Information_Handout_-_Asbestos-Containing_Materials_and_Lead-Containing_Paint_Survey_Report.pdf
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- Sacramento County, San Francisco City, California
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This is an Asbestos-Containing Materials and Lead-Containing Paint Survey Report prepared by Geocon Consultants, Inc. for Parikh Consultants on behalf of Mark Thomas and Company and the County of Sacramento in support of the State Route 50/Hazel Avenue Interchange Improvement Project. The survey assessed two structures—the Alder Creek Bridge sidewall and the Hazel Avenue Bridge—for the presence of asbestos-containing materials (ACM), lead-containing paint (LCP), and chromium-containing paint (CCP) prior to renovation activities. The investigation was conducted on April 7, 2026, by certified professionals and included collection of 19 bulk asbestos samples representing eight suspect materials and four bulk paint samples. Samples were submitted to EMSL Analytical, Inc. for asbestos analysis using polarized light microscopy and to Asset Laboratories for lead and chromium analysis using EPA Test Method 6010B. The survey findings indicate that asbestos was not detected in any of the collected samples from either structure.
The paint analysis results identified low concentrations of lead and chromium in intact paint samples collected from both bridge locations. At the Alder Creek Bridge sidewall, total lead was reported at 3.5 mg/kg in white traffic striping and below the reporting limit in beige-gray graffiti abatement paint; at the Hazel Avenue Bridge, total lead was reported at 6.6 mg/kg in white traffic striping and 17 mg/kg in gray graffiti abatement paint. None of the analyzed paint samples were classified as California or Federal (RCRA) hazardous waste based on lead or chromium content when intact. The report recommends that all paints at the site be considered hazardous based on historical lead content unless further testing by contractors indicates otherwise, and notes that written notification to the Sacramento Metropolitan Air Quality Management District and Cal/OSHA district office is required prior to demolition and lead-related work activities. The survey limitations note that concealed materials in cavities, voids, and inaccessible areas may not have been identified, and recommend additional sampling if suspect materials are uncovered during renovation or demolition operations.
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AUGUST 2026
PREPARED FOR:
PARIKH CONSULTANTS
1497 NORTH MILPITAS BOULEVARD
MILPITAS, CALIFORNIA 95035
PREPARED BY:
GEOCON CONSULTANTS, INC.
6671 BRISA STREET
LIVERMORE, CALIFORNIA 94550
GEOCON PROJECT NO. E9453-02-01
ASBESTOS-CONTAINING MATERIALS AND
LEAD-CONTAINING PAINT
SURVEY REPORT
State Route 50/Hazel Avenue Interchange Improvement Project
Sacramento, California
Project No. E9453-02-01 August 5, 2026
Parikh Consultants 1497 North Milpitas Boulevard Milpitas, California 95035
Attention: Gary Parikh
Subject: ASBESTOS-CONTAINING MATERIALS AND LEAD-CONTAINING PAINT SURVEY REPORT
STATE ROUTE 50/HAZEL AVENUE INTERCHANGE IMPROVEMENT PROJECT
ALDER CREEK BRIDGE SIDEWALL AND HAZEL AVENUE BRIDGE
SACRAMENTO, CALIFORNIA
Mr. Parikh:
In accordance with your authorization and on behalf of Mark Thomas and Company and County of Sacramento, Geocon Consultants, Inc. has performed an asbestos-containing materials and lead-containing paint survey in support of the State Route 50/Hazel Avenue Interchange Improvement Project. Our scope of services included surveying the structure for suspect asbestos-containing materials and lead- or chromium-containing paint, collecting bulk samples, and submitting the samples to laboratories for analyses.
The accompanying report summarizes the services performed and laboratory analysis.
The contents of this report reflect the views of Geocon Consultants, Inc., who are responsible for the facts and accuracy of the data presented herein. This report does not constitute a standard, specification, or regulation.
Please contact us if you have questions concerning the contents of this report or if we may be of further service.
Sincerely, Geocon Consultants, Inc.
Nicholas Rice, CAC No. 24-7578 Cord Dennig, CAC No. 21-6915 Project Scientist Senior Project Scientist
SR-50 / Hazel Avenue Interchange Improvement Project Asbestos-Containing Materials and Lead-Containing Paint Survey Report
TABLE OF CONTENTS
ASBESTOS-CONTAINING MATERIALS AND LEAD-CONTAINING PAINT SURVEY REPORT PAGE
1.0 INTRODUCTION
1.1 Project Description
1.2 General Objectives
2.0 BACKGROUND
2.1 Asbestos
2.2 Lead and Chromium
3.0 SCOPE OF SERVICES
3.1 Asbestos
3.2 Lead and Chromium
4.0 INVESTIGATIVE RESULTS
4.1 Asbestos
4.2 Lead Paint
4.2.1 Alder Creek Bridge Sidewall
4.2.2 Hazel Avenue Bridge
5.0 RECOMMENDATIONS
5.1 Asbestos
5.2 Lead Paint
5.2.1 Alder Creek Bridge Sidewall
5.2.2 Hazel Avenue Bridge
6.0 REPORT LIMITATIONS
FIGURES
1. Site Location Map
2. Site Plan - Alder Creek Bridge Sidewall
3. Site Plan - Hazel Avenue Bridge
PHOTOGRAPHS 1 through 8
TABLES
1. Summary of Laboratory Analytical Results – Asbestos
2. Summary of Laboratory Analytical Results – Paint
APPENDICES
A. Personnel Certifications B. Analytical Laboratory Reports and Chain-of-custody Documentation
SR-50/Hazel Avenue Interchange Improvement Project
Geocon Project Number E9453-02-01 1 - August 5, 2026
ASBESTOS-CONTAINING MATERIALS AND LEAD-CONTAINING PAINT
SURVEY REPORT
1.0 INTRODUCTION
We performed an asbestos-containing material (ACM), lead-containing paint (LCP), and chromium-containing paint (CCP) survey of the Alder Creek bridge sidewall along State Route 50 (SR-50) and the Hazel Avenue Bridge over SR-50 in support of the SR-50/Hazel Avenue Interchange Improvement Project for Parikh Consultants (Parikh) on behalf of Mark Thomas and Company and the County of Sacramento.
1.1 Project Description
We surveyed the Alder Creek Bridge sidewall and Hazel Avenue Bridge for suspect ACM, LCP, and CCP in Sacramento, California as requested by Mark Thomas. The project location is depicted on the Site Location Map (Figure 1), Site Plans (Figure 2 and Figure 3), and shown in the attached photographs.
1.2 General Objectives
The purpose of the scope of services was to determine the presence and quantity of asbestos, deteriorated LCP, and CCP at the bridge and wall structure prior to renovations. The information obtained from this investigation will be used by Mark Thomas and the City of Sacramento for waste profiling, determining Division of Occupational Safety and Health Administration (DOSH) also known as (Cal/OSHA) applicability, and coordinating asbestos and LCP disturbance activities.
It was not Geocon’s intent during this inspection to conduct an evaluation of lead-based paint hazards in accordance with U.S. Department of Housing and Urban Development (HUD) guidelines.
2.0 BACKGROUND
2.1 Asbestos
The Code of Federal Regulations (CFR), 40 CFR 61, Subpart M, National Emissions Standards for
Hazardous Air Pollutants (NESHAP) and Federal Occupational Safety and Health Administration (FED OSHA) classify asbestos-containing material (ACM) as any material or product that contains greater than 1% asbestos. Nonfriable ACM is classified by NESHAP as either Category I or Category II material defined as follows:
Geocon Project Number E9453-02-01 2 - August 5, 2026
Category I – asbestos-containing packings, gaskets, resilient floor coverings, and asphalt roofing products.
Category II – all remaining types of nonfriable asbestos-containing material not included in Category I that when dry, cannot be crumbled, pulverized, or reduced to powder by hand pressure.
Regulated asbestos-containing material (RACM), a California hazardous waste when friable, is classified as any manufactured material that contains greater than 1% asbestos by dry weight and is:
• Friable (can be crumbled, pulverized, or reduced to powder by hand pressure); or
• Category I material that has become friable; or
• Category I material that has been subjected to sanding, grinding, cutting, or abrading; or
• Category II nonfriable material that has a high probability of becoming crumbled, pulverized, or reduced to a powder during demolition or renovation activities.
Activities that disturb materials containing any amount of asbestos are subject to certain requirements of the Cal/OSHA asbestos standard contained in Title 8 of the California Code of Regulations (CCR) §1529. Typically, removal or disturbance of more than 100 square feet of material containing more than 0.1% asbestos must be performed by a registered asbestos abatement contractor, but associated waste labeling is not required if the material contains 1% or less asbestos. When the asbestos content of a material exceeds 1%, virtually all requirements of the standard become effective.
Materials containing more than 1% asbestos are also subject to NESHAP regulations (40 CFR Part 61, Subpart M). RACM (friable ACM and nonfriable ACM that will become friable during demolition operations) must be removed from structures prior to demolition. Certain nonfriable ACM and materials containing 1% or less asbestos may remain in structures during demolition; however, there are waste handling/disposal issues and Cal/OSHA work requirements that must be addressed.
Contractors are responsible for segregating and characterizing waste streams prior to disposal.
With respect to potential worker exposure, notification, and registration requirements, Cal/OSHA defines asbestos-containing construction material (ACCM) as construction material that contains more than 0.1% asbestos (Title 8, CCR 341.6).
2.2 Lead and Chromium
Construction activities (including demolition) that disturb materials or paints containing any amount of lead are subject to certain requirements of the Cal/OSHA lead standard contained in Title 8, CCR, Section 1532.1. Deteriorated paint is defined by Title 17, CCR, Division 1, Chapter 8, §35022 as a surface
Geocon Project Number E9453-02-01 3 - August 5, 2026 coating that is cracking, chalking, flaking, chipping, peeling, non-intact, failed, or otherwise separating from a substrate. Demolition of a deteriorated lead- and chromium-containing paint component would require waste characterization and appropriate disposal. Intact lead- and chromium-containing paint on a component is currently accepted by most landfills and recycling facilities; however, contractors are responsible for segregating and characterizing waste streams prior to disposal.
For a solid waste containing lead, the waste is classified as California hazardous when: 1) the total lead content equals or exceeds the respective Total Threshold Limit Concentration (TTLC) of 1,000 milligrams per kilogram (mg/kg); or 2) the soluble lead content equals or exceeds the respective
Soluble Threshold Limit Concentration (STLC) of 5 milligrams per liter (mg/l) based on the standard Waste Extraction Test (WET). The soluble lead concentration of a waste has the potential to exceed the lead STLC when the waste’s total lead concentration is greater than or equal to 10 times the respective STLC value since the WET uses a 1:10 dilution ratio. Hence, when total lead is detected at a concentration greater than or equal to 50 mg/kg, and assuming that 100 percent of the total lead is soluble, soluble lead analysis is required. Lead-containing waste is classified as “Resource, Conservation, and Recovery Act” (RCRA) hazardous, or Federal hazardous, when its soluble lead concentration equals or exceeds the Federal regulatory level of 5 mg/l based on the Toxicity Characteristic Leaching Procedure (TCLP).
For a solid waste containing chromium, the waste is classified as California hazardous when: 1) the total chromium content equals or exceeds the respective TTLC of 2,500 mg/kg; or 2) the soluble chromium content equals or exceeds the respective STLC of 5 mg/l based on the standard WET. The soluble chromium concentration of a waste has the potential to exceed the chromium STLC when the waste’s total chromium concentration is greater than or equal to 10 times the respective STLC value since the WET uses a 1:10 dilution ratio. Hence, when total chromium is detected at a concentration greater than or equal to 50 mg/kg, and assuming that 100 percent of the total chromium is soluble, soluble chromium analysis is required. Chromium-containing waste is classified as RCRA hazardous, or Federal hazardous, when its soluble chromium concentration equals or exceeds the Federal regulatory level of 5 mg/l based on the TCLP.
The above regulatory criteria are based on chemical concentrations. Wastes may also be classified as hazardous based on other criteria such as ignitability; however, for the purposes of this investigation, toxicity (i.e., lead concentrations) is the primary factor considered for waste classification since waste generated during the construction activities would not likely warrant testing for ignitability or other criteria. Waste that is classified as either California hazardous or RCRA hazardous requires management as a hazardous waste.
Geocon Project Number E9453-02-01 4 - August 5, 2026
Potential hazards exist to workers who remove or cut through LCP and chromium-containing paints and coatings during demolition. Dust containing hazardous concentrations of lead may be generated during scraping or cutting materials coated with lead- and chromium-containing paint. Torching of these materials may produce lead oxide fumes. Therefore, air monitoring and/or respiratory protection may be required during the disturbance of materials coated with lead- and chromium-containing paint.
Guidelines regarding regulatory provisions for construction work where workers may be exposed to lead are in Title 8, CCR, §1532.1.
3.0 SCOPE OF SERVICES
Nick Rice and Cord Dennig performed the survey on April 7, 2026. Mr. Rice is a California-Certified Asbestos Consultant (CAC), Certification Number 24-7578, and Certified Lead Paint Inspector/Assessor with the California Department of Public Health (CDPH), Certification Number LRC-13870. Cord Dennig reviewed this report. Mr. Dennig is a California-CAC, Certification Number 21-6915, and a Certified Lead Paint Inspector/Assessor and Certified Lead Paint Project Monitor with the CDPH, Certification Numbers LRC-2374 and LRC-12229. Copies of Messrs. Rice’s and Dennig’s Cal/OSHA CAC and CDPH certification cards are in Appendix A.
3.1 Asbestos
We grouped suspect ACM at the project location into homogeneous areas with representative samples randomly collected from each. In addition, we evaluated each potential ACM for friability. We collected 19 bulk samples representing eight suspect materials at the project locations.
Our procedures for inspection and sampling were as follows:
• Collected bulk asbestos samples after wetting friable materials with a light mist of water.
The samples were then removed from the substrate and transferred to labeled containers. Note that when we collected multiple samples, we distributed the sampling locations throughout the homogeneous area (spaces where the material was observed).
• Relinquished bulk asbestos samples under chain-of-custody protocol to EMSL Analytical, Inc.
(EMSL), a California-licensed subcontractor, for asbestos analysis in accordance with United States Environmental Protection Agency (EPA) Test Method 600/R-93/116 using polarized light microscopy (PLM). EMSL is a laboratory accredited by the National Institute of Standards and Technology National Voluntary Laboratory Accreditation Program (NVLAP) (NVLAP Certification Number 200232-0) for bulk asbestos fiber analysis. We requested the laboratory analyses on a one-week turnaround time.
Sample identification numbers, material descriptions, approximate quantities, friability assessments, and photo references are summarized in Table 1. Approximate sample locations are depicted on Figures 2 and 3. Materials represented by the samples collected are shown in the attached photographs.
Geocon Project Number E9453-02-01 5 - August 5, 2026
3.2 Lead and Chromium
We collected four bulk paint samples of suspect LCP and CCP observed at the project location. Our sampling procedures were as follows:
• Collected bulk samples of suspect LCP and CCP using techniques presented in HUD guidelines. In addition, we evaluated the painted areas for evidence of deterioration such as flaking or cracking.
• Relinquished the bulk samples under chain-of-custody protocol to Asset Laboratories (Asset), a California-licensed subcontractor, for total lead and chromium analysis in accordance with EPA Test Method 6010B. Additionally we requested that the paint samples be also analyzed for chromium in accordance with EPA Test Method 6010B. Asset is accredited by the California State Water Resources Control Board under the Environmental Laboratory Accreditation Program for lead and chromium analysis. We requested the laboratory analyses on a one-week turnaround time.
The sample identification numbers, descriptions, and photo references are summarized in Table 2. The approximate sample locations are depicted on Figures 2 and 3. Materials represented by the samples collected are shown in the attached photographs.
4.0 INVESTIGATIVE RESULTS
4.1 Asbestos
Asbestos was not observed in the samples of suspect materials collected during our survey of the Alder Creek sidewall or Hazel Avenue bridge structure. Analytical laboratory test results for asbestos are presented in Table 1. Copies of the laboratory report and chain-of-custody documentation are in Appendix B.
4.2 Lead Paint
4.2.1 Alder Creek Bridge Sidewall
Total lead was reported at a concentration of 3.5 mg/kg in a sample representing intact white traffic striping applied to the asphalt drive isle. Total chromium was reported at a concentration of 7.0 mg/kg in the same paint sample.
Total lead was not detected at a concentration at or exceeding the laboratory reporting limit (RL) of 5.0 mg/kg in a sample representing intact beige-gray graffiti abatement paint applied to bridge sidewall.
Total chromium was reported at a concentration of 14 mg/kg in the same paint sample.
Geocon Project Number E9453-02-01 6 - August 5, 2026
4.2.2 Hazel Avenue Bridge
Total lead was reported at a concentration of 6.6 mg/kg in a sample representing intact white traffic striping applied to the bridge deck. Total chromium was reported at a concentration of 2.5 mg/kg in the same paint sample.
Total lead was reported at a concentration of 17 mg/kg in a sample representing intact gray graffiti abatement paint applied to the bridge sidewalls. Total chromium was reported at a concentration of
110 mg/kg in the same paint sample, with a WET chromium concentration of 1.1 mg/l.
A summary of the analytical laboratory test results for paint is presented in Table 2. Copies of the laboratory reports and chain-of-custody documentation are in Appendix B.
5.0 RECOMMENDATIONS
Based on our findings, we recommend the following:
5.1 Asbestos
Since asbestos was not detected in samples of suspect material collected during our survey, the Cal/OSHA asbestos standard does not apply for planned activities involving materials sampled during our survey of the Alder Creek Bridge sidewall and Hazel Avenue bridge structure. In addition, construction debris would not be considered a California hazardous waste based on asbestos content.
Analytical laboratory test results for asbestos are presented in the report table. Copies of the laboratory report and chain-of-custody documentation are in Appendix B.
In accordance with NESHAP and Sacramento Metropolitan Air Quality Management District (SMAQMD), written notification to SMAQMD is required ten working days prior to commencement of any demolition activity (whether asbestos is present or not).
5.2 Lead Paint
Geocon recommends that all paints present at the site be considered hazardous based on lead content unless sampling and analytical testing by the paint removal contractor indicates otherwise. For the purpose of determining the applicability of the Cal/OSHA lead standard during maintenance, renovation, and demolition activities. This recommendation is based on LCP sample results and the fact that lead was a common ingredient of paints manufactured before 1978 and is still an ingredient of
Geocon Project Number E9453-02-01 7 - August 5, 2026 some paints. In accordance with Title 8, CCR, §1532.1(p), written notification to the nearest Cal/OSHA district office is required at least 24 hours prior to certain lead-related work. Compliance and training requirements regarding construction activities where workers may be exposed to lead are presented in Title 8, CCR, §1532.1, subsections I and (l), respectively. The removal, transportation, placement, handling, and disposal of LCP must result in no visible dust.
5.2.1 Alder Creek Bridge Sidewall
Intact white traffic striping applied to the asphalt drive isle and intact beige-gray paint applied to the sidewall would not be considered California or Federal (RCRA) hazardous waste based on lead or chromium content if stripped, blasted, or otherwise separated from the substrates.
5.2.2 Hazel Avenue Bridge
Intact white traffic striping applied to the bridge deck and intact gray paint applied to the sidewalls would not be considered California or Federal (RCRA) hazardous waste based on lead or chromium content if stripped, blasted, or otherwise separated from the substrates.
Geocon Project Number E9453-02-01 8 - August 5, 2026
6.0 REPORT LIMITATIONS
The asbestos and LCP survey was conducted in conformance with generally accepted standards of practice for identifying and evaluating asbestos and LCP in structures. The survey addressed only the structures identified in Section 1.1. Due to the nature of structure surveys, asbestos and LCP use, and laboratory analytical limitations, some ACM or LCP at the project location may not have been identified.
Spaces such as cavities, voids, crawlspaces, and pipe chases may have been concealed to our investigator. Previous renovation work may have concealed or covered spaces or materials or may have partially demolished materials and left debris in inaccessible areas. Additionally, renovation activities may have partially replaced ACM with indistinguishable non-ACM. Asbestos and/or LCP may exist in areas of the structures that were not accessible or sampled during this survey.
During renovation or demolition operations, suspect materials may be uncovered which are different from those accessible for sampling during this assessment. Personnel in charge of renovation/demolition should be alerted to note materials uncovered during such activities that differ substantially from those included in this or previous assessment reports. If suspect ACM and/or LCP are found, additional sampling and analysis should be performed to determine if the materials contain asbestos or lead.
This report has been prepared exclusively for Parikh, Mark Thomas, and the County of Sacramento. The information contained herein is only valid as of the date of the report and will require an update to reflect additional information obtained.
This report is not a comprehensive site characterization and should not be construed as such.
The findings as presented in this report are predicated on the results of the limited sampling and laboratory testing performed. In addition, the information obtained is not intended to address potential impacts related to sources other than those specified herein. Therefore, the report should be deemed conclusive with respect to only the information obtained. We make no warranty with respect to the content of this report or any subsequent reports, correspondence or consultation. Geocon strove to perform the services summarized herein in accordance with the local standard of care in the geographic region at the time the services were rendered.
The contents of this report reflect the views of the author who is responsible for the facts and accuracy of the data presented herein. This report does not constitute a standard, specification, or regulation.
FOLSOM
ORANGEVALE
Alder Creek Bridge (Br. No. 24-0033)
Prairie City Off Highway Vehicle Park
American River Parkway Sailor Bar Area
Folsom Lake State Recreation Area
Hazel Avenue Overcrossing (Br. No. 24-0168)
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CONSULTANTS, INC.
6 6 7 1 B R I S A S T R E E T - L I V E R M O R E , C A 9 4 5 5 0
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Figure 1August 2026E9453-02-01
SITE LOCATION MAP
Sacramento California
State Route 50/Hazel Avenue Interchange
H-1C
H-6A H-6B
H-3B
H-1A
H-2A
H-P1
H-5A
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Approximate Paint Sample Location (Lead Analysis)
CONSULTANTS, INC.
6 6 7 1 B R I S A S T R E E T - L I V E R M O R E , C A 9 4 5 5 0
P H O N E 9 2 5 . 3 7 1 . 5 9 0 0 - FA X 9 2 5 . 3 7 1 . 5 9 1 5
Figure 2August 2026E9453-02-01
SITE PLAN - HAZEL AVENUE
Sacramento California
Alder Creek
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Approximate Paint Sample Location (Lead Analysis)
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Figure 3August 2026E9453-02-01
SITE PLAN - ALDER CREEK
Sacramento California
Photo 1 – Alder Creek Wall along Highway 50 in Sacramento, California; concrete.
Photo 2 – Alder Creek Wall; concrete, asphalt, white traffic striping and gray graffiti abatement paint.
Photo 3 – Hazel Avenue Bridge in Sacramento, California; asphalt, concrete, and white traffic striping.
PHOTOGRAPHS 1, 2, & 3
State Route 50 / Hazel Avenue Interchange Improvement Project
State Route 50 Sacramento County, California
E9453-02-01 August 2026
Photo 4 – Hazel Avenue Bridge; concrete, and gray graffiti abatement paint.
Photo 5 – Hazel Avenue Bridge; concrete, asphalt, rubber joint seal.
Photo 6 – Hazel Avenue Bridge; brown fibrous joint fill.
PHOTOGRAPHS 4, 5, & 6
State Route 50 / Hazel Avenue Interchange Improvement Project
State Route 50
Photo 7 – Hazel Avenue Bridge; concrete, and gray graffiti abatement paint.
Photo 8 – Hazel Avenue Bridge; concrete, asphalt, rubber joint seal.
PHOTOGRAPHS 7 & 8
State Route 50 / Hazel Avenue Interchange Improvement Project
State Route 50
TABLE 1
SUMMARY OF ANALYTICAL LABORATORY TEST RESULTS - ASBESTOS
STATE ROUTE 50/HAZEL AVENUE INTERCHANGE IMPROVEMENT PROJECT
Polarized Light Microscopy (PLM) - EPA Test Method 600/R-93/116
Sample Group Description of Suspect Material Approximate Quantity Friable Site Photos Asbestos Content
Alder Creek Wall AC-1A-1C Concrete NA NA 1 & 2 ND AC-2A/B Asphalt NA NA 2 ND
Hazel Avenue Bridge H-1A-1D Concrete NA NA 3 - 8 ND H-2A/B Asphalt NA NA 3 & 5 ND H-3A/B Rubber joint seal NA NA 5 ND H-4A/B Brown fibrous joint fill NA NA 6 ND H-5A/B Sheet bearing material NA NA 7 ND H-6A/B Rubber conduit jacket NA NA 8 ND
Notes:
EPA = Environmental Protection Agency NA = Not applicable (asbestos not detected) ND = No asbestos fibers detected
SACRAMENTO COUNTY, CALIFORNIA
Geocon Project No. E9453-02-01 1 of 1 August 2026
TABLE 2
SUMMARY OF ANALYTICAL LABORATORY TEST RESULTS - PAINT
LEAD AND CHROMIUM
STATE ROUTE 50/HAZEL AVENUE INTERCHANGE IMPROVEMENT PROJECT
SACRAMENTO COUNTY, CALIFORNIA
Total and Soluble Lead and Chromium (EPA Test Method 6010B)
Sample No. Paint Description Approximate Quantity Peeling/Flaking Site Photo Total Lead
(mg/kg)
Total Chromium
(mg/kg)
WET
Chromium
(mg/l) Alder Creek Wall
AC-P1 White traffic striping Intact 2 3.5 7.0 --- AC-P2 Beige-gray graffiti abatement paint Intact 2 <5.0 14 ---
Hazel Avenue Bridge H-P1 White traffic striping Intact 3 & 5 6.6 2.5 --- H-P2 Gray graffiti abatement paint Intact 4 17 110 1.1
Notes:
mg/kg = milligrams per kilogram
EPA = Environmental Protection Agency WET = Waste Extraction Test mg/l = milligrams per liter
Geocon Project No. E9369-02-64 1 of 1 August 2026
APPENDIX A
STATE OF CALIFORNIA
DEPARTMENT OF PUBLIC HEALTH
LEAD-RELATED CONSTRUCTION CERTIFICATE
Disclaimer: This document alone should not be relied upon to confirm certification status. Compare the individual’s photo and name to another valid form of government issued photo identification. Verify the individual’s certification status by searching for Lead-Related Construction Professionals at www.cdph.ca.gov/programs/clppb or calling (800) 597-LEAD
INDIVIDUAL: CERTIFICATE TYPE: NUMBER: EXPIRATION DATE:
Lead Inspector/Assessor LRC-00002374 2/15/2027
Lead Project Monitor LRC-00012229 1/3/2027
Cord Dennig
APPENDIX B
LA Testing 520 Mission Street South Pasadena, CA 91030
Tel/Fax: (323) 254-9960 / (323) 254-9982 http://www.LATesting.com / pasadenalab@latesting.com
322608663LA Testing Order:
Customer ID: GECN21
Customer PO: E9453-02-01
Project ID:
Attention: Phone:Nick Rice (775) 685-6116
Fax:Geocon Consultants, Inc. (925) 371-5915
Received Date:6671 Brisa Street 04/07/2026 11:45 AM
Analysis Date:Livermore, CA 94550 04/15/2026
Collected Date:
Project: E9453-02-01 US-50/Hazel Avenue Bridges
Test Report: Asbestos Analysis of Bulk Materials via AHERA Method 40CFR 763 Subpart E
Appendix E supplemented with EPA 600/R-93/116 using Polarized Light Microscopy
Sample Description Appearance % Fibrous % Non-Fibrous
Non-Asbestos Asbestos
% Type
H-1A
322608663-0001
None DetectedNon-fibrous (Other)100%Gray
Non-Fibrous
Homogeneous
Concrete
H-1B
322608663-0002
None DetectedNon-fibrous (Other)100%Gray
Non-Fibrous
Homogeneous
Concrete
H-1C
322608663-0003
None DetectedNon-fibrous (Other)100%Gray
Non-Fibrous
Homogeneous
Concrete
H-1D
322608663-0004
None DetectedNon-fibrous (Other)100%Gray
Non-Fibrous
Homogeneous
Concrete
H-2A
322608663-0005
None DetectedNon-fibrous (Other)100%Gray/Black
Non-Fibrous
Homogeneous
Asphalt
H-2B
322608663-0006
None DetectedNon-fibrous (Other)100%Black
Non-Fibrous
Homogeneous
Asphalt
H-3A
322608663-0007
None DetectedNon-fibrous (Other)100%Black
Non-Fibrous
Homogeneous
Rubber Joint Seal
H-3B
322608663-0008
None DetectedNon-fibrous (Other)100%Black
Non-Fibrous
Homogeneous
Rubber Joint Seal
H-4A
322608663-0009
None DetectedNon-fibrous (Other)65%Cellulose35%Black
Fibrous
Homogeneous
Brown Fibrous Joint
Fill
H-4B
322608663-0010
None DetectedNon-fibrous (Other)100%Black
Non-Fibrous
Homogeneous
Brown Fibrous Joint
Fill
H-5A
322608663-0011
None DetectedNon-fibrous (Other)5%Cellulose95%Brown
Fibrous
Homogeneous
Sheet Bearing
Material
H-5B
322608663-0012
None DetectedNon-fibrous (Other)5%Cellulose95%Brown
Non-Fibrous
Homogeneous
Sheet Bearing
Material
H-6A
322608663-0013
None DetectedNon-fibrous (Other)100%Black
Non-Fibrous
Homogeneous
Rubber Condoit
Jacket
H-6B
322608663-0014
None DetectedNon-fibrous (Other)100%Black
Non-Fibrous
Homogeneous
Rubber Condoit
Jacket
AC-1A
322608663-0015
None DetectedNon-fibrous (Other)100%Gray
Non-Fibrous
Homogeneous
Concrete
AC-1B
322608663-0016
None DetectedNon-fibrous (Other)100%Gray
Non-Fibrous
Homogeneous
Concrete
Initial report from: 04/15/2026 11:20:31
Page 1 of 2ASB_PLM_0008_0002 - 2.31 Printed: 4/15/2026 11:21 AM
LA Testing 520 Mission Street South Pasadena, CA 91030
Tel/Fax: (323) 254-9960 / (323) 254-9982 http://www.LATesting.com / pasadenalab@latesting.com
322608663LA Testing Order:
Customer ID: GECN21
Customer PO: E9453-02-01
Project ID:
Test Report: Asbestos Analysis of Bulk Materials via AHERA Method 40CFR 763 Subpart E
Appendix E supplemented with EPA 600/R-93/116 using Polarized Light Microscopy
Sample Description Appearance % Fibrous % Non-Fibrous
Non-Asbestos Asbestos
% Type
AC-1C
322608663-0017
None DetectedNon-fibrous (Other)100%Gray
Non-Fibrous
Homogeneous
Concrete
AC-2A
322608663-0018
None DetectedNon-fibrous (Other)100%Gray/Black
Non-Fibrous
Homogeneous
Asphalt
AC-2B
322608663-0019
None DetectedNon-fibrous (Other)100%Gray/Black
Non-Fibrous
Homogeneous
Asphalt
Analyst(s)
Nahid Motamedi (10)
Rafael Palacios (9)
Jerry Drapala Ph.D, Laboratory Manager or Other Approved Signatory
LA Testing maintains liability limited to cost of analysis. Interpretation and use of test results are the responsibility of the client. This report relates only to the samples reported above, and may not be reproduced, except in full, without written approval by LA Testing. LA Testing bears no responsibility for sample collection activities or analytical method limitations. The report reflects the samples as received. Results are generated from the field sampling data (sampling volumes and areas, locations, etc.) provided by the client on the Chain of Custody. Samples are within quality control criteria and met method specifications unless otherwise noted. The above analyses were performed in general compliance with Appendix E to Subpart E of 40 CFR (previously EPA 600/M4-82-020 “Interim
Method”) but augmented with procedures outlined in the 1993 (”final”) version of the method. This report must not be used by the client to claim product certification, approval, or endorsement by
NVLAP, NIST or any agency of the federal government. Non-friable organically bound materials present a problem matrix and therefore LA Testing recommends gravimetric reduction prior to analysis.
Unless requested by the client, building materials manufactured with multiple layers (i.e. linoleum, wallboard, etc.) are reported as a single sample. Estimation of uncertainty is available on request.
Samples analyzed by LA Testing South Pasadena, CA NVLAP Lab Code 200232-0, CA ELAP 2283
Initial report from: 04/15/2026 11:20:31
Page 2 of 2ASB_PLM_0008_0002 - 2.31 Printed: 4/15/2026 11:21 AM
OrderID: 322608663
OrderID: 322608663
April 15, 2026
Geocon Consultants, Inc.
Cord Dennig/Nick Rice
Attention: Cord Dennig/Nick Rice
RE: US-50/Hazel Avenue Bridges, E9453-02-01
Workorder No.: N082784FAX: (916) 852-9132
TEL: (916) 852-9118
3160 Gold Valley Drive, Suite 800 Rancho Cordova, CA 95742
The reported results relate only to the samples as received and parameters tested by the laboratory.
Thank you for the opportunity to service the needs of your company.
Please feel free to call me at (702) 307-2659 if I can be of further assistance to your company.
Sincerely, Nancy Sibucao
Laboratory Director
Enclosed are the results for sample(s) received on April 08, 2026 by ASSET Laboratories. The sample(s) are tested for the parameters as indicated in the enclosed chain of custody in accordance with the applicable laboratory certifications.
The cover letter is an integral part of this analytical report. This Laboratory Report cannot be reproduced in part or in its entirety without written permission from the client and ASSET Laboratories - Las Vegas.
15-Apr-26Date:ASSET Laboratories
Project: US-50/Hazel Avenue Bridges, E9453-02-01 CLIENT: Geocon Consultants, Inc.
Lab Order: N082784
CASE NARRATIVE
SAMPLE RECEIVING/GENERAL COMMENTS:
All sample containers were received intact with proper chain of custody documentation.
Information on sample receipt conditions including discrepancies can be found in attached Sample Receipt Checklist Form.
Cooler temperature and sample preservation were verified upon receipt of samples if applicable.
Samples were analyzed within method holding time.
Analytical Comments for EPA 6010B:
Matrix Spike Duplicate (MSD) is outside recovery criteria for Chromium in QC sample N082776- 001A-MSD possibly due to matrix interference. The associated Laboratory Control Sample (LCS) recovery was acceptable.
CLIENT: Geocon Consultants, Inc.
Lab Order: N082784 Work Order Sample Summary
Lab Sample ID Client Sample ID Collection DateMatrix Date Received
Contract No:
Date Reported
N082784-001A H-P1 4/2/2026 4/8/2026 4/15/2026Paint Chips
N082784-002A H-P2 4/2/2026 4/8/2026 4/15/2026Paint Chips
N082784-003A AC-P1 4/2/2026 4/8/2026 4/15/2026Paint Chips
N082784-004A AC-P2 4/2/2026 4/8/2026 4/15/2026Paint Chips
Client Sample ID: H-P1
Collection Date: 4/2/2026
Matrix: PAINT CHIPS
Analyses Result Qual Units Date Analyzed
CLIENT: Geocon Consultants, Inc.
Lab Order: N082784
DF
Lab ID: N082784-001
ASSET Laboratories Print Date: 15-Apr-26
PQL
ANALYTICAL RESULTS
TOTAL METALS BY ICP
EPA 6010B
Analyst: DJ
EPA 3050B
RunID: NV00922-ICP4_260408B 130775QC Batch: PrepDate: 4/8/2026
Chromium 4/8/2026 10:33 PM1.0 mg/Kg 12.5 Lead 4/8/2026 10:33 PM1.0 mg/Kg 16.6
Qualifiers: B Analyte detected in the associated Method Blank E Value above quantitation range H Holding times for preparation or analysis exceeded ND Not Detected at the Reporting Limit S Spike/Surrogate outside of limits due to matrix interference Results are wet unless otherwise specified
DO Surrogate Diluted Out (M) Test is modified
Client Sample ID: H-P2
Collection Date: 4/2/2026
Matrix: PAINT CHIPS
Analyses Result Qual Units Date Analyzed
CLIENT: Geocon Consultants, Inc.
Lab Order: N082784
DF
Lab ID: N082784-002
ASSET Laboratories Print Date: 15-Apr-26
PQL
ANALYTICAL RESULTS
TOTAL METALS BY ICP
EPA 6010B
Analyst: DJ
EPA 3050B
RunID: NV00922-ICP4_260408B 130775QC Batch: PrepDate: 4/8/2026
Chromium 4/8/2026 10:35 PM1.0 mg/Kg 1110 Lead 4/8/2026 10:35 PM1.0 mg/Kg 117
Qualifiers: B Analyte detected in the associated Method Blank E Value above quantitation range H Holding times for preparation or analysis exceeded ND Not Detected at the Reporting Limit S Spike/Surrogate outside of limits due to matrix interference Results are wet unless otherwise specified
Client Sample ID: AC-P1
Collection Date: 4/2/2026
Matrix: PAINT CHIPS
Analyses Result Qual Units Date Analyzed
CLIENT: Geocon Consultants, Inc.
Lab Order: N082784
DF
Lab ID: N082784-003
ASSET Laboratories Print Date: 15-Apr-26
PQL
ANALYTICAL RESULTS
TOTAL METALS BY ICP
EPA 6010B
Analyst: DJ
EPA 3050B
RunID: NV00922-ICP4_260408B 130775QC Batch: PrepDate: 4/8/2026
Chromium 4/8/2026 10:38 PM1.0 mg/Kg 17.0 Lead 4/8/2026 10:38 PM1.0 mg/Kg 13.5
Qualifiers: B Analyte detected in the associated Method Blank E Value above quantitation range H Holding times for preparation or analysis exceeded ND Not Detected at the Reporting Limit S Spike/Surrogate outside of limits due to matrix interference Results are wet unless otherwise specified
Client Sample ID: AC-P2
Collection Date: 4/2/2026
Matrix: PAINT CHIPS
Analyses Result Qual Units Date Analyzed
CLIENT: Geocon Consultants, Inc.
Lab Order: N082784
DF
Lab ID: N082784-004
ASSET Laboratories Print Date: 15-Apr-26
PQL
ANALYTICAL RESULTS
TOTAL METALS BY ICP
EPA 6010B
Analyst: DJ
EPA 3050B
RunID: NV00922-ICP4_260409I 130775QC Batch: PrepDate: 4/8/2026
Chromium 4/9/2026 05:55 PM5.0 mg/Kg 514 Lead 4/9/2026 05:55 PM5.0 mg/Kg 5ND
Qualifiers: B Analyte detected in the associated Method Blank E Value above quantitation range H Holding times for preparation or analysis exceeded ND Not Detected at the Reporting Limit S Spike/Surrogate outside of limits due to matrix interference Results are wet unless otherwise specified
CLIENT: Geocon Consultants, Inc.
Work Order: N082784
ANALYTICAL QC SUMMARY REPORT
TestCode: 6010_S
Sample ID MB-130775
Batch ID: 130775 TestNo: EPA 6010B Analysis Date: 4/8/2026
Prep Date: 4/8/2026
Analyte Result SPK value SPK Ref Val %REC RPD Ref Val %RPDLowLimit HighLimit RPDLimit Qual
Units: mg/Kg
PQL
Client ID: PBS
RunNo: 217598
SeqNo: 7576246
MBLKSampType: TestCode: 6010_S
EPA 3050B
Chromium 1.0ND Lead 1.00.249
Sample ID LCS1-130775
Batch ID: 130775 TestNo: EPA 6010B Analysis Date: 4/8/2026
Prep Date: 4/8/2026
Analyte Result SPK value SPK Ref Val %REC RPD Ref Val %RPDLowLimit HighLimit RPDLimit Qual
Units: mg/Kg
PQL
Client ID: LCSS
RunNo: 217598
SeqNo: 7576247
LCSSampType: TestCode: 6010_S
EPA 3050B
Chromium 25.00 103 80 1201.0 025.633 Lead 25.00 103 80 1201.0 025.737
Sample ID LCS2-130775
Batch ID: 130775 TestNo: EPA 6010B Analysis Date: 4/8/2026
Prep Date: 4/8/2026
Analyte Result SPK value SPK Ref Val %REC RPD Ref Val %RPDLowLimit HighLimit RPDLimit Qual
Units: mg/Kg
PQL
Client ID: LCSS
RunNo: 217598
SeqNo: 7576248
LCSSampType: TestCode: 6010_S
EPA 3050B
Chromium 25.00 103 80 1201.0 025.657 Lead 25.00 102 80 1201.0 025.603
Sample ID LCS3-130775
Batch ID: 130775 TestNo: EPA 6010B Analysis Date: 4/8/2026
Prep Date: 4/8/2026
Analyte Result SPK value SPK Ref Val %REC RPD Ref Val %RPDLowLimit HighLimit RPDLimit Qual
Units: mg/Kg
PQL
Client ID: LCSS
RunNo: 217598
SeqNo: 7576249
LCSSampType: TestCode: 6010_S
EPA 3050B
Chromium 25.00 103 80 1201.0 025.702 Lead 25.00 103 80 1201.0 025.687
Sample ID LCS4-130775
Batch ID: 130775 TestNo: EPA 6010B Analysis Date: 4/8/2026
Prep Date: 4/8/2026
Analyte Result SPK value SPK Ref Val %REC RPD Ref Val %RPDLowLimit HighLimit RPDLimit Qual
Units: mg/Kg
PQL
Client ID: LCSS
RunNo: 217598
SeqNo: 7576250
LCSSampType: TestCode: 6010_S
EPA 3050B
Qualifiers:
B Analyte detected in the associated Method Blank E Value above quantitation range H Holding times for preparation or analysis exceeded
ND Not Detected at the Reporting Limit R RPD outside accepted recovery limits S Spike/Surrogate outside of limits due to matrix interference DO Surrogate Diluted Out Calculations are based on raw values (M) Test is modified
CLIENT: Geocon Consultants, Inc.
Work Order: N082784
ANALYTICAL QC SUMMARY REPORT
TestCode: 6010_S
Sample ID LCS4-130775
Batch ID: 130775 TestNo: EPA 6010B Analysis Date: 4/8/2026
Prep Date: 4/8/2026
Analyte Result SPK value SPK Ref Val %REC RPD Ref Val %RPDLowLimit HighLimit RPDLimit Qual
Units: mg/Kg
PQL
Client ID: LCSS
RunNo: 217598
SeqNo: 7576250
LCSSampType: TestCode: 6010_S
EPA 3050B
Chromium 25.00 103 80 1201.0 025.678 Lead 25.00 103 80 1201.0 025.641
Sample ID N082776-001A-MS
Batch ID: 130775 TestNo: EPA 6010B Analysis Date: 4/8/2026
Prep Date: 4/8/2026
Analyte Result SPK value SPK Ref Val %REC RPD Ref Val %RPDLowLimit HighLimit RPDLimit Qual
Units: mg/Kg
PQL
Client ID: ZZZZZZ
RunNo: 217598
SeqNo: 7576254
MSSampType: TestCode: 6010_S
EPA 3050B
Chromium 24.88 103 75 1251.0 16.8942.573 Lead 24.88 93.6 75 1251.0 8.88332.174
Sample ID N082776-001A-MSD
Batch ID: 130775 TestNo: EPA 6010B Analysis Date: 4/8/2026
Prep Date: 4/8/2026
Analyte Result SPK value SPK Ref Val %REC RPD Ref Val %RPDLowLimit HighLimit RPDLimit Qual
Units: mg/Kg
PQL
Client ID: ZZZZZZ
RunNo: 217598
SeqNo: 7576255
MSDSampType: TestCode: 6010_S
EPA 3050B
Chromium 25.00 132 75 125 20 S1.0 16.89 42.57 15.949.935 Lead 25.00 97.4 75 125 201.0 8.883 32.17 3.2833.246
Sample ID N082783-001A-DUP
Batch ID: 130775 TestNo: EPA 6010B Analysis Date: 4/8/2026
Prep Date: 4/8/2026
Analyte Result SPK value SPK Ref Val %REC RPD Ref Val %RPDLowLimit HighLimit RPDLimit Qual
Units: mg/Kg
PQL
Client ID: ZZZZZZ
RunNo: 217598
SeqNo: 7576260
DUPSampType: TestCode: 6010_S
EPA 3050B
Chromium 201.0 39.44 0.12439.487 Lead 201.0 5.795 0.4045.771
Qualifiers:
B Analyte detected in the associated Method Blank E Value above quantitation range H Holding times for preparation or analysis exceeded
ND Not Detected at the Reporting Limit R RPD outside accepted recovery limits S Spike/Surrogate outside of limits due to matrix interference
ASSET Laboratories Please review the checklist below. Any NO signifies non-compliance. Any non-compliance will be noted and must be understood as having an impact on the quality of the data. All tests will be performed as requested regardless of any compliance issues.
If you have any questions or further instruction, please contact our Project Coordinator at (702) 307-2659.
Carrier name: Southwest Express
Cooler Received/Opened On: 4/8/2026
Rep sample Temp (Deg C): 2.9 IR Gun ID: 4
Temp Blank: Yes No
Last 4 digits of Tracking No.: 0652
Cooling process: Ice Ice Pack Dry Ice Other None
Packing Material Used: None
Workorder: N082784
Sample Receipt Checklist
4. Chain of custody present? Yes No
6. Chain of custody signed when relinquished and received? Yes No
7. Chain of custody agrees with sample labels? Yes No
8. Samples in proper container/bottle? Yes No
9. Sample containers intact? Yes No
10. Sufficient sample volume for indicated test? Yes No
11. All samples received within holding time? Yes No
Yes No NA13. Water - VOA vials have zero headspace?
14. Water - pH acceptable upon receipt? Yes No NA Example: pH > 12 for (CN,S); pH<2 for Metals
1. Shipping container/cooler in good condition? Yes No Not Present
2. Custody seals intact, signed, dated on shippping container/cooler? Yes No Not Present
3. Custody seals intact on sample bottles? Yes No Not Present
5. Sampler's name present in COC? Yes No
12. Temperature of rep sample or Temp Blank within acceptable limit? Yes No NA
Yes No NA15. Did the bottle labels indicate correct preservatives used?
16. Were there Non-Conformance issues at login? Yes No NA Was Client notified? Yes No NA
Comments:
Checklist Completed By: VM Reviewed By: YR 04/10/2026
Sample ID Client Sample ID Date Collected
Date Received:
Date Due Matrix Test No
WORK ORDER Summary 08-Apr-26
WorkOrder: N082784
Comments: Standard Geocon Base Rates
Client ID: GEOCO02 Project: US-50/Hazel Avenue Bridges, E9453-02-01 QC Level: CT
Hld MS Sub
4/8/2026
Test Name
ASSET Laboratories
Storage
9:45 AM
N082784-001A H-P1 4/2/2026 4/15/2026 Paint Chips EPA 3050B SOPREP TOTAL METALS WS
4/15/2026 EPA 6010B TOTAL METALS BY ICP WS
N082784-002A H-P2 4/15/2026 EPA 3050B SOPREP TOTAL METALS WS
4/15/2026 EPA 6010B TOTAL METALS BY ICP WS
N082784-003A AC-P1 4/15/2026 EPA 3050B SOPREP TOTAL METALS WS
4/15/2026 EPA 6010B TOTAL METALS BY ICP WS
N082784-004A AC-P2 4/15/2026 EPA 3050B SOPREP TOTAL METALS WS
4/15/2026 EPA 6010B TOTAL METALS BY ICP WS
N082784-005A FOLDER 4/15/2026 4/15/2026 Folder Folder LAB
4/15/2026 Folder Folder LAB
1 of 1Page
May 11, 2026
Geocon Consultants, Inc.
Cord Dennig/Nick Rice
Attention: Cord Dennig/Nick Rice
RE: US-50/Hazel Avenue Bridges, E9453-02-01
Workorder No.: N083523FAX: (916) 852-9132
TEL: (916) 852-9118
3160 Gold Valley Drive, Suite 800 Rancho Cordova, CA 95742
The reported results relate only to the samples as received and parameters tested by the laboratory.
Thank you for the opportunity to service the needs of your company.
Please feel free to call me at (702) 307-2659 if I can be of further assistance to your company.
Sincerely, Nancy Sibucao
Laboratory Director
Enclosed are the results for sample(s) received on May 04, 2026 by ASSET Laboratories. The sample(s) are tested for the parameters as indicated in the enclosed chain of custody in accordance with the applicable laboratory certifications.
The cover letter is an integral part of this analytical report. This Laboratory Report cannot be reproduced in part or in its entirety without written permission from the client and ASSET Laboratories - Las Vegas.
11-May-26Date:ASSET Laboratories
CLIENT: Geocon Consultants, Inc.
Lab Order: N083523
CASE NARRATIVE
SAMPLE RECEIVING/GENERAL COMMENTS:
All sample containers were received intact with proper chain of custody documentation.
Information on sample receipt conditions including discrepancies can be found in attached Sample Receipt Checklist Form.
Cooler temperature and sample preservation were verified upon receipt of samples if applicable.
Samples were analyzed within method holding time.
This is an addendum for Work order N082784.
Analytical Comments for WET/EPA 6010B:
Dilution was necessary due to sample matrix.
CLIENT: Geocon Consultants, Inc.
Lab Order: N083523 Work Order Sample Summary
Lab Sample ID Client Sample ID Collection DateMatrix Date Received
Contract No:
Date Reported
N083523-001A H-P2 4/2/2026 5/4/2026 5/11/2026Paint Chips
Client Sample ID: H-P2
Collection Date: 4/2/2026
Matrix: PAINT CHIPS
Analyses Result Qual Units Date Analyzed
CLIENT: Geocon Consultants, Inc.
Lab Order: N083523
DF
Lab ID: N083523-001
ASSET Laboratories Print Date: 11-May-26
PQL
ANALYTICAL RESULTS
ICP METALS BY STLC
WET/ EPA 6010B
Analyst: MN
EPA 3010A
RunID: NV00922-ICP4_260508A 131661QC Batch: PrepDate: 5/8/2026
Chromium 5/8/2026 03:56 PM0.25 mg/L 51.1
Qualifiers: B Analyte detected in the associated Method Blank E Value above quantitation range H Holding times for preparation or analysis exceeded ND Not Detected at the Reporting Limit S Spike/Surrogate outside of limits due to matrix interference Results are wet unless otherwise specified
CLIENT: Geocon Consultants, Inc.
Work Order: N083523
ANALYTICAL QC SUMMARY REPORT
TestCode: 6010_ST
Sample ID: MB-131661
Batch ID: 131661 TestNo: WET/ EPA 60 Analysis Date: 5/8/2026
Prep Date: 5/8/2026
Analyte Result SPK value SPK Ref Val %REC RPD Ref Val %RPDLowLimit HighLimit RPDLimit Qual
Units: mg/L
PQL
Client ID: PBS
RunNo: 219082
SeqNo: 7688089
MBLKSampType: TestCode: 6010_ST
EPA 3010A
Chromium 0.0500.00029
Sample ID: MB-131542 STLC
Batch ID: 131661 TestNo: WET/ EPA 60 Analysis Date: 5/8/2026
Prep Date: 5/8/2026
Analyte Result SPK value SPK Ref Val %REC RPD Ref Val %RPDLowLimit HighLimit RPDLimit Qual
Units: mg/L
PQL
Client ID: PBS
RunNo: 219082
SeqNo: 7688090
MBLKSampType: TestCode: 6010_ST
EPA 3010A
Chromium 0.250.001
Sample ID: LCS-131661
Batch ID: 131661 TestNo: WET/ EPA 60 Analysis Date: 5/8/2026
Prep Date: 5/8/2026
Analyte Result SPK value SPK Ref Val %REC RPD Ref Val %RPDLowLimit HighLimit RPDLimit Qual
Units: mg/L
PQL
Client ID: LCSS
RunNo: 219082
SeqNo: 7688091
LCSSampType: TestCode: 6010_ST
EPA 3010A
Chromium 0.5000 99.6 85 1150.050 00.498
Sample ID: N083524-004A-DUP
Batch ID: 131661 TestNo: WET/ EPA 60 Analysis Date: 5/8/2026
Prep Date: 5/8/2026
Analyte Result SPK value SPK Ref Val %REC RPD Ref Val %RPDLowLimit HighLimit RPDLimit Qual
Units: mg/L
PQL
Client ID: ZZZZZZ
RunNo: 219082
SeqNo: 7688098
DUPSampType: TestCode: 6010_ST
EPA 3010A
Chromium 200.25 0.1013 00.102
Sample ID: N083524-004A-MS
Batch ID: 131661 TestNo: WET/ EPA 60 Analysis Date: 5/8/2026
Prep Date: 5/8/2026
Analyte Result SPK value SPK Ref Val %REC RPD Ref Val %RPDLowLimit HighLimit RPDLimit Qual
Units: mg/L
PQL
Client ID: ZZZZZZ
RunNo: 219082
SeqNo: 7688102
MSSampType: TestCode: 6010_ST
EPA 3010A
Chromium 0.5000 95.7 75 1250.25 0.10130.580
Qualifiers:
B Analyte detected in the associated Method Blank E Value above quantitation range H Holding times for preparation or analysis exceeded
ND Not Detected at the Reporting Limit R RPD outside accepted recovery limits S Spike/Surrogate outside of limits due to matrix interference
CLIENT: Geocon Consultants, Inc.
Work Order: N083523
ANALYTICAL QC SUMMARY REPORT
TestCode: 6010_ST
Sample ID: N083524-004A-MSD
Batch ID: 131661 TestNo: WET/ EPA 60 Analysis Date: 5/8/2026
Prep Date: 5/8/2026
Analyte Result SPK value SPK Ref Val %REC RPD Ref Val %RPDLowLimit HighLimit RPDLimit Qual
Units: mg/L
PQL
Client ID: ZZZZZZ
RunNo: 219082
SeqNo: 7688103
MSDSampType: TestCode: 6010_ST
EPA 3010A
Chromium 0.5000 95.0 75 125 200.25 0.1013 0.5796 0.5710.576
Qualifiers:
B Analyte detected in the associated Method Blank E Value above quantitation range H Holding times for preparation or analysis exceeded
ND Not Detected at the Reporting Limit R RPD outside accepted recovery limits S Spike/Surrogate outside of limits due to matrix interference
Subject: Re: US-50/Hazel Avenue Bridges, E9453-02-01 (ASSET Labs No. N082784) From: Yoandra Rodriguez <yoandra@assetlaboratories.com> Date: 5/4/2026, 11:35 AM To: Nick Rice <rice@geoconinc.com>, Reports LV <reports.lv@assetlaboratories.com>, "Marlon B.
Car�n" <marlon@assetlaboratories.com> CC: "maryann.balilu@assetlaboratoriesph.com" <maryann.balilu@assetlaboratoriesph.com>, 'ASSET Sample Control LV' <samplecontrol.lv@assetlaboratories.com>, "vaughn@assetlaboratories.com" <vaughn@assetlaboratories.com>
Hello Nick, We'll do.
Sample control please proceed.
Thanks, Yoandra Rodriguez Project Manager
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