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EPA METHOD 508A PDF

This kit provides all of the necessary materials to conduct the EPA A test. It can be used to analyze finished drinking water, drinking water in any stage for. EPA Method a – Screening for Polychlorinated Biphenyls by Perchlorination and Gas Chromatography. Analyzer Description. Configuration: 1-capillary. Subsequently, the LabCert program has only offered certification for the analysis of PCBs in drinking water by EPA method A. Method A, and s.

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Additional references to laboratory safety are available methos have been identified for the information of the analyst. The analyst should verify appropriate extract holding times applicable to the samples under study.

Exhaustive purification of reagents and glassware may be required to eliminate background phthalate contamination.

Dilute to volume with MTBE and thoroughly mix the solution. If suspended solids are present in the source, a representative portion of solids must be included in the water sample.

Dissolve the material in methanol and dilute to volume in a mL volumetric flask.

Between-sample rinsing of the sample syringe and associated equipment with methyl-t-butyl-ether MTBE can minimize sample cross contamination. Additional data are available in the method.

Decachlorobiphenyl, A / Reference Standards / Chromatography Products at

To be marginally acceptable, the system should function from 0. The method detection limits are presented in Table 1. At the laboratory, fill a minimum of two sample bottles with reagent water, seal, and ship to the sampling site along with sample bottles. Winfield – MethodRevision 1. Repeated failure, however, will confirm a general problem with the measurement system. See Figure 1 for a sample 058a. Based upon a literature search 2 such compounds include biphenyl, polyhalogenated biphenyls, hydrogenated biphenyls, and polyhalogenated epz.

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Check the pH of the sample with pH paper; if the sample does not have a pH less than or equal to 2, adjust the pH by adding more 12 N H2S Each time such a modification is made to the method, the analyst is required to repeat the procedure in Sect. Pre- servation study results indicated that most method analytes present in samples were stable for 14 days when stored under these conditions.

In general background from method analytes should be below the method detection limit. When a solvent is purified, stabilizers added by the manufacturer may be removed thus potentially making the solvent hazardous.

EPA Method 508A Screening for Polychlorinated Biphenyls by Perchlorination

Record the resulting peak The form of each acid is not distinguished by this method. This detector has proven effective in mwthod analysis of fortified reagent and arti- ficial ground waters. It is also recommended for use only with a purge and trap system devoted to the analysis of low level samples. The calibration standards must bracket the analyte concentrations found in the sample extracts. Tables 3 and 4 list the resulting data.

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Methods for the Determination of Organic Compounds in Drinking Water

Other columns or element specific detectors may be used if the requirements of Sect. Budde, Trace Analyses for Wastewaters, Environ. The working calibration curve or calibration factor must be verified on each working day by the measurement of a minimum methood two calibration check standards, one at the beginning and one at the end of the analysis day.

This procedure is applicable to samples containing PCBs as single congeners or as complex mixtures such as weathered, intact, or mixtures of commercial Aroclors. Allow the extract to remain in contact with the sodium sulfate for approximately 2 hours.

Applications

Disposable pipettes are a convenient means of directing the nitrogen into the test tube. Calculate the MDL of each analyte using the procedures described in 4.

Interference-free solvent is defined as a solvent containing less than 0. Inject a known volume between and L at room temperature of the calibration gas at room temperature directly into the purging device with a gas tight syringe.

If only brominated compounds show poor peak geometry or do not properly respond at low concentrations, repack the trap. Accordingly, exposure to these chemicals must be reduced to the lowest possible level.