Cursory Data Review of Analytical Results for Sample Sets



Similar documents
CALIFORNIA DEPARTMENT OF PUBLIC HEALTH ENVIRONMENTAL LABORATORY ACCREDITATION PROGRAM Accredited Fields of Testing

Rule 318A.f: Rule Description

San Mateo County Environmental Health Characterization and Reuse of Petroleum Hydrocarbon Impacted Soil

Extractable Petroleum Hydrocarbon Fractions Using the ETPH Analytical Method and Criteria Development TECHNICAL SUPPORT DOCUMENT

Appendix D lists the Field Services Standard Operating Procedures. Appendix E lists the Biological Monitoring Standard Operating Procedures.

56 TOLEDO STREET, FARMINGDALE, NY P: F:

EMERGENCY PETROLEUM SPILL WASTE MANAGEMENT GUIDANCE. Hazardous Materials and Waste Management Division (303)

Special Waste Disposal Request

CHAPTER SOIL TREATMENT FACILITIES

TERRA TEK LIMITED GUIDE TO SAMPLE HANDLING. Version 1.06

WASTE ACCEPTANCE PROTOCOLS FOR THE PROVINCES OF

To meet our acceptance criteria, we may require you to partially treat your wastewater before it discharges to sewer.

DATA ON TEXPET S CLEANUP

Fact Sheet: Disposal of Alkaline Batteries

Data Management Tool -

APPENDIX II TIER I CHECKLIST

Land Application of Drilling Fluids: Landowner Considerations

MBJ Environmental Programmes

Removing Thallium from Industrial FGD Scrubber Water with Sorbster Adsorbent Media

NWTPH-HCID. Hydrocarbon Identification Method for Soil and Water

LED Life-Cycle Assessment & Environmental Testing

Environmental Technology March/April 1998

LEACHING CHARACTERISTICS OF ASPHALT ROAD WASTE

Here are some hazardous wastes commonly generated by the marina industry:

Characterizing Beauty Salon Wastewater for the Purpose of Regulating Onsite Disposal Systems

Date: Chairman, Energy Facility Site Evaluation Council

The purpose of this bid is to procure a contract with a laboratory to provide analytical testing services on an as-needed basis.

Culligan Exchange Tank Deionization Service

Frequently Asked Questions about Hazardous Waste Lamps (e.g., fluorescent or other lights containing mercury)


Introduction. The following definitions may help you better understand the components of the data report.

Sent via FedEx with delivery confirmation

GAS WELL/WATER WELL SUBSURFACE CONTAMINATION

Environmental Forensics

Texas Commission on Environmental Quality

Produced water from oil and gas production

Oil and Gas Air Quality Regulations and Permitting

Pace Analytical e-report

DEPARTMENT OF ENVIRONMENTAL REGULATION. Technical Document DETERMINING REPRESENTATIVE GROUND WATER SAMPLES, FILTERED OR UNFILTERED

In-Situ Remediation Strategies as Sustainable Alternatives to Traditional Options. Ryan Bernesky, B.Sc., P.Ag. February 26, 2013

South Dakota s Statewide Ground Water Quality Monitoring Network

Managing Floor Drains and Flammable Traps

FDEP Soil Cleanup Target Level Residential soil = 400 ppm Industrial soil = 920 ppm. Arsenic is a known human carcinogen EPA regulation

University Lands THE UNIVERSITY OF TEXAS SYSTEM

ANALYTICAL REPORT LABORATORY DETAILS. Telephone Facsimile . SGS Reference Report Number Date Reported

BOTTLED WATER QUALITY REPORT INTRODUCTION VOSS SOURCE SPECIFIC MINERAL ANALYSIS. VOSS Still. VOSS Sparkling. General Mineral Analysis

Purity of water is defined in part by the mineral level found in specific bottled waters and is referred to as

APPENDIX B. Magna Reservoir Leak Detection & Water Quality Sampling Plan (Revised June 2011)

Guidelines for the Responsible Disposal of Wastes and Containers from Polyurethane Processing

Sampling Techniques to Ensure Quality Results. David Springer ACLCA Adelaide June 2013

In Fracking s Wake: New Rules are Needed to Protect Our Health and Environment from Contaminated Wastewater

MITIGATION MONITORING PROGRAM (Accompanies the Van Nuys Fire Station 39 Initial Study/Mitigated Negative Declaration)

WHAT IS A HAZARDOUS WASTE? Kansas Department of Health and Environment Bureau of Waste Management

Proposed Soil Lead Management Criteria as Part of Caltrans Highway Construction and Maintenance

MATERIAL CONTAINMENT PLAN. for the PIÑON RIDGE MILL HIGHWAY 90 BEDROCK, CO Prepared by: ENERGY FUELS RESOURCES CORPORATION

Dispelling the Myths of Heat Transfer Fluids. Kevin Connor The Dow Chemical Company

Ontario Drinking Water Parameter Limits and Descriptions

Innovative Removal of Agricultural Related Water Pollutants in the Chesapeake Bay Watershed

DEP 2012 QUALITY ASSURANCE CHAPTER QUALITY ASSURANCE TABLE OF CONTENTS PART I GENERAL

WATER EFFLUENT AND SOLID WASTE CHARACTERISTICS IN THE PROFESSIONAL CAR WASH INDUSTRY. A Report for the International Carwash Association

Pharmaceutical Waste Management for Minnesota Veterinary Facilities

BUREAU OF ENVIRONMENTAL REMEDIATION/REMEDIAL SECTION GUIDANCE INVESTIGATION AND REMEDIATION OF SALT (CHLORIDE)- IMPACTED SOIL AND GROUND WATER

Temple College Compliance with the Environmental Protection Agency Requirements

SYNTHETIC TURF STUDY: OVERVIEW OF THE STUDY ELEMENTS

EPA Test Method TCLP, Toxicity Characteristic Leaching Procedure

3. IDENTITY AND ANALYSIS OF TOTAL PETROLEUM HYDROCARBONS

40 CFR Hazardous Waste Determination

HAZARDOUS AND NONHAZARDOUS OIL AND GAS WASTE

Water Analysis Report Report Date: March 31, 2012 Testing Period: 1st - 4th Quarter 2011

1. Page 1, Incoming Soil Materials, Testing Frequency :

Impact of utilised bottom ash

80. Testing salts for anions and cations

Quality Assurance Program Plan

IMPACT OF SOLID WASTE EFFECT ON GROUND WATER AND SOIL QUALITY NEARER TO PALLAVARAM SOLID WASTE LANDFILL SITE IN CHENNAI

Hazardous Materials Handling and Disposal Policy and Procedures

Oil, grease and used petroleum oil management and environmental economic issues

integrity without compromise Environmental Monitoring

Irrigation Water for Greenhouses and Nurseries

Nitrate and Nitrite Removal from Municipal Drinking Water Supplies with Electrodialysis Reversal

Industrial Solid Waste Management Plan (ISWMP)

Risk-Based Decision Making for Site Cleanup

FACT SHEET STATEMENT OF BASIS HARLEY DOME 1 PRODUCED WATER TREATMENT FACILITY UPDES PERMIT NUMBER: UT NEW PERMIT MINOR INDUSTRIAL

1.3 Wastewater and Ambient Water Quality

DATA VALIDATION STANDARD OPERATING PROCEDURES FOR CONTRACT LABORATORY PROGRAM ROUTINE ANALYTICAL SERVICES

Guidance on Remediation of Petroleum-Contaminated Ground Water By Natural Attenuation

THE METHOD DETECTION LIMIT AND PRACTICAL QUANTITATION LEVEL: THEIR DERIVATIONS AND REGULATORY IMPLICATIONS

5.4 Nitrogen Loading Mix-Bury-Cover and Landspreading Landspray, Landspray-While-Drilling, Pump-Off

APPENDIX C. WASTE MANAGEMENT PLAN March 6, 2009

EOC Quality Through Compliance. Policies and Procedures. HAWAII HEALTH SYSTEMS C O R P O R A T I O N Touching Lives Everyday" N/A

Coke Manufacturing. Industry Description and Practices. Waste Characteristics

REUSE AND DISPOSAL OF CONTAMINATED SOIL AT MASSACHUSETTS LANDFILLS DEPARTMENT OF ENVIRONMENTAL PROTECTION POLICY # COMM

Testing Water for Gardening and Lawn Irrigation

Saving water means saving money; Fix those leaks right away. Community Water Company of Green Valley. Our Water Source

DMR-QA Planning Guide 2015 DMR-QA 35: Plan for Success

Standard methods in water analysis

4. PRODUCTION, IMPORT/EXPORT, USE, AND DISPOSAL

3M MATERIAL SAFETY DATA SHEET NO. 4004, 4008, 4026 AND 4032 DOUBLE COATED URETHANE FOAM TAPE 07/29/2002

Fact Sheet Ground Water Remediation General Permit for Temporary Discharges Permit Number WYG940000

Material Safety Data Sheet

Material Safety Data Sheet SECTION 1: PRODUCT AND COMPANY IDENTIFICATION

Transcription:

Cursory Data Review of Analytical Results for Sample Sets L67895 L67896 L68186 L68187 L68302 L79307 First it must be noted that all samples in these sets were solid material. They were either analyzed for total analysis, TCLP, or SPLP. L67895 Date Received: 9 23 2005 Dates Analyzed: 9 26 2005 and 9 27 2005 Number of samples: 1 This set was analyzed for TCLP (method 1311) RCRA metals (8). The only hit above the PQL was barium at 0.47 mg/l. The remaining metals were not detected above the PQL. All PQLs meet RCRA limits that apply to the TCLP method. No results exceed RCRA limits for hazardous waste. L67896 Date Received: 9 23 2005 Date Extracted: 10 4 2005 Date Analyzed: 10 4 2005 This sample was analyzed for TPH DRO (method 8015B) with a result of 19000 J mg/kg dry. The surrogate was understandably high due to the high analyte concentration. No data qualifier based on this issue. The sample was not shipped on ice and exceeded the recommended temperature of >0 to 6 degrees C. The result should be qualified as estimated J based on this issue. The datum is still useable.

L68186 Date Collected: 10 11 2005 Date Received: 10 12 2005 TPH DRO Analysis: Date Extracted: 10 12 2005 Date Analyzed: 10 13 2005 The TPH DRO result was 2700 mg/kg dry. The surrogate was understandably high due to the high analyte concentration. No data qualifier based on this issue. For the analysis of volatile organics (BTEX) by method 8260B, TCLP was requested. Date Extracted: 10 12 2005 Date Analyzed: 10 13 2005 The BTEX (benzene, toluene, ethylbenzene, and xylene) were not detected (<0.042 mg/l). These were well below the associated RCRA criteria for TCLP. The sample was received with headspace. However, since Utah continues to accept method 5030 for the collection of solid/soil samples it is impossible to collect samples without headspace. No data qualifier as a result of this issue.

L68187 Date Collected: 10 11 2005 Date Received: 10 12 2005 Dates Analyzed: 10 14 2005 and 10 18 2005 This set was analyzed for TCLP RCRA metals (8). The only hit above the PQL was barium at 1.6 mg/l. The remaining metals were not detected above the PQL. All PQLs meet RCRA limits that apply to the TCLP method. No results exceed RCRA limits for hazardous waste. L68302 Date Received: 10 18 2005 Date Analyzed: 10 20 2005 Number of Samples: 2 This set was extracted by SPLP (Synthetic Precipitation Leaching Procedure) and the leachate was analyzed for total recoverable hydrocarbons (TRPH) by method 1664 SGT. Sample #1 result was <3.0 UJ mg/l and sample #2 was 3.3 J mg/l. Insufficient time was available to perform the SPLP and analysis before the 28 day hold time for TRPH analysis due to the delay in sample receipt. The holding time of 28 days was missed by one day. According to guidelines the data is still useable but should be qualified J as estimated. The U flag indicates the sample is not detected at the reporting limit provided. All data is acceptable with appropriate qualifiers.

L79307 Date Collected: 7 31 2007 Date Received: 8 10 2007 Number of Samples: 3 For the RCRA TCLP (Method 1311) analysis the elements calcium, magnesium, potassium, and sodium were analyzed by method 6010B. Date Analyzed: 8 20 2007 There were several low concentration hits of these elements. There are no RCRA limits for these elements as they are not considered toxic under this regulation. Several classical chemistry methods were requested: Alkalinity, chloride, oil and grease, sulfate, total dissolved solids (TDS) and TRPH. Dates Analyzed: 8 13 2007, 8 15 2007, and 8 17 2007 All analytes were determined within the holding time with the exception of TDS. There are no guidelines for determining TDS in solid samples. EPA suggests using professional judgment in these cases. It is our judgment that the data should be accepted but qualified as J as estimated. The result for oil and grease on sample #1 exceeded the limitations of the method. This result should be qualified J as estimated. TPH DRO by method 8015B Three samples were analyzed with positive results (12000, 930, and 3400 mg/kg dry respectively). The surrogate on one sample was understandably high due to the high analyte concentration. No data qualifier based on this issue.

RCRA SPLP (method 1312) Semivolatile Analysis (SVOAs) The three samples were analyzed for SVOA with no positive hits above the reporting limit of 0.025 mg/l. The reporting limit is below the RCRA regulatory limits. The holding time for the SPLP set up was exceeded by one day. The analysis after the SPLP preparation was analyzed within the holding time. All data is qualified as UJ estimated as a result. The data are still useable. RCRA SPLP (method 1312) Volatile Analysis (VOAs) The three samples were analyzed for VOAs with no positive hits above the reporting limits. The reporting limit is below the RCRA regulatory limits. The holding time for the SPLP set up was exceeded by one day. The analysis after the SPLP preparation was analyzed within the holding time. All data is qualified as UJ estimated as a result. The data are still useable. Summary It is our opinion that all of the data reviewed are useable. Most data are acceptable as presented. Some data are qualified as estimated based on minor issues. The methods performed were based on meeting RCRA limits for hazardous waste. At no time was there information provided that the RCRA methods were to be used but alternative regulatory limits (Utah Groundwater Quality Standards) detection limits required. Unless specific information is provided, SPLP, TCLP and total analysis using RCRA methods are designed to meet RCRA limits not for Utah groundwater criteria. If lower reporting limits are required additional sampling and analysis may be required.