Site: EQ TANK EFF. 

Matrix: OTHER

Analyte Result Units Qualifiers RDL Method Analysis Date/Time

Sample #:

DF Analyst

DISSOLVED METALS BY ICP-MS

Selenium (Se) 127 ug/L 10 10 EPA 200.8 8/14/2012 1:58:00 PM DJSULL1

TOTAL RECOVERABLE METALS BY ICP-MS

Arsenic (As) 204 ug/L 10 10 EPA 200.8 8/16/2012 11:20:00 AM KRICHAR

Chromium (Cr) 223 ug/L 10 10 EPA 200.8 8/16/2012 11:20:00 AM KRICHAR

Copper (Cu) 129 ug/L 10 10 EPA 200.8 8/16/2012 11:20:00 AM KRICHAR

Nickel (Ni) 202 ug/L 10 10 EPA 200.8 8/16/2012 11:20:00 AM KRICHAR

Selenium (Se) 5010 ug/L 10 10 EPA 200.8 8/16/2012 11:20:00 AM KRICHAR

Silver (Ag) < 10 ug/L 10 10 EPA 200.8 8/16/2012 11:20:00 AM KRICHAR

Zinc (Zn) 235 ug/L 10 10 EPA 200.8 8/16/2012 11:20:00 AM KRICHAR

2012016852

Collection Date: 08-Aug-12 8:30 AM

Site: BIOREACTOR 1 INF. 

Matrix: OTHER

Analyte Result Units Qualifiers RDL Method Analysis Date/Time

Sample #:

DF Analyst

DISSOLVED METALS BY ICP

Manganese (Mn) 8.73 mg/L 0.05 10 EPA 200.7 8/14/2012 10:58:00 AM MHH7131

TOTAL RECOVERABLE METALS BY ICP

Boron (B) 220 mg/L 0.5 10 EPA 200.7 8/22/2012 12:39:00 PM DJSULL1

Manganese (Mn) 8.79 mg/L 0.05 10 EPA 200.7 8/22/2012 12:39:00 PM DJSULL1

DISSOLVED METALS BY ICP-MS

Selenium (Se) 114 ug/L 10 10 EPA 200.8 8/14/2012 2:01:00 PM DJSULL1

TOTAL RECOVERABLE METALS BY ICP-MS

Arsenic (As) < 10 ug/L 10 10 EPA 200.8 8/16/2012 11:23:00 AM KRICHAR

Chromium (Cr) < 10 ug/L 10 10 EPA 200.8 8/16/2012 11:23:00 AM KRICHAR

Copper (Cu) < 10 ug/L 10 10 EPA 200.8 8/16/2012 11:23:00 AM KRICHAR

Nickel (Ni) 115 ug/L 10 10 EPA 200.8 8/16/2012 11:23:00 AM KRICHAR

Selenium (Se) 104 ug/L 10 10 EPA 200.8 8/16/2012 11:23:00 AM KRICHAR

Silver (Ag) < 10 ug/L 10 10 EPA 200.8 8/16/2012 11:23:00 AM KRICHAR

Zinc (Zn) < 10 ug/L 10 10 EPA 200.8 8/16/2012 11:23:00 AM KRICHAR

SELENIUM SPECIATION - (Analysis Performed by Applied Speciation and Consulting, LLC)

Vendor Parameter Complete Vendor Method V_AS&C

Page 5 of 28
Certificate of Laboratory Analysis

This report shall not be reproduced, except in full.

Order # J12080079

2012016853

Collection Date: 08-Aug-12 8:30 AM

Site: BIOREACTOR 2 INF. 

Matrix: OTHER

Analyte Result Units Qualifiers RDL Method Analysis Date/Time

Sample #:

DF Analyst

TOTAL RECOVERABLE METALS BY ICP

Boron (B) 218 mg/L 0.5 10 EPA 200.7 8/22/2012 12:43:00 PM DJSULL1

Manganese (Mn) 7.57 mg/L 0.05 10 EPA 200.7 8/22/2012 12:43:00 PM DJSULL1

TOTAL RECOVERABLE METALS BY ICP-MS

Arsenic (As) < 10 ug/L 10 10 EPA 200.8 8/16/2012 11:26:00 AM KRICHAR

Chromium (Cr) < 10 ug/L 10 10 EPA 200.8 8/16/2012 11:26:00 AM KRICHAR

Copper (Cu) < 10 ug/L 10 10 EPA 200.8 8/16/2012 11:26:00 AM KRICHAR

Nickel (Ni) 15.0 ug/L 10 10 EPA 200.8 8/16/2012 11:26:00 AM KRICHAR

Selenium (Se) 22.4 ug/L 10 10 EPA 200.8 8/16/2012 11:26:00 AM KRICHAR

Silver (Ag) < 10 ug/L 10 10 EPA 200.8 8/16/2012 11:26:00 AM KRICHAR

Zinc (Zn) < 10 ug/L 10 10 EPA 200.8 8/16/2012 11:26:00 AM KRICHAR

2012016854

Collection Date: 08-Aug-12 8:30 AM

Site: BIOREACTOR 2 EFF. 

Matrix: OTHER

Analyte Result Units Qualifiers RDL Method Analysis Date/Time

Sample #:

DF Analyst

INORGANIC IONS BY IC

Bromide 120 mg/L 5 50 EPA 300.0 8/13/2012 6:19:00 PM JAHERMA

MERCURY (COLD VAPOR) IN WATER

Mercury (Hg) < 1 ug/L 1 20 EPA 245.1 8/16/2012 1:27:33 PM AGIBBS

TOTAL RECOVERABLE METALS BY ICP

Boron (B) 213 mg/L 0.5 10 EPA 200.7 8/22/2012 12:47:00 PM DJSULL1

Manganese (Mn) 5.56 mg/L 0.05 10 EPA 200.7 8/22/2012 12:47:00 PM DJSULL1

TOTAL RECOVERABLE METALS BY ICP-MS

Arsenic (As) < 5 ug/L 5 5 EPA 200.8 8/16/2012 11:29:00 AM KRICHAR

Chromium (Cr) < 5 ug/L 5 5 EPA 200.8 8/16/2012 11:29:00 AM KRICHAR

Copper (Cu) < 5 ug/L 5 5 EPA 200.8 8/16/2012 11:29:00 AM KRICHAR

Nickel (Ni) < 5 ug/L 5 5 EPA 200.8 8/16/2012 11:29:00 AM KRICHAR

Selenium (Se) 8.35 ug/L 5 5 EPA 200.8 8/16/2012 11:29:00 AM KRICHAR

Silver (Ag) < 5 ug/L 5 5 EPA 200.8 8/16/2012 11:29:00 AM KRICHAR

Zinc (Zn) < 5 ug/L 5 5 EPA 200.8 8/16/2012 11:29:00 AM KRICHAR

SELENIUM SPECIATION - (Analysis Performed by Applied Speciation and Consulting, LLC)

Vendor Parameter Complete Vendor Method V_AS&C

Page 6 of 28
Certificate of Laboratory Analysis

This report shall not be reproduced, except in full.

Order # J12080079

2012016855

Collection Date: 08-Aug-12 8:30 AM

Site: FILTER BLANK 

Matrix: OTHER

Analyte Result Units Qualifiers RDL Method Analysis Date/Time

Sample #:

DF Analyst

DISSOLVED METALS BY ICP

Manganese (Mn) < 0.005 mg/L 0.005 1 EPA 200.7 8/14/2012 11:02:00 AM MHH7131

DISSOLVED METALS BY ICP-MS

Selenium (Se) 1.05 ug/L B 1 1 EPA 200.8 8/14/2012 1:27:00 PM DJSULL1

2012016856

Collection Date: 08-Aug-12 8:30 AM

Site: Trip Blank 

Matrix: OTHER

Analyte Result Units Qualifiers RDL Method Analysis Date/Time

Sample #:

DF Analyst

TOTAL RECOVERABLE METALS BY ICP

Boron (B) < 0.05 mg/L 0.05 1 EPA 200.7 8/22/2012 12:23:00 PM DJSULL1

Manganese (Mn) < 0.005 mg/L 0.005 1 EPA 200.7 8/22/2012 12:23:00 PM DJSULL1

TOTAL RECOVERABLE METALS BY ICP-MS

Arsenic (As) < 1 ug/L 1 1 EPA 200.8 8/16/2012 10:28:00 AM KRICHAR

Chromium (Cr) < 1 ug/L 1 1 EPA 200.8 8/16/2012 10:28:00 AM KRICHAR

Copper (Cu) < 1 ug/L 1 1 EPA 200.8 8/16/2012 10:28:00 AM KRICHAR

Nickel (Ni) < 1 ug/L 1 1 EPA 200.8 8/16/2012 10:28:00 AM KRICHAR

Selenium (Se) < 1 ug/L 1 1 EPA 200.8 8/16/2012 10:28:00 AM KRICHAR

Silver (Ag) < 1 ug/L 1 1 EPA 200.8 8/16/2012 10:28:00 AM KRICHAR

Zinc (Zn) < 1 ug/L 1 1 EPA 200.8 8/16/2012 10:28:00 AM KRICHAR

SELENIUM SPECIATION - (Analysis Performed by Applied Speciation and Consulting, LLC)

Vendor Parameter Complete Vendor Method V_AS&C

2012016857

Collection Date: 08-Aug-12 8:00 AM

Site: BIOREACTOR 1 INF (HG) 

Matrix: OTHER

Analyte Result Units Qualifiers RDL Method Analysis Date/Time

Sample #:

DF Analyst

MERCURY 1631 - (Analysis Performed by Brooks Rand Labs LLC)

Vendor Parameter Complete Vendor Method V_BRAND

2012016858

Collection Date: 08-Aug-12 8:00 AM

Site: HG BLANK BIOREACTOR 1 INF. 

Matrix: OTHER

Analyte Result Units Qualifiers RDL Method Analysis Date/Time

Sample #:

DF Analyst

MERCURY 1631 - (Analysis Performed by Brooks Rand Labs LLC)

Vendor Parameter Complete Vendor Method V_BRAND

Page 7 of 28
Certificate of Laboratory Analysis

This report shall not be reproduced, except in full.

Order # J12080079

2012016858

Collection Date: 08-Aug-12 8:00 AM

Site: HG BLANK BIOREACTOR 1 INF. 

Matrix: OTHER

Analyte Result Units Qualifiers RDL Method Analysis Date/Time

Sample #:

DF Analyst

2012016859

Collection Date: 08-Aug-12 8:00 AM

Site: BIOREACTOR 2 INF (HG) 

Matrix: OTHER

Analyte Result Units Qualifiers RDL Method Analysis Date/Time

Sample #:

DF Analyst

MERCURY 1631 - (Analysis Performed by Brooks Rand Labs LLC)

Vendor Parameter Complete Vendor Method V_BRAND

2012016860

Collection Date: 08-Aug-12 8:00 AM

Site: Hg Blk BioReactor 2 Inf 

Matrix: OTHER

Analyte Result Units Qualifiers RDL Method Analysis Date/Time

Sample #:

DF Analyst

MERCURY 1631 - (Analysis Performed by Brooks Rand Labs LLC)

Vendor Parameter Complete Vendor Method V_BRAND

2012016861

Collection Date: 08-Aug-12 8:00 AM

Site: BIOREACTOR 2 EFF (HG) 

Matrix: OTHER

Analyte Result Units Qualifiers RDL Method Analysis Date/Time

Sample #:

DF Analyst

MERCURY 1631 - (Analysis Performed by Brooks Rand Labs LLC)

Vendor Parameter Complete Vendor Method V_BRAND

2012016862

Collection Date: 08-Aug-12 8:00 AM

Site: Hg Blk BioReactor 2 Eff 

Matrix: OTHER

Analyte Result Units Qualifiers RDL Method Analysis Date/Time

Sample #:

DF Analyst

MERCURY 1631 - (Analysis Performed by Brooks Rand Labs LLC)

Vendor Parameter Complete Vendor Method V_BRAND

Qualifiers:

B Target analyte detected in method blank at or above the reporting limit. Target analyte concentration in 

sample is less than 10X the concentration in the method blank. Analyte concentration in sample could be 

due to contamination.

Page 8 of 28
 

August 20, 2012 

Jay Perkins 

Duke Energy Analytical Laboratory 

Mail Code MGO3A2 (Building 7405) 

13339 Hagers Ferry Rd. 

Huntersville, NC 28078 

(704) 875-5245 

Project: Belews - FGD WWTS Bi-Monthly Sampling) (LIMS #J12080079) 

Dear Mr. Perkins, 

Attached is the report associated with four (4) aqueous samples submitted for selenium 

speciation analysis on August 9, 2012. The samples were received in a sealed cooler at -0.3°C 

on August 10, 2012. Selenium speciation analysis was performed via ion chromatography 

inductively coupled plasma collision reaction cell mass spectrometry (IC-ICP-CRC-MS). Any 

issues associated with the analysis are addressed in the following report. 

If you have any questions, please feel free to contact me at your convenience. 

 Sincerely, 

 

 Russell Gerads 

 Vice President 

 Applied Speciation and Consulting, LLC 

 

Page 9 of 28
Applied Speciation and Consulting, LLC 

Report prepared for: 

Jay Perkins 

Duke Energy Analytical Laboratory 

Mail Code MGO3A2 (Building 7405) 

13339 Hagers Ferry Rd. 

Huntersville, NC 28078 

Project: Belews - FGD WWTS Bi-Monthly Sampling) (LIMS #J12080079) 

August 20, 2012 

1. Sample Reception 

Four (4) aqueous samples in 125mL HDPE bottles (provided by Applied Speciation and 

Consulting) were submitted for selenium speciation analysis on August 9, 2012. The 

samples were received on August 10, 2012 in a sealed container at -0.3°C. 

The samples were received in a laminar flow clean hood, void of trace metals contamination 

and ultra-violet radiation, and were designated discrete sample identifiers. An aliquot of 

each sample was filtered (0.45μm) and each filtrate was stored in a secure, monitored 

cryofreezer (maintained at a temperature of -80oC) until selenium speciation analysis could 

be performed via ion chromatography inductively coupled plasma collision reaction cell 

mass spectrometry (IC-ICP-CRC-MS). 

2. Sample Preparation 

All sample preparation is performed in laminar flow clean hoods known to be free from trace 

metals contamination. All applied water for dilutions and sample preservatives are 

monitored for contamination to account for any biases associated with the sample results. 

Selenium Speciation Analysis by IC-ICP-CRC-MS Prior to analysis, an aliquot of each 

sample was filtered with a syringe filter (0.45μm) and injected directly into a sealed 

autosampler vial. No further sample preparation was performed as any chemical alteration of 

a sample may shift the equilibrium of the system, resulting in changes in speciation ratios. 

3. Sample Analysis 

All sample analysis is preceded by a minimum of a five-point calibration curve spanning the 

entire concentration range of interest. Calibration curves are performed at the beginning of 

each analytical day. All calibration curves, associated with each species of interest, are 

Page 10 of 28
standardized by linear regression resulting in a response factor. All sample results are 

instrument blank corrected to account for any operational biases associated with the 

analytical platform. 

Prior to sample analysis, all calibration curves are verified using second source standards 

which are identified as initial calibration verification standards (ICV). 

Ongoing instrument performance is identified by the analysis of continuing calibration 

verification standards (CCV) and continuing calibration blanks (CCB) at a minimal interval 

of every ten analytical runs. 

Selenium Speciation Analysis by IC-ICP-CRC-MS Each sample for selenium speciation 

analysis was analyzed by ion chromatography inductively coupled plasma collision reaction 

cell mass spectrometry (IC-ICP-CRC-MS) on August 17, 2012. An aliquot of each sample is

injected onto an anion exchange column and mobilized by a basic (pH > 7) gradient. The 

eluting selenium species are then introduced into a radio frequency (RF) plasma where 

energy-transfer processes cause desolvation, atomization, and ionization. The ions are 

extracted from the plasma through a differentially-pumped vacuum interface and travel 

through a pressurized chamber (CRC) containing a reaction gas which preferentially reacts 

with interfering ions of the same target mass to charge ratios (m/z). A solid-state detector 

detects ions transmitted through the mass analyzer and the resulting current is processed by a 

data handling system. 

Retention times for each eluting species are compared to known standards for species 

identification. 

4. Analytical Issues 

The overall analyses went well and no significant analytical issues were encountered. All 

quality control parameters associated with the samples were within acceptance limits.

The estimated method detection limits (eMDLs) for selenite, selenate, and selenocyanate are 

generated from replicate analyses of the lowest standard in the calibration curve. Not all 

selenium species are present in preparation blanks; therefore, eMDL calculations based on 

preparation blanks are artificially biased low. 

The eMDL for methylseleninic acid and selenomethionine is calculated from the average 

eMDL of selenite, selenate, and selenocyanate. The calibration does not contain 

methylseleninic acid or selenomethionine due to impurities in these standards which would 

bias the results for other selenium species. 

Page 11 of 28
If you have any questions or concerns regarding this report, please feel free to contact me. 

Sincerely, 

Russell Gerads 

Vice President 

Applied Speciation and Consulting, LLC 

Page 12 of 28
Sample Results

Sample ID Se(IV) Se(VI) SeCN MeSe(IV) SeMe

Unknown Se 

Species (n)

FGD Purge Eff 87.7 65.0 ND (<0.40) ND (<1.7) ND (<1.7) 0.0 (0)

BioReactor 1 Inf 23.0 69.3 ND (<0.099) 2.31 ND (<0.42) 0.0 (0)

BioReactor 2 Eff ND (<0.81) ND (<0.35) ND (<0.099) ND (<0.42) ND (<0.42) 0.0 (0)

Metals Trip Blk ND (<0.032) ND (<0.014) ND (<0.0040) ND (<0.017) ND (<0.017) 0.0 (0)

All results reflect the applied dilution and are reported in μg/L

ND = Not detected at the applied dilution

SeCN = Selenocyanate

MeSe(IV) = Methylseleninic acid

SeMe = Selenomethionine

Unknown Se Species = Total concentration of all unknown Se species observed by IC-ICP-MS

n = number of unknown Se species observed

Report Generated by: Russell Gerads

Applied Speciation and Consulting, LLC

Selenium Speciation Results for Duke Energy

Project Name: Belews - FGD WWTS Bi-Monthly Sampling)

Contact: Jay Perkins

Date: August 20, 2012

LIMS #J12080079

Page 13 of 28
Quality Control Summary - Preparation Blank Summary

Analyte (μg/L) PBW1 PBW2 PBW3 PBW4 Mean StdDev eMDL* eMDL 10x eMDL 250x

Se(IV) 0.000 0.000 0.000 0.000 0.000 0.000 0.0032 0.032 0.81

Se(VI) 0.000 0.000 0.000 0.000 0.000 0.000 0.0014 0.014 0.35

SeCN 0.000 0.000 0.000 0.000 0.000 0.000 0.00040 0.0040 0.099

MeSe(IV) 0.000 0.000 0.000 0.000 0.000 0.000 0.0017 0.017 0.42

SeMe 0.000 0.000 0.000 0.000 0.000 0.000 0.0017 0.017 0.42

eMDL = Estimated Method Detection Limit

*Please see narrative regarding eMDL calculations

Quality Control Summary - Certified Reference Materials

Analyte (μg/L) CRM True Value Result Recovery

Se(IV) LCS 9.57 9.38 98.0

Se(VI) LCS 9.48 8.95 94.4

SeCN LCS 8.92 8.61 96.5

MeSe(IV) LCS 6.47 6.60 102.0

SeMe LCS 9.32 8.40 90.1

Applied Speciation and Consulting, LLC

Selenium Speciation Results for Duke Energy

Project Name: Belews - FGD WWTS Bi-Monthly Sampling)

Contact: Jay Perkins

LIMS #J12080079

Date: August 20, 2012

Report Generated by: Russell Gerads

Page 14 of 28
Quality Control Summary - Matrix Duplicates

Analyte (μg/L) Sample ID Rep 1 Rep 2 Mean RPD

Se(IV) BioReactor 2 Eff ND (<0.81) ND (<0.81) NC NC

Se(VI) BioReactor 2 Eff ND (<0.35) ND (<0.35) NC NC

SeCN BioReactor 2 Eff ND (<0.099) ND (<0.099) NC NC

MeSe(IV) BioReactor 2 Eff ND (<0.42) ND (<0.42) NC NC

SeMe BioReactor 2 Eff ND (<0.42) ND (<0.42) NC NC

ND = Not detected at the applied dilution

NC = Value was not calculated due to one or more concentrations below the eMDL

Quality Control Summary - Matrix Spike/ Matrix Spike Duplicate

Analyte (μg/L) Sample ID Spike Conc MS Result Recovery Spike Conc MSD Result Recovery RPD

Se(IV) BioReactor 2 Eff 1390 1484 106.8 1390 1493 107.4 0.6

Se(VI) BioReactor 2 Eff 1261 1301 103.1 1261 1318 104.5 1.3

SeCN BioReactor 2 Eff 1144 1124 98.3 1144 1141 99.7 1.5

Applied Speciation and Consulting, LLC

Selenium Speciation Results for Duke Energy

Project Name: Belews - FGD WWTS Bi-Monthly Sampling)

Contact: Jay Perkins

LIMS #J12080079

Date: August 20, 2012

Report Generated by: Russell Gerads

Page 15 of 28
Page 16 of 28
3958 6th Ave NW • Seattle, WA 98107 • T: 206-632-6206 • F: 206-632-6017 • www.brooksrand.com • brl@brooksrand.com

August 24, 2012

Duke Energy

ATTN: Jay Perkins

Scientific Support-Laboratory

13339 Hagers Ferry Road

Huntersville NC 28078

jcperkins@duke-energy.com

labcustomer@duke-energy.com

RE: Project DUK-HV1201 Client Project: J12080079

Dear Mr. Perkins,

On August 10, 2012, Brooks Rand Labs (BRL) received three (3) wastewater samples and three

(3) corresponding field blanks. The samples were logged-in for total mercury (Hg) analysis 

according to the chain-of-custody form. All samples were received, prepared, analyzed, and 

stored according to BRL SOPs and EPA methodology.

The results were blank-corrected as described in the calculations section of the relevant SOP(s) 

and may have been evaluated using reporting limits that have been adjusted to account for 

sample aliquot size. Please refer to the Sample Results page for sample-specific MDLs, MRLs, 

and other details. 

Several continuing calibration blanks (CCBs) were analyzed on purge vessel (PV4) to remove 

any possible carryover. Following the CCBs, a non-reported continuing calibration verification 

(CCV) was analyzed on this same purge vessel, which resulted in an elevated recovery (157%). 

Since the result of the CCV was indicative of the carryover contamination, PV4 retired from 

service and no other client samples were analyzed using that purge vessel. All samples 

analyzed on PV4 were re-analyzed.

Sample BioReactor 2 Inf (1232034-03) yielded a non-detectable result. The BRL label and Duke 

Energy label were verified. The sample was re-analyzed twice and confirmed the original nondetectable result. Also, the result of field blank sample, Hg Blk BioReactor 2 Eff (1232034-06), 

was 29.9 ng/L and was significant when compared to the associated total Hg field sample result. 

It is entirely likely these samples were mislabeled in the field.

All data was reported without qualification, aside from concentration qualifiers, and all

associated quality control sample results met the acceptance criteria.

BRL, an accredited laboratory, certifies the reported results of all analyses for which BRL is 

NELAP accredited meet all NELAP requirements. For more details, see the Report Information

page of the report. 

Page 17 of 28
Please feel free to contact me if you have any questions regarding this report.

Sincerely,

 

Tiffany Stilwater 

Project Manager 

tiffany@brooksrand.com

Page 18 of 28
Project ID: DUK-HV1201

PM: Tiffany Stilwater

Client PM: Jay Perkins

 Client PO: 141391

Definition of Data Qualifiers

(Effective 9/23/09)

Laboratory Accreditation

BRL is accredited by the National Environmental Laboratory Accreditation Program (NELAP) through the State of Florida 

Department of Health, Bureau of Laboratories (E87982) and is certified to perform many environmental analyses. BRL is 

also certified by many other states to perform environmental analyses. For a current list of our accreditations /certifications, 

please visit our website at <http://www.brooksrand.com/default.asp?contentID=586>. Results reported relate only to the 

samples listed in the report.

Report Information

BLK

BRL

BS

CAL

CCV

CRM

D

DUP

ICV

MSD

ND

NR

PS

REC

RPD

RSD

SCV

SOP

method blank 

Brooks Rand Labs

laboratory fortified blank

calibration standard

continuing calibration verification

certified reference material

dissolved fraction

duplicate

initial calibration verification

matrix spike duplicate

non-detect

non-reportable

post preparation spike

percent recovery

relative percent difference

relative standard deviation

secondary calibration verification

standard operating procedure

MDL

MRL

MS

method detection limit

method reporting limit

matrix spike

SRM

T

COC

standard reference material

total recoverable fraction

chain of custody record 

Common Abbreviations

These qualifiers are based on those previously utilized by Brooks Rand Labs, those found in the EPA SOW ILM03.0, 

Exhibit B, Section III, pg. B-18, and the USEPA Contract Laboratory Program National Functional Guidelines for Inorganic 

Superfund Data Review; USEPA; January 2010. These supersede all previous qualifiers ever employed by BRL.

Detected by the instrument, the result is > the MDL but ≤ the MRL. Result is reported and considered an estimate.

B

E 

An estimated value due to the presence of interferences. A full explanation is presented in the narrative.

H 

Holding time and/or preservation requirements not met. Result is estimated.

J 

Estimated value. A full explanation is presented in the narrative.

J-M

Duplicate precision (RPD) for associated QC sample was not within acceptance criteria. Result is estimated.

J-N

Spike recovery for associated QC sample was not within acceptance criteria. Result is estimated.

M 

Duplicate precision (RPD) was not within acceptance criteria. Result is estimated.

N 

Spike recovery was not within acceptance criteria. Result is estimated.

R 

Rejected, unusable value. A full explanation is presented in the narrative.

U 

Result is ≤ the MDL or client requested reporting limit (CRRL). Result reported as the MDL or CRRL.

X 

Result is not BLK-corrected and is within 10x the absolute value of the highest detectable BLK in the batch. 

Result is estimated.

Field Quality Control Samples

Please be notified that certain EPA methods require the collection of field quality control samples of an appropriate type 

and frequency; failure to do so is considered a deviation from some methods and for compliance purposes should only be 

done with the approval of regulatory authorities. Please see the specific EPA methods for details regarding required field 

quality control samples.

3958 6th Avenue NW Seattle WA 98107 · P(206) 632-6206 · F(206) 632-6017 · brl@brooksrand.com · www.brooksrand.com

Page 19 of 28
Project ID: DUK-HV1201

PM: Tiffany Stilwater

Client PM: Jay Perkins

 Client PO: 141391

Sample Information

Sample Lab ID Report Matrix Type Sampled Received

BioReactor 1 Inf 1232034-01 Influent Sample 08/08/2012 08/10/2012

Hg Blk BioReactor 1 Inf 1232034-02 DIW Field Blank 08/08/2012 08/10/2012

BioReactor 2 Inf 1232034-03 Influent QC Sample 08/08/2012 08/10/2012

Hg Blk BioReactor 2 Inf 1232034-04 DIW Field Blank 08/08/2012 08/10/2012

BioReactor 2 Eff 1232034-05 Effluent Sample 08/08/2012 08/10/2012

Hg Blk BioReactor 2 Eff 1232034-06 DIW Field Blank 08/08/2012 08/10/2012

Batch Summary

Analyte Lab Matrix Method Prepared Analyzed Batch Sequence

Hg Water EPA 1631 08/15/2012 08/17/2012 B121451 1200642

3958 6th Avenue NW Seattle WA 98107 · P(206) 632-6206 · F(206) 632-6017 · brl@brooksrand.com · www.brooksrand.com

Page 20 of 28
Project ID: DUK-HV1201

PM: Tiffany Stilwater

Client PM: Jay Perkins

 Client PO: 141391

Sample Results

Sample Analyte Report Matrix Basis Result Qualifier MDL MRL Unit Batch Sequence

BioReactor 1 Inf

1232034-01 Hg Influent T 252 15.3 40.8 ng/L B121451 1200642

BioReactor 2 Eff

1232034-05 Hg Effluent T 106 1.53 4.08 ng/L B121451 1200642

BioReactor 2 Inf

1232034-03 Hg Influent T 0.15 U 0.15 0.41 ng/L B121451 1200642

Hg Blk BioReactor 1 Inf

1232034-02 Hg DIW T 0.15 U 0.15 0.40 ng/L B121451 1200642

Hg Blk BioReactor 2 Eff

1232034-06 Hg DIW T 29.9 0.15 0.40 ng/L B121451 1200642

Hg Blk BioReactor 2 Inf

1232034-04 Hg DIW T 0.15 U 0.15 0.40 ng/L B121451 1200642

3958 6th Avenue NW Seattle WA 98107 · P(206) 632-6206 · F(206) 632-6017 · brl@brooksrand.com · www.brooksrand.com

Page 21 of 28
Project ID: DUK-HV1201

PM: Tiffany Stilwater

Client PM: Jay Perkins

 Client PO: 141391

Accuracy & Precision Summary

Batch: B121451

Analyte Native Spike Result Units REC & Limits RPD & Limits

Method: EPA 1631

Lab Matrix: Water

Sample

B121451-SRM1 Certified Reference Material (1232065, NIST 1641d 1000x dilution)

Hg 15.68 15.73 ng/L 100% 85-115

B121451-MS2 Matrix Spike (1232034-01)

Hg 260.0 1224 1641 ng/L 113% 71-125

B121451-MSD2 Matrix Spike Duplicate (1232034-01)

Hg 260.0 1224 1637 ng/L 112% 71-125 240.2%

B121451-MS3 Matrix Spike (1232034-03)

Hg ND 2.035 2.19 ng/L 108% 71-125

Method Blanks & Reporting Limits

Batch: B121451

Method: EPA 1631

Matrix: Water

Analyte: Hg

Sample Result Units

B121451-BLK1 0.23 ng/L

B121451-BLK2 0.17 ng/L

B121451-BLK3 0.08 ng/L

B121451-BLK4 0.07 ng/L

Average: 0.14 Standard Deviation: 0.08 MDL: 0.15

Limit: 0.50 Limit: 0.10 MRL: 0.40

3958 6th Avenue NW Seattle WA 98107 · P(206) 632-6206 · F(206) 632-6017 · brl@brooksrand.com · www.brooksrand.com

Page 22 of 28
Project ID: DUK-HV1201

PM: Tiffany Stilwater

Client PM: Jay Perkins

 Client PO: 141391

Instrument Calibration

Sequence: 1200642

Instrument: THG-05 Method: EPA 1631

Date: 08/17/2012

Total Mercury and Mercury Speciation by CVAFS

Analyte: Hg

Lab ID True Value Result Units REC & Limits

1200642-IBL1 5.91 pg of Hg

1200642-IBL2 5.43 pg of Hg

1200642-IBL3 4.83 pg of Hg

1200642-IBL4 6.71 pg of Hg

1200642-CAL1 25.00 25.25 pg of Hg 101%

1200642-CAL2 100.0 93.67 pg of Hg 94%

1200642-CAL3 500.0 477.2 pg of Hg 95%

1200642-CAL4 2500 2661 pg of Hg 106%

1200642-CAL5 10000 10470 pg of Hg 105%

1200642-ICV1 1568 1573 pg of Hg 100% 85-115

1200642-CCV1 500.0 469.5 pg of Hg 94% 77-123

1200642-CCB1 12.0 pg of Hg

1200642-CCB2 3260 pg of Hg

1200642-CCB3 462 pg of Hg

1200642-CCB4 645 pg of Hg

1200642-CCB5 378 pg of Hg

1200642-CCB6 284 pg of Hg

1200642-CCB7 357 pg of Hg

1200642-CCB8 222 pg of Hg

1200642-CCV3 500.0 516.3 pg of Hg 103% 77-123

1200642-CCB9 2.30 pg of Hg

1200642-CCV4 500.0 546.6 pg of Hg 109% 77-123

1200642-CCBA 3.49 pg of Hg

1200642-ICB2 9.07 pg of Hg

1200642-CCV5 500.0 546.0 pg of Hg 109% 77-123

3958 6th Avenue NW Seattle WA 98107 · P(206) 632-6206 · F(206) 632-6017 · brl@brooksrand.com · www.brooksrand.com

Page 23 of 28
Project ID: DUK-HV1201

PM: Tiffany Stilwater

Client PM: Jay Perkins

 Client PO: 141391

Sample Containers

Lab ID: 1232034-01 Report Matrix: Influent

Sample: BioReactor 1 Inf Sample Type: Sample Received: 08/10/2012

Collected: 08/08/2012

Des Container Size Lot Preservation P-Lot pH Ship. Cont.

A 71392670

10

Bottle FLPE Hg-T 250 mL none n/a Cooler

Lab ID: 1232034-02 Report Matrix: DIW

Sample: Hg Blk BioReactor 1 Inf Sample Type: Field Blank Received: 08/10/2012

Collected: 08/08/2012

Des Container Size Lot Preservation P-Lot pH Ship. Cont.

A 71392670

10

Bottle FLPE Hg-T 250 mL none n/a Cooler

Lab ID: 1232034-03 Report Matrix: Influent

Sample: BioReactor 2 Inf Sample Type: QC Sample Received: 08/10/2012

Collected: 08/08/2012

Des Container Size Lot Preservation P-Lot pH Ship. Cont.

A 71392670

10

Bottle FLPE Hg-T 250 mL none n/a Cooler

Lab ID: 1232034-04 Report Matrix: DIW

Sample: Hg Blk BioReactor 2 Inf Sample Type: Field Blank Received: 08/10/2012

Collected: 08/08/2012

Des Container Size Lot Preservation P-Lot pH Ship. Cont.

A 71392670

10

Bottle FLPE Hg-T 250 mL none n/a Cooler

Lab ID: 1232034-05 Report Matrix: Effluent

Sample: BioReactor 2 Eff Sample Type: Sample Received: 08/10/2012

Collected: 08/08/2012

Des Container Size Lot Preservation P-Lot pH Ship. Cont.

A 71392670

10

Bottle FLPE Hg-T 250 mL none n/a Cooler

Lab ID: 1232034-06 Report Matrix: DIW

Sample: Hg Blk BioReactor 2 Eff Sample Type: Field Blank Received: 08/10/2012

Collected: 08/08/2012

Des Container Size Lot Preservation P-Lot pH Ship. Cont.

A 71392670

10

Bottle FLPE Hg-T 250 mL none n/a Cooler

3958 6th Avenue NW Seattle WA 98107 · P(206) 632-6206 · F(206) 632-6017 · brl@brooksrand.com · www.brooksrand.com

Page 24 of 28
Project ID: DUK-HV1201

PM: Tiffany Stilwater

Client PM: Jay Perkins

 Client PO: 141391

Shipping Containers

Cooler

Tracking No: 5353 0519 2892 via FedEx

Temperature: -0.8 °C

Coolant Type: Ice

Description: Cooler

Damaged in transit? No

Returned to client? No

Custody seals present? No

Custody seals intact? No

COC present? Yes

Received: August 10, 2012 9:00

3958 6th Avenue NW Seattle WA 98107 · P(206) 632-6206 · F(206) 632-6017 · brl@brooksrand.com · www.brooksrand.com

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