Determination of organochlorine levels in Antarctic skua and penguin eggs by application of combined focused open-vessel microwave-assisted extraction, gel-permeation chromatography, adsorption chromatography, and GC/ECD
M. Weichbrodt et al., Determination of organochlorine levels in Antarctic skua and penguin eggs by application of combined focused open-vessel microwave-assisted extraction, gel-permeation chromatography, adsorption chromatography, and GC/ECD, INT J ENV A, 73(4), 1999, pp. 309-328
Citations number
45
Categorie Soggetti
Environment/Ecology
Journal title
INTERNATIONAL JOURNAL OF ENVIRONMENTAL ANALYTICAL CHEMISTRY
Levels of organochlorines (PCBs, DDT, toxaphene, chlordane, hexachlorobenze
ne (HCB), hexachlorocyclohexanes (HCHs), dieldrin, Q1) were determined in e
ggs of both penguins (Adelie Pygoscelis adeliae, Chinstrap Pygoscelis antar
ctica, Gentoo Pygoscelis papua) and skuas (South Polar Skua Catharacta macc
ormicki, Brown Skua Catharacta antarctica lonnbergi, Mixed Pair Skua Cathar
acta maccormicki x lonnbergi) from the Antarctic.
Focused open-vessel microwave-assisted extraction (FOV-MAE) was performed f
or the extraction of entire, partly lyophilised eggs (approx. 50 g). After
gel-permeation chromatography(GPC) and adsorption chromatography on deactiv
ated silica gel, the quantitation was performed by GC/ECD on two capillary
columns of different polarity. Compounds of technical toxaphene (CTTs) were
determined after separation of the PCBs. The sample clean-up method was va
lidated with certified reference material SRM 1588.
In general, skua eggs revealed higher organochlorine levels than penguin eg
gs. Main contaminants in skua eggs were p,p'-DDE, PCB 153, and PCB 180 with
levels about 10 - 350 mu g/kg wet weight without shell (ww). Eggs of pengu
ins were topped by levers of hexachlorobenzene (HCB) and p,pl-DDE (2 - 22 m
u g/kg ww), respectively. In skua eggs, the most abundant CTTs were B9-1679
(Parlar #50) > B8-1413 (Parlar #26) > B9-1025 (Parlar #62) > B8-1412, the
levels were about 1-20 mu g/kg ww. In penguin eggs, however, the order was
B8-1413 (Parlar #26)> B9-1679 (Parlar #50) > B8-1412 > B9-1025 (Parlar #62)
, and the levels ranged from 0.02 - 0.8 mu g/kg ww. A so far unknown heptac
hloro compound labelled Q1 caused an abundant peak in some samples. Levels
of Q1 (2 - 126 mu g/kg ww in skua eggs and 0.3 - 1.2 mu g/kg ww without she
ll in penguin eggs) were estimated relative to the ECD response factor of t
rans-nonachlor.