Data collected over a 3-year study o
f a high arcticwatershed and lake are used to understand the
fate o
forganochlorine compounds (OCs) and
form the basis o
f amass balance contaminant
fate model. The model usesthe
fugacity/aquivalence approach to describe OC dynamicsbetween air, stream in
flows and out
flow, the watercolumn, and sur
ficial sediments. The steady-state modelresults indicate that stream in
flows contributed
from 96 to>99% o
f total chemical loadings, but 57-98% o
f totalloadings were lost
from the lake via the outlet, the percentageo
f which is controlled by the hydrologic regime o
f thehigh arctic lake. Conversely, only 0.4-3.4% o
f loadings wereretained within the sediments due to the high exportrate, minimal scavenging
from the water column and loworganic carbon
fraction o
f the sediments. Using theunsteady-state model, which includes year-round processes,degradation was estimated to account
for losses o
f7-32%
for the more persistent OCs and 42-50%
for theless persistent OCs (
fchars/alpha.gi
f" BORDER=0>-HCH,
fchars/gamma.gi
f" BORDER=0 >-HCH, and endosul
fan I). I
floadings were eliminated, water column concentrations woulddecline with hal
f-lives <1 year
for less persistent OCsand 1-2 years
for the more persistent OCs, whereas the hal
f-lives
for OCs in sediment are 8-25 years.