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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Analyses of laboratory reagent blanks Sect. Storage, labelling and disposal of PCBs must conform to all applicable laws and regulations. Between-sample rinsing of the sample syringe and associated equipment with hexane can minimize sample cross contamination. If this is not ea case, chromatographic comparability of standards to sample may be affected. If the tumbler is used, pour contents of tumbler bottle into a separatory funnel.

This procedure is applicable to samples containing PCBs as single congeners or as complex mixtures such as weathered, intact, or mixtures of commercial Aroclors. Two L of the extract are then injected into a gas chromatograph equipped with a linearized electron capture detector for separation and analysis. When peaks obviously represent more than one sample componenet i. Repeat shaking and venting until pressure release is not observed during venting.

EPA Method a – Screening for Polychlorinated Biphenyls by Perchlorination and Gas Chromatography

Fortify four to seven 1-L portions of reagent water with methid These calculated control limits should methoc exceed those established in Section For extended periods of analysis greater than 8 hrit is strongly recommended that check standards be interspersed with samples at regular intervals during the course of the analyses.

Fortify the sample with 50 JtL of the surrogate standard solution. Conventional sampling practices 6 should be followed; however, the bottle must not be prerinsed with sample before collection.

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Certified mixtures of vinyl chloride in nitrogen at 1. Six of the methods are for volatile organic compounds VOCs and certain disinfection by-products, and these methods were cited in the Federal Register of July 8,under the National Primary Drinking Water Regulations. The names of methoe of the methods are provided to assist users in obtaining direct telephone support when required. Monitor the retention times for each method analyte using data generated from calibration standards.

The storage time described for stock standard solutions in Sect. Transfer the internal standard solution to a TFE-fluorocarbon-sealed screw cap bottle and store at room temperature.

Five calibration solutions containing DCB from 0.

Decachlorobiphenyl, A / Reference Standards / Chromatography Products at

When potential interfering peaks are noted in laboratory reagent blanks, the analyst must eliminate the problem before analyzing samples. The purpose of a surrogate analyte is to monitor method performance with each sample. Alternately, 75 L of freshly prepared sodium thiosulfate solution 0. Preservation data for the analytes chlorthalonil, alpha-HCH, delta-HCH, gamma-HCH, cis- permethrin, trans-permethrin, and trifluralin are nondefinitive, and therefore if these are analytes of interest, it is recommended that the samples be analyzed immediately.

Budde, “Trace Analyses for Wastewaters,” Environ. Field duplicates may be analyzed to assess the precision of the environmental measurements. Collect duplicate samples in clean 1-L glass containers and seal with a Teflon-lined screw cap.

The gas will rapidly dissolve in the methanol. An explosion shield should be used during the perchlorination and neutralization procedures along with additional eye protection such as an 8-in.

Other concentration devices or techniques may be used in place of the K-D if the requirements of Sect. Dilute an aliquot of the DCB stock solution to produce about 10 ml of a solution containing If the retention time of an unknown compound corresponds, within limits, to the retention time of a standard compound, then identification is considered positive. Mark the sample meniscus on the side of the sample bottle for later determination of sample volume. These compounds generally appear in the chromatogram as large peaks.

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Alternative de- tectors, including a mass spectrometer, may be used in accordance with the provisions described in Sect. The background concentrations of the. Solution should be replaced when ongoing QC Sect. Cartridges from six suppliers were used in the methods research, and a quality control procedure was developed to permit selection of cartridges with acceptable performance characteristics.

If heptachlor is to be determined, samples should be extracted within 7 days of collection. Extract matrix effect evaluation –It has been found that there may be a matrix effect from the perchlorinated extract which can bias the response on certain GC systems. Laboratory Fortified Sample Matrix LFM — An aliquot of an environmental sample to which known quantities of the method analytes are added in the laboratory.

A preventive technique is between-sample rinsing of the purging apparatus and sample syringes with two portions of reagent water. DDT and endrin are easily degraded in the injection port if the injection port or front of the column is dirty.

EPA Method 508A

The staff of the Technical Support Division of the Office of Drinking Water, and particularly Richard Reding, provided extensive comments on the first draft of this manual, and on previous revisions of many of the analytical methods. The container must be washed and dried as described in Sect.

The added concentration should not be less then the background concentration of the sample -selected for fortification. Add 2 ml of MTBE and a fresh boiling stone.

Seal and shake for 2 min.