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| 02128nam 2200397zi 4500 |
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| 001 | 9.873672 |
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| 003 | CaOODSP |
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| 005 | 20221107164000 |
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| 006 | m o d f |
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| 007 | cr |n||||||||| |
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| 008 | 190527s1989 onc #ot f000 0 eng d |
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| 040 | |aCaOODSP|beng|erda|cCaOODSP |
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| 041 | |aeng|bfre |
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| 043 | |an-cn--- |
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| 086 | 1 |aEn13-5/89-95E-PDF |
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| 100 | 1 |aScott, Brian F., |d1939- |eauthor. |
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| 245 | 10|aComparison of results between PCB congener method and standard method obtained during validation study / |cby B.F. Scott and Richard Szawiola. |
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| 264 | 1|aBurlington, Ontario : |bResearch and Applications Branch, National Water Research Institute, |c1989. |
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| 300 | |a1 online resource (iii, 9, (6) pages). |
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| 336 | |atext|btxt|2rdacontent |
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| 337 | |acomputer|bc|2rdamedia |
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| 338 | |aonline resource|bcr|2rdacarrier |
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| 490 | 1 |aNWRI contribution ; |vno. 89-95 |
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| 500 | |aDigitized edition from print [produced by Environment and Climate Change Canada]. |
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| 500 | |a"May 1989." |
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| 504 | |aIncludes bibliographical references. |
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| 520 | |a"The results from a new congener specific gas chromatographic PCB method were compared to those derived from a standard method. The samples included replicates of a spiked sediment sample, replicates of the spike treated only with the cleanup technique, replicates of the unspiked sediment, and replicates of the spiking solution. The results derived from both methods agreed and the precision was similar. Accordingly, the PCB congener specific method provides the composition of the PCBs present but requires less analysis time"--Abstract. |
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| 546 | |aIncludes abstract in French. |
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| 692 | 07|2gccst|aWater pollution |
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| 692 | 07|2gccst|aSediments |
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| 700 | 1 |aSzawiola, R., |eauthor. |
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| 710 | 1 |aCanada. |bEnvironment Canada. |
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| 710 | 2 |aNational Water Research Institute (Canada). |bResearch and Applications Branch. |
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| 830 | #0|aNWRI contribution ;|vno. 89-95.|w(CaOODSP)9.844121 |
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| 856 | 40|qPDF|s1.26 MB|uhttps://publications.gc.ca/collections/collection_2019/eccc/en13-5/En13-5-89-95-eng.pdf |
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