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Distribution of Chlorinated Hydrocarbon Pesticides and PCBs in the ...

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<strong>and</strong> <strong>the</strong> analyses exp<strong>and</strong>ed to <strong>in</strong>clude elution <strong>of</strong> <strong>the</strong> filtered<br />

water through an XAD column followed by hexane extraction <strong>of</strong> <strong>the</strong><br />

eluate. This allowed <strong>the</strong> column retention <strong>and</strong> efficiency to be<br />

determ<strong>in</strong>ed directly for surface sea water.<br />

The results <strong>of</strong> <strong>the</strong> second XAD validation experiment, which<br />

are summarised for <strong>the</strong> HCHs <strong>in</strong> Table 3.1 <strong>and</strong> presented <strong>in</strong> full <strong>in</strong><br />

Appendix C , <strong>in</strong>dicate similar results to <strong>the</strong> first validation<br />

experiment <strong>of</strong> a 64% column efficiency for a-HCH for <strong>the</strong> <strong>in</strong>-situ<br />

sampler extraction. However, only 1.3% alpha <strong>and</strong> 3.2 % gamma -<br />

HCH were found <strong>in</strong> <strong>the</strong> column output <strong>in</strong>dicat<strong>in</strong>g an extraction<br />

efficiency <strong>of</strong> > 96%. The XAD column efficency from water sampled<br />

by NBS drop sampler agreed well for beta <strong>and</strong> gamma HCH but was<br />

substantially higher for alpha HCH than for <strong>the</strong> <strong>in</strong>-situ sampler<br />

(6700 pg/L vs 4400 pg/L). This would suggest some alteration <strong>of</strong><br />

<strong>the</strong> sample dur<strong>in</strong>g storage <strong>and</strong> lab process<strong>in</strong>g to change <strong>the</strong><br />

availability <strong>of</strong> <strong>the</strong> alpha HCH to <strong>the</strong> XAD res<strong>in</strong>.<br />

Surface seawater was also analysed dur<strong>in</strong>g June 1987 by<br />

Greg Patton <strong>of</strong> <strong>the</strong> University <strong>of</strong> South Carol<strong>in</strong>a (Patton al,<br />

1987). Sea water samples (2 -3L) were collected from lorn by NBS<br />

drop sampler, filtered <strong>in</strong> <strong>the</strong> Ice Isl<strong>and</strong> laboratory (Gelman 47mm<br />

b<strong>in</strong>derless glass fiber filters), extracted onto bonded octyl<br />

silica gel cartridges (500mg, J.T.Baker C8-SPE) <strong>and</strong> analysed<br />

<strong>in</strong>dependantly at USC. The HCHs were <strong>the</strong> only organochlor<strong>in</strong>es<br />

detected <strong>in</strong> extracts from <strong>the</strong>se cartridges (Table 3.2) <strong>and</strong> are<br />

compared to <strong>the</strong> <strong>in</strong>-situ sampler <strong>and</strong> XAD validation results <strong>in</strong><br />

Table 3.3.<br />

HCH concentrations sampled by NBS <strong>and</strong> extracted by XAD or<br />

bonded n-octyl silica are comparable <strong>and</strong> are similar to NBS<br />

sampled-hexane extracted samples collected August 86. The reason<br />

for <strong>the</strong> lower values <strong>in</strong> 1987 by <strong>in</strong>-situ sampler <strong>and</strong> NBS/hexane<br />

extraction is not clear.<br />

There has been no correction <strong>of</strong> <strong>the</strong> XAD tabulated data for<br />

column extraction/recovery efficency. The USC data <strong>in</strong>cludes a<br />

uniform recovery efficiency factor <strong>of</strong> 78% which has been applied<br />

to all organochlor<strong>in</strong>e concentrations to compensate for method<br />

losses.

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