Specific
(long term) Objective:
The overall goal of our MITE research is two
fold. First, we wish to determine the best methodology for predicting single-metal effects
on invertebrates. Measurement of metal concentrations within the animals themselves
promises to be a much better predictor of toxic effects than concentrations in the
environment, but is not always appropriate for metals which are essential and regulated by
animals. Measurement of metal speciation in the water, and modelling of metal uptake and
effects based on free ions may be more effective for essential metals. Our second goal is
to determine if bioaccumulation and/or speciation can improve our prediction of toxicity
in metal mixtures. If one metal affects accumulation of another, it stands to reason that
modelling of metal mixture toxicity should be more reliable when based on a body, rather
than water, concentration basis.
Objectives for 1998/99:
Our objectives for 1998/99 were to lay the
groundwork for more detailed studies if the MITE proposal was accepted by NSERC. One of
the main study sites chosen by the MITE network was the Rouyn-Noranda area. We wished to
determine if sediments from lakes in this area were toxic to Hyalella azteca, which
metals were most bioavailable and most likely to contribute to toxicity, and which lakes
might serve as useful field sites for testing bioaccumulation-toxicity-speciation
relationships. In preparation for more extensive metal mixture studies we also needed more
information on the toxicity and bioaccumulation of nickel in Hyalella. Some data of
this type were already available for most other metals (Cd, Cu, Hg, Pb, Tl and Zn). Some
preliminary mixture studies were also planned.
Accomplishments to date:
Accomplishments in the current year include
development of a methodology for measuring multiple metals in Hyalella using ICP-MS
(in collaboration with NLET-EC). The method has been tested on animals exposed to
sediments from Sudbury and seems to be reliable. Use of ICP-MS considerably reduces
analysis time for multiple metals, including analysis of field samples and tests with
metal mixtures.
Chronic toxicity tests were conducted with
sediments from 14 lakes (21 samples) in the Rouyan-Noranda area. Sediments from eleven of
these lakes were provided by the GSC, including surface sediments and deeper (20-30 cm
deep-i.e. pre-contamination?) sediments. Survival ranged from 20-93%, and was below 50%
for surface sediments from only two of the lakes (Table 1). Hyalella and overlying
water have been digested and are currently being analyzed for metals by ICP-MS for
determination of metal bioavailability. This will help identify metals and study sites for
future work.
Chronic toxicity and bioaccumulation of
nickel to Hyalella have been measured for comparison with similar data for Cd, Cu,
Hg, Pb, Tl and Zn, but some of these experiments are currently being repeated to refine
our estimates of Ni toxicity. This will form the basis for metal mixture studies including
Ni. Estimated critical body concentrations (4-week LBC25s) are around 200 nmol/g dry
weight, similar to those for Cd, Hg, Pb and Tl. Values are slightly lower after 24 hr gut
clearance; gut clearance is required for experiments with sediments. Data collected so far
suggest that body concentrations are much more reliable indicators of toxicity than
sediment or water concentrations, in agreement with previous observations with other
metals (Table 2).
Preliminary one-week single-metal and Cd-Cu-Ni-Pb-mixture
toxicity tests have been conducted. The mixture contained metals at equivalently toxic
concentrations, and resulted in 50% mortality at 2.6 times the concentration expected if
toxicity was strictly additive on a water concentration basis. Body concentration analyses
are currently in progress and should reveal if toxicity is more closely additive on a body
concentration basis. These data should provide a basis for designing more detailed chronic
toxicity tests.
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