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Fish Tissue Analysis


Sample Preparation

Laboratory setting, testing a mercury Sample

EPA and participating agencies collected fish composite samples from 500 lakes and reservoirs during the four sampling years of the National Lake Fish Tissue Study (2000-2003). To control variability among sample results, we used the same laboratory for each type of analysis, and laboratories applied the same analytical method for each chemical for the duration of the study. We ensured further control of variability by utilizing a single laboratory to prepare, composite, homogenize, and aliquot samples in a strictly controlled, contaminant-free environment.

Laboratory staff performed all sample preparation, filleting, and homogenization activities in accordance with EPA's Guidance for Assessing Chemical Contaminant Data for Use in Fish Advisories, Volume 1: Fish Sampling and Analysis (Third Edition, November 2000). Bottom-dwelling species were composited as whole fish (i.e., the entire specimen, including the head, skin, internal organs, muscle, and bones were thoroughly homogenized). Predators or gamefish were composited as skin-on (scales removed, with belly flap attached) fillets. Once homogenized and composited, sample aliquots were prepared for distribution to each of the analytical laboratories, and extra volume aliquots were shipped to a sample repository for archiving.

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Target Chemicals

A sampling machine for testing target chemicals

We are analyzing the fish tissue samples for the following target chemicals:

For a complete list of all target chemicals, refer to the National Lake Fish Tissue Study Target Analyte (Chemical) List (PDF) (4 pp., 41 K).

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Analytical Methods

Laboratories employed the following analytical methods for analysis of the fish tissue samples:

EPA Method 1631, Revision B (Mercury in Water by Oxidation, Purge and Trap, and Cold Vapor Atomic Fluorescence Spectrometry) and its Appendix (Digestion Procedures for the Determination of Total Mercury in Tissue, Sludge, Sediment, and Soil) to measure total mercury (Hg) concentrations.

A strictly controlled, contaminant-free environment -- a clean room

EPA Method 1632, Revision A (Chemical Speciation of Arsenic in Water and Tissue using Hydride Generation Quartz Furnace Atomic Absorption Spectrometry) to directly determine total inorganic arsenic, arsenic (III), monomethylarsonic acid (MMA), and dimethylarsinic acid (DMA) concentrations. Arsenic (V) concentrations were derived by mathematically subtracting the measured concentration of arsenic (III) from the measured concentration of total inorganic arsenic for each composite sample.

EPA Method 1613, Revision B (Tetra- through Octa- Chlorinated Dioxins and Furans by Isotope Dilution HRGC/HRMS, EPA-821-B-94-005) a slightly modified version of this method to determine the concentrations of seventeen 2,3,7,8-substituted chlorinated dibenzo-p-dioxins and dibenzofurans (CDDs and CDFs).

EPA Method 1668, Revision A (Chlorinated Biphenyls Congeners in Water, Soil, Sediment, and Tissue by HRGC/HRMS, EPA-821-R-00-002) to measure PCB congener concentrations.

EPA Method 1656, Revision A (Organo-Halide Pesticides in Wastewater, Soil, Sludge, Sediment, and Tissue by GC/HSD) to measure concentrations of organochlorine pesticides and total Aroclors. Sample extracts were concentrated by a factor of five beyond method-specified levels (before instrumental analysis) in order to ensure that all target pesticides could be quantified at levels equal to or lower than the screening values published in EPA's Guidance for Assessing Chemical Contaminant Data for Use in Fish Advisories, Volume 1: Fish Sampling and Analysis (Third Edition, November 2000).

EPA Method 1657, Revision A (Organophosphorus Pesticides in Water, Soil, and Tissue by GC/FPD) to determine the presence and concentrations of organophosphorus pesticides.

EPA Method 1625, Revision C (Semivolatile Organic Compounds by Isotope Dilution GC/MS) to analyze the remainder of the target organic chemicals.

EPA Method 1614 - August, 2003 Draft (Brominated Diphenyl Ethers in Water, Soil, Sediment and Tissue by HRGC/HRMS) to measure specific PBDE congener concentrations (statistical year 4 samples only).

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Quality Assurance (QA) Program

In addition to the Quality Assurance Project Plan (QAPP) for sample collection activities, we developed a separate QAPP for analytical control and assessment activities. The Quality Assurance Project Plan for Analytical Control and Assessment Activities in the National Study of Chemical Residues in Lake Fish Tissue (September 2000) establishes method quality objectives (MQOs) for laboratory data generated during the study and describes QA/QC techniques employed by laboratory and Sample Control Center staff to ensure that these goals are met.

Stacks of coolers holding fish samples

Our Sample Control Center subjects all analytical data to three levels of review:

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Documents

Quality Assurance Report for the National Study of Chemical Residues in Lake Fish Tissue: Analytical Data for Years 1 through 4 (EPA-823-R-05-005) (PDF) (57 pp., 252 K) The Quality Assurance Report documents the quality of fish tissue data for samples collected during the four sampling years of the National Lake Fish Tissue Study (2000-2003). It provides a brief overview of the study, a description of the QA program for the study, a summary of analytical methods used in the study, and an assessment of the fish tissue data quality.

Laboratory equipment called mercury bubblers

Quality Assurance Project Plan for Analytical Control and Assessment Activities in the National Study of Chemical Residues in Lake Fish Tissue (EPA-823-R-02-006) (PDF) (46 pp., 1.1 MB) The Quality Assurance Project Plan (QAPP) describes the quality assurance/quality control (QA/QC) requirements for analytical activities being conducted for the National Lake Fish Tissue Study. It was approved by the Office of Science and Technology's (OST) Quality Assurance Officer in September 2000.

National Lake Fish Tissue Study Target Analyte (Chemical) List (PDF) (4 pp., 41 K) This list contains the chemicals included in the analysis of fish tissue samples for the study. The chemicals are arranged by chemical group method and listed alphabetically under each method.

Table: Reporting Limits for PCBs, Dioxins/Furans, Pesticides, Metals, & Organics (PDF) (6 pp., 22 K) This table contains the reporting limits for each chemical included in the fish tissue analysis, including the method detection limit and the minimum level (quantitation limit). The chemicals are arranged by analytical method and listed alphabetically under each method.

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