Analytical Report.pdf
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- Solicitation number
- S-73000-00008075
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- Coos County, Oregon
About this file
This document is an analytical report provided by Pace Analytical National on behalf of the Oregon Department of Transportation (ODOT) for the Chandler Bridge project. The report details the results of analytical testing performed on two bridge paint samples collected by Kenny Camp on February 15, 2022. The samples were analyzed for metals content via ICP Method 6010D and polychlorinated biphenyls (PCBs) via GC Method 8082A. Key findings include elevated levels of chromium, lead, and PCB 1016 in the paint samples. A TCLP extraction was also conducted on one of the samples to evaluate the paint's hazardous waste characteristics. Results show the paint exhibits elevated TCLP lead levels, requiring special handling and disposal.
The Chandler Bridge project aims to modify the bridge operators house to allow for safe operation and maintenance of the control panel. This is a state and local contract opportunity in Coos County, Oregon. No other details about the project scope, timeline, or procurement process are provided in this analytical report.
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| 35797 ITB.docx | DOCX document | |
| ATT B Plans~12.pdf | ||
| Attachment 1_System Requirements.pdf | ||
| Preliminary Results~50.xlsx | XLSX spreadsheet | |
| ATT A Special Provisions and Specifications~19.pdf |
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ANALYTICAL REPORT
March 14 , 2022
Oregon Dept of Transportation - ODOT
Sample Delivery Group: L1464514
Samples Received: 02/23/2022
Project Number:
Description: Chandler Bridge
Report To: Kenny Camp
6000 SW Raab Road
Portland, OR 97221
Entire Report Reviewed By:
March 14 , 2022
[Preliminary Report]
Brian Ford Pro ject Manager
Results relate only to the items tested or calibrated and are reported as rounded values. This test report shall not be reproduced, except in full, without written approval of the laboratory. Where applicable, sampling conducted by Pace Analytical National is performed per guidance provided in laboratory standard operating procedures ENV-SOP-MTJL-0067 and ENV-SOP-MTJL-0068. Where sampling conducted by the customer, results relate to the accuracy of the information provided, and as the samples are received.
Pace Analytical National 12065 Lebanon Rd Mount Ju l ie t , TN 37122 615 -758-5858 800-767-5859 www.pacenat iona l . com
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March 14 , 2022
Jason Romer Pro ject Manager
ACCOUNT: PROJECT: SDG: DATE/TIME: PAGE:
Oregon Dept of Transportation - ODOT L1464514 03/14/22 15:49 1 of 12 https://www.pacenational.com mailto:kenny.l.camp@odot.state.or.us?subject=Pace Analytical National SDG: L1464514&body=Email regarding SDG: L1464514 mailto:brian.ford@pacelabs.com?subject=Pace Analytical National SDG: L1464514&body=Email regarding SDG: L1464514 https://www.pacenational.com mailto:jason.romer@pacelabs.com?subject=Pace Analytical National SDG: L1464514&body=Email regarding SDG: L1464514
TABLE OF CONTENTS
Cp: Cover Page 1
Tc: Table of Contents 2
Ss: Sample Summary 3
Cn: Case Narrative 4
Sr: Sample Results 5
BRIDGE PAINT L1464514-01 5
BRIDGE PAINT L1464514-02 6
Qc: Quality Control Summary 7
Metals (ICP) by Method 6010D 7
Polychlorinated Biphenyls (GC) by Method 8082 A 9
Gl: Glossary of Terms 10
Al: Accreditations & Locations 11
Sc: Sample Chain of Custody 12
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SAMPLE SUMMARY
Collected by Collected date/time Received date/time
BRIDGE PAINT L1464514-01 PAINT Kenny Camp 02/15/22 09:00 02/23/22 09:00
Method Batch Dilution Preparation Analysis Analyst Location date/time date/time
Metals (ICP) by Method 6010D WG1822938 1 02/28/22 15:12 03/03/22 12:30 ZSA Mt. Juliet, TN
Metals (ICP) by Method 6010D WG1822938 10 02/28/22 15:12 03/03/22 13:26 ZSA Mt. Juliet, TN
Polychlorinated Biphenyls (GC) by Method 8082 A WG1829739 13.8 03/10/22 04:11 03/10/22 16:50 AMM Mt. Juliet, TN
Collected by Collected date/time Received date/time
BRIDGE PAINT L1464514-02 Waste Kenny Camp 02/15/22 09:00 02/23/22 09:00
Method Batch Dilution Preparation Analysis Analyst Location date/time date/time
Preparation by Method 1311 WG1823564 1 02/28/22 09:33 02/28/22 09:33 JWS Mt. Juliet, TN
Metals (ICP) by Method 6010D WG1825606 1 03/02/22 12:32 03/02/22 15:33 CCE Mt. Juliet, TN
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CASE NARRATIVE
All sample aliquots were received at the correct temperature, in the proper containers, with the appropriate preservatives, and within method specified holding times, unless qualified or notated within the report. Where applicable, all MDL (LOD) and RDL (LOQ) values reported for environmental samples have been corrected for the dilution factor used in the analysis. All Method and Batch Quality Control are within established criteria except where addressed in this case narrative, a non-conformance form or properly qualified within the sample results. By my digital signature below, I affirm to the best of my knowledge, all problems/anomalies observed by the laboratory as having the potential to affect the quality of the data have been identified by the laboratory, and no information or data have been knowingly withheld that would affect the quality of the data.
[Preliminary Report]
Brian Ford Pro jec t Manager
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Oregon Dept of Transportation - ODOT L1464514 03/14/22 12:54 4 of 12
Jason Romer Pro jec t Manager
ACCOUNT: PROJECT: SDG: DATE/TIME: PAGE:
Oregon Dept of Transportation - ODOT L1464514 03/14/22 15:49 4 of 12 mailto:brian.ford@pacelabs.com?subject=Pace Analytical National SDG: L1464514&body=Email regarding SDG: L1464514 mailto:jason.romer@pacelabs.com?subject=Pace Analytical National SDG: L1464514&body=Email regarding SDG: L1464514
SAMPLE RESULTS - 01
L 1 4 6 4 5 1 4
BRIDGE PAINT
C o l l e c t e d d a t e / t i m e : 0 2 / 1 5 / 2 2 0 9 : 0 0
Metals (ICP) by Method 6010D
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/kg ug/kg ug/kg date / time
Cadmium 1220 81.0 498 1 03/03/2022 12:30 WG1822938
Chromium 4570000 250 995 1 03/03/2022 12:30 WG1822938
Lead 248000000 2080 4980 10 03/03/2022 13:26 WG1822938
Polychlorinated Biphenyls (GC) by Method 8082 A
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte mg/kg mg/kg mg/kg date / time
PCB 1016 U 0.163 0.469 13.8 03/10/2022 16:50 WG1829739
PCB 1221 U 0.163 0.469 13.8 03/10/2022 16:50 WG1829739
PCB 1232 U 0.163 0.469 13.8 03/10/2022 16:50 WG1829739
PCB 1242 U 0.163 0.469 13.8 03/10/2022 16:50 WG1829739
PCB 1248 U 0.102 0.235 13.8 03/10/2022 16:50 WG1829739
PCB 1254 U 0.102 0.235 13.8 03/10/2022 16:50 WG1829739
PCB 1260 U 0.102 0.235 13.8 03/10/2022 16:50 WG1829739
(S) Decachlorobiphenyl 94.2 10.0-135 03/10/2022 16:50 WG1829739
(S) Tetrachloro-m-xylene 83.8 10.0-139 03/10/2022 16:50 WG1829739
Sample Narrative:
L1464514-01 WG1829739: Dilution due to matrix impact during extraction procedure
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SAMPLE RESULTS - 02
L 1 4 6 4 5 1 4
BRIDGE PAINT
C o l l e c t e d d a t e / t i m e : 0 2 / 1 5 / 2 2 0 9 : 0 0
Preparation by Method 1311
Result Qualifier Prep Batch
Analyte date / time
TCLP Extraction - 2/28/2022 9:33:17 AM WG1823564
Fluid 1 2/28/2022 9:33:17 AM WG1823564
Initial pH 8.02 2/28/2022 9:33:17 AM WG1823564
Final pH 5.00 2/28/2022 9:33:17 AM WG1823564
Metals (ICP) by Method 6010D
Result Qualifier RDL Limit Dilution Analysis Batch
Analyte mg/l mg/l mg/l date / time
Cadmium ND 0.100 1 1 03/02/2022 15:33 WG1825606
Chromium 0.218 0.100 5 1 03/02/2022 15:33 WG1825606
Lead 46.4 0.100 5 1 03/02/2022 15:33 WG1825606
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QUALITY CONTROL SUMMARYWG1822938
M e t a l s ( I C P ) b y M e t h o d 6 0 1 0 D L 1 4 6 4 5 1 4 - 0 1
Method Blank (MB)
(MB) R3765554-1 03/01/22 18:49
MB Result MB Qualifier MB MDL MB RDL
Analyte ug/kg ug/kg ug/kg
Cadmium U 81.0 500
Chromium U 250 1000
Method Blank (MB)
(MB) R3765554-2 03/01/22 18:52
MB Result MB Qualifier MB MDL MB RDL
Analyte ug/kg ug/kg ug/kg
Lead 1000 208 500
Laboratory Control Sample (LCS)
(LCS) R3765554-3 03/01/22 18:54
Spike Amount LCS Result LCS Rec. Rec. Limits LCS Qualifier
Analyte ug/kg ug/kg % %
Cadmium 100000 86500 86.5 80.0-120
Chromium 100000 89600 89.6 80.0-120
Laboratory Control Sample (LCS)
(LCS) R3765554-4 03/01/22 18:57
Spike Amount LCS Result LCS Rec. Rec. Limits LCS Qualifier
Analyte ug/kg ug/kg % %
Lead 604000 523000 86.7 80.0-120
L1465238-01 Original Sample (OS) • Matrix Spike (MS) • Matrix Spike Duplicate (MSD)
(OS) L1465238-01 03/01/22 19:00 • (MS) R3765554-7 03/01/22 19:08 • (MSD) R3765554-8 03/01/22 19:10
Spike Amount Original Result MS Result MSD Result MS Rec. MSD Rec. Dilution Rec. Limits MS Qualifier MSD Qualifier RPD RPD Limits
Analyte ug/kg ug/kg ug/kg ug/kg % % % % %
Cadmium 463000 U 420000 409000 90.7 82.4 1 75.0-125 2.77 25
Chromium 463000 7320 427000 417000 92.3 84.1 1 75.0-125 2.37 25
Lead 463000 304000 483000 510000 38.8 41.5 1 75.0-125 J6 J6 5.36 25
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QUALITY CONTROL SUMMARYWG1825606
M e t a l s ( I C P ) b y M e t h o d 6 0 1 0 D L 1 4 6 4 5 1 4 - 0 2
Method Blank (MB)
(MB) R3765658-1 03/02/22 14:18
MB Result MB Qualifier MB MDL MB RDL
Analyte mg/l mg/l mg/l
Cadmium U 0.0333 0.100
Chromium U 0.0333 0.100
Lead U 0.0333 0.100
Laboratory Control Sample (LCS)
(LCS) R3765658-2 03/02/22 14:21
Spike Amount LCS Result LCS Rec. Rec. Limits LCS Qualifier
Analyte mg/l mg/l % %
Cadmium 10.0 9.40 94.0 80.0-120
Chromium 10.0 9.30 93.0 80.0-120
Lead 10.0 9.47 94.7 80.0-120
L1464206-01 Original Sample (OS) • Matrix Spike (MS) • Matrix Spike Duplicate (MSD)
(OS) L1464206-01 03/02/22 14:24 • (MS) R3765658-4 03/02/22 14:30 • (MSD) R3765658-5 03/02/22 14:32
Spike Amount Original Result MS Result MSD Result MS Rec. MSD Rec. Dilution Rec. Limits MS Qualifier MSD Qualifier RPD RPD Limits
Analyte mg/l mg/l mg/l mg/l % % % % %
Cadmium 10.0 ND 9.55 9.60 95.5 96.0 1 75.0-125 0.498 20
Chromium 10.0 ND 9.41 9.47 94.1 94.7 1 75.0-125 0.680 20
Lead 10.0 ND 9.63 9.71 96.3 97.1 1 75.0-125 0.914 20
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QUALITY CONTROL SUMMARYWG1829739
P o l y c h l o r i n a t e d B i p h e n y l s ( G C ) b y M e t h o d 8 0 8 2 A L 1 4 6 4 5 1 4 - 0 1
Method Blank (MB)
(MB) R3768718-1 03/10/22 14:56
MB Result MB Qualifier MB MDL MB RDL
Analyte mg/kg mg/kg mg/kg
PCB 1016 U 0.0118 0.0340
PCB 1221 U 0.0118 0.0340
PCB 1232 U 0.0118 0.0340
PCB 1242 U 0.0118 0.0340
PCB 1248 U 0.00738 0.0170
PCB 1254 U 0.00738 0.0170
PCB 1260 U 0.00738 0.0170
(S) Decachlorobiphenyl 80.8 10.0-135
(S) Tetrachloro-m-xylene 85.7 10.0-139
Laboratory Control Sample (LCS)
(LCS) R3768718-2 03/10/22 15:15
Spike Amount LCS Result LCS Rec. Rec. Limits LCS Qualifier
Analyte mg/kg mg/kg % %
PCB 1016 0.167 0.151 90.4 36.0-141
PCB 1260 0.167 0.130 77.8 37.0-145
(S) Decachlorobiphenyl 70.1 10.0-135
(S) Tetrachloro-m-xylene 88.0 10.0-139
L1468244-02 Original Sample (OS) • Matrix Spike (MS) • Matrix Spike Duplicate (MSD)
(OS) L1468244-02 03/10/22 18:53 • (MS) R3768718-3 03/10/22 19:22 • (MSD) R3768718-4 03/10/22 19:31
Spike Amount Original Result MS Result MSD Result MS Rec. MSD Rec. Dilution Rec. Limits MS Qualifier MSD Qualifier RPD RPD Limits
Analyte mg/kg mg/kg mg/kg mg/kg % % % % %
PCB 1016 0.167 U 0.353 0.285 211 171 1 10.0-160 J5 P J5 P 21.3 37
PCB 1260 0.167 U 0.0773 0.0810 46.3 48.5 1 10.0-160 4.67 38
(S) Decachlorobiphenyl 51.5 59.6 10.0-135
(S) Tetrachloro-m-xylene 56.0 51.4 10.0-139
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GLOSSARY OF TERMS
Guide to Reading and Understanding Your Laboratory Report
The information below is designed to better explain the various terms used in your report of analytical results from the Laboratory. This is not intended as a comprehensive explanation, and if you have additional questions please contact your project representative.
Results Disclaimer - Information that may be provided by the customer, and contained within this report, include Permit Limits, Project Name, Sample ID, Sample Matrix, Sample Preservation, Field Blanks, Field Spikes, Field Duplicates, On-Site Data, Sampling Collection Dates/Times, and Sampling Location. Results relate to the accuracy of this information provided, and as the samples are received.
Abbreviations and Definitions
MDL Method Detection Limit.
ND Not detected at the Reporting Limit (or MDL where applicable).
RDL Reported Detection Limit.
Rec. Recovery.
RPD Relative Percent Difference.
SDG Sample Delivery Group.
(S) Surrogate (Surrogate Standard) - Analytes added to every blank, sample, Laboratory Control Sample/Duplicate and Matrix Spike/Duplicate; used to evaluate analytical efficiency by measuring recovery. Surrogates are not expected to be detected in all environmental media.
U Not detected at the Reporting Limit (or MDL where applicable).
Analyte The name of the particular compound or analysis performed. Some Analyses and Methods will have multiple analytes reported.
Dilution
If the sample matrix contains an interfering material, the sample preparation volume or weight values differ from the standard, or if concentrations of analytes in the sample are higher than the highest limit of concentration that the laboratory can accurately report, the sample may be diluted for analysis. If a value different than 1 is used in this field, the result reported has already been corrected for this factor.
Limits These are the target % recovery ranges or % difference value that the laboratory has historically determined as normal for the method and analyte being reported. Successful QC Sample analysis will target all analytes recovered or duplicated within these ranges.
Original Sample The non-spiked sample in the prep batch used to determine the Relative Percent Difference (RPD) from a quality control sample. The Original Sample may not be included within the reported SDG.
Qualifier This column provides a letter and/or number designation that corresponds to additional information concerning the result reported. If a Qualifier is present, a definition per Qualifier is provided within the Glossary and Definitions page and potentially a discussion of possible implications of the Qualifier in the Case Narrative if applicable.
Result
The actual analytical final result (corrected for any sample specific characteristics) reported for your sample. If there was no measurable result returned for a specific analyte, the result in this column may state “ND” (Not Detected) or “BDL” (Below Detectable Levels). The information in the results column should always be accompanied by either an MDL (Method Detection Limit) or RDL (Reporting Detection Limit) that defines the lowest value that the laboratory could detect or report for this analyte.
Uncertainty (Radiochemistry) Confidence level of 2 sigma.
Case Narrative (Cn) A brief discussion about the included sample results, including a discussion of any non-conformances to protocol observed either at sample receipt by the laboratory from the field or during the analytical process. If present, there will be a section in the Case Narrative to discuss the meaning of any data qualifiers used in the report.
Quality Control Summary (Qc)
This section of the report includes the results of the laboratory quality control analyses required by procedure or analytical methods to assist in evaluating the validity of the results reported for your samples. These analyses are not being performed on your samples typically, but on laboratory generated material.
Sample Chain of Custody (Sc)
This is the document created in the field when your samples were initially collected. This is used to verify the time and date of collection, the person collecting the samples, and the analyses that the laboratory is requested to perform. This chain of custody also documents all persons (excluding commercial shippers) that have had control or possession of the samples from the time of collection until delivery to the laboratory for analysis.
Sample Results (Sr) This section of your report will provide the results of all testing performed on your samples. These results are provided by sample ID and are separated by the analyses performed on each sample. The header line of each analysis section for each sample will provide the name and method number for the analysis reported.
Sample Summary (Ss) This section of the Analytical Report defines the specific analyses performed for each sample ID, including the dates and times of preparation and/or analysis.
Qualifier Description
J5 The sample matrix interfered with the ability to make any accurate determination; spike value is high.
J6 The sample matrix interfered with the ability to make any accurate determination; spike value is low.
P RPD between the primary and confirmatory analysis exceeded 40%.
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Pace Analytical National 12065 Lebanon Rd Mount Juliet, TN 37122 Alabama 40660 Nebraska NE-OS-15-05
Alaska 17-026 Nevada TN000032021-1
Arizona AZ0612 New Hampshire 2975
Arkansas 88-0469 New Jersey–NELAP TN002
California 2932 New Mexico ¹ TN00003
Colorado TN00003 New York 11742
Connecticut PH-0197 North Carolina Env375
Florida E87487 North Carolina ¹ DW21704
Georgia NELAP North Carolina ³ 41
Georgia ¹ 923 North Dakota R-140
Idaho TN00003 Ohio–VAP CL0069
Illinois 200008 Oklahoma 9915
Indiana C-TN-01 Oregon TN200002
Iowa 364 Pennsylvania 68-02979
Kansas E-10277 Rhode Island LAO00356
Kentucky ¹ ⁶ KY90010 South Carolina 84004002
Kentucky ² 16 South Dakota n/a
Louisiana AI30792 Tennessee ¹ ⁴ 2006
Louisiana LA018 Texas T104704245-20-18
Maine TN00003 Texas ⁵ LAB0152
Maryland 324 Utah TN000032021-11
Massachusetts M-TN003 Vermont VT2006
Michigan 9958 Virginia 110033
Minnesota 047-999-395 Washington C847
Mississippi TN00003 West Virginia 233
Missouri 340 Wisconsin 998093910
Montana CERT0086 Wyoming A2LA
A2LA – ISO 17025 1461.01 AIHA-LAP,LLC EMLAP 100789
A2LA – ISO 17025 ⁵ 1461.02 DOD 1461.01
Canada 1461.01 USDA P330-15-00234
EPA–Crypto TN00003
ACCREDITATIONS & LOCATIONS
¹ Drinking Water ² Underground Storage Tanks ³ Aquatic Toxicity ⁴ Chemical/Microbiological ⁵ Mold ⁶ Wastewater n/a Accreditation not applicable
* Not all certifications held by the laboratory are applicable to the results reported in the attached report.
* Accreditation is only applicable to the test methods specified on each scope of accreditation held by Pace Analytical.
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| Cp: Cover Page |
| Tc: Table of Contents |
| Ss: Sample Summary |
| Cn: Case Narrative |
| Sr: Sample Results |
| BRIDGE PAINT L1464514-01 |
| Metals (ICP) by Method 6010D |
| Polychlorinated Biphenyls (GC) by Method 8082 A |
| BRIDGE PAINT L1464514-02 |
| Preparation by Method 1311 |
| Metals (ICP) by Method 6010D |
| Qc: Quality Control Summary |
| Metals (ICP) by Method 6010D |
| WG1822938 |
| WG1825606 |
| Polychlorinated Biphenyls (GC) by Method 8082 A |
| WG1829739 |
| Gl: Glossary of Terms |
| Al: Accreditations & Locations |
| Sc: Sample Chain of Custody |
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| 645776_btnQ-2-3-2: |
| 645776_btnQ-2-11-2: |
| 645776_btnQ-5-18-5: |
| 645776_btnQ-5-26-5: |
| 645776_btnQ-9;10-33-9: |
| 645776_btnQ-9;10-33-10: |
| 645776_btn-9;10-38-9: |
| 645776_btn-9;10-38-10: |
| 645776_btnNav-Cp7: |
| 645776_btnNav-Tc7: |
| 645776_btnNav-Ss7: |
| 645776_btnNav-Cn7: |
| 645776_btnNav-Sr7: |
| 645776_btnNav-Qc7: |
| 645776_btnNav-Gl7: |
| 645776_btnNav-Al7: |
| 645776_btnNav-Sc7: |
| 645776_btnQ-2-42-2: |
| 645776_btnQ-5-51-5: |
| 645776_btnQ-9;10-60-9: |
| 645776_btnQ-9;10-60-10: |
| 645776_btnNav-Cp8: |
| 645776_btnNav-Tc8: |
| 645776_btnNav-Ss8: |
| 645776_btnNav-Cn8: |
| 645776_btnNav-Sr8: |
| 645776_btnNav-Qc8: |
| 645776_btnNav-Gl8: |
| 645776_btnNav-Al8: |
| 645776_btnNav-Sc8: |
| 645776_btnQ-2-69-2: |
| 645776_btnQ-5-84-5: |
| 645776_btnQ-9;10-94-9: |
| 645776_btnQ-9;10-94-10: |
| 645776_btn-9;10-97-9: |
| 645776_btn-9;10-97-10: |
| 645776_btnNav-Cp9: |
| 645776_btnNav-Tc9: |
| 645776_btnNav-Ss9: |
| 645776_btnNav-Cn9: |
| 645776_btnNav-Sr9: |
| 645776_btnNav-Qc9: |
| 645776_btnNav-Gl9: |
| 645776_btnNav-Al9: |
| 645776_btnNav-Sc9: |
| 645776_btnNav-Cp10: |
| 645776_btnNav-Tc10: |
| 645776_btnNav-Ss10: |
| 645776_btnNav-Cn10: |
| 645776_btnNav-Sr10: |
| 645776_btnNav-Qc10: |
| 645776_btnNav-Gl10: |
| 645776_btnNav-Al10: |
| 645776_btnNav-Sc10: |
| 645776_btnNav-Cp11: |
| 645776_btnNav-Tc11: |
| 645776_btnNav-Ss11: |
| 645776_btnNav-Cn11: |
| 645776_btnNav-Sr11: |
| 645776_btnNav-Qc11: |
| 645776_btnNav-Gl11: |
| 645776_btnNav-Al11: |
| 645776_btnNav-Sc11: |
File details come from the government source that posted it. Updated .