Use of semipermeable membrane devices (SPMDs) - Determination of bioavailable, organic, waterborne contaminants in the industrial region of Bitterfeld, Saxony-Anhalt, Germany
B. Vrana et al., Use of semipermeable membrane devices (SPMDs) - Determination of bioavailable, organic, waterborne contaminants in the industrial region of Bitterfeld, Saxony-Anhalt, Germany, ENV SCI P R, 8(1), 2001, pp. 27-34
Triolein-containing semipermeable membrane devices (SPMDs) were employed as
passive samplers to provide data on the bioavailable fraction of organic,
waterborne, organochlorine pesticides (OCPs), polychlorinated biphenyls (PC
Bs) and poly nuclear aromatic hydrocarbons (PAHs) in streams flowing throug
h a highly polluted industrial area of Bitterfeld in Saxony-Anhalt, Germany
. The contamination of the region with organic pollutants originates in was
tewater effluents from the chemical industry, from over one-hundred years o
f lignite exploitation, and from chemical waste dumps. The main objective w
as to characterise time-integrated levels of dissolved contaminants, to use
them for identification of spatial trends of contamination, and their rela
tionship to potential pollution sources. SPMDs were deployed for 43 days in
the summer of 1998 at four sampling sites. The total concentration of poll
utants at sampling sites was found to range from a low of 0.8 mug/SPMD to 2
5 mug/ SPMD for PAHs, and from 0.4 mug/SPMD to 22 mug/SPMD for OCPs, respec
tively. None of the selected PCB congeners was present at quantifiable leve
ls at any sampling site. A point source of water pollution with OCPs and PA
Hs was identified in the river system considering the total contaminant con
centrations and the distribution of individual compounds accumulated by SPM
Ds at different sampling sites. SPMD-data was also used to estimate average
ambient water concentrations of the contaminants at each field site and co
mpared with concentrations measured in bulk water extracts. The truly disso
lved or bioavailable portion of contaminants at different sampling sites ra
nged from 4% to 86% for the PAHs, and from 8% to 18% for the OCPs included
in the estimation. The fraction of individual compounds found in the freely
dissolved form can be attributed to the range of their hydrophobicity. In
comparison with liquid/liquid extraction of water samples, the SPMD method
is more suitable for an assessment of the background concentrations of hydr
ophobic organic contaminants because of substantially lower method quantifi
cation limits. Moreover, contaminant residues sequestered by the SPMDs repr
esent an estimation of the dissolved or readily bioavailable concentration
of hydrophobic contaminants in water, which is not provided by most analyti
cal approaches.