Using earthworm behaviour to assess contaminated soil
by Natalie Feisthauer,
ESG International Inc.
Placement of earthworms into an
avoidance response test unit filled
with contaminated and control soil.
Researchers are using earthworm
behaviour as an economical
method to assess contaminated
soils. These new
test methods will assist decision-makers
in addressing clean-up options.
Working with Environment Canada,
researchers at ESG International
are in the final stages of the development
of national toxicity test methods
that will be used to assess the toxicity
of contaminated soils to terrestrial
plants, arthropods (springtails) and
earthworms. Three different types of
earthworm tests have been developed
and include acute (lethal), behaviour
(sublethal) and chronic (reproduction)
tests.
The acute toxicity test is used to
measure the acute, or short-term,
effects of contaminated soils on adult
earthworm survival. Earthworm survival
is assessed following 7 and 14
days of exposure to the contaminated
soil. This acute test is useful as a
screening tool; however, it cannot
detect sublethal effects of contaminated
soils.
The reproduction test is a 56 to 63
day test that is used to measure the
effects of chronic or long-term exposure
to contaminated soil on the reproductive
ability of earthworms. At the
beginning of a test, two reproductively
mature earthworms are placed in a test
unit (glass 500 mL wide-mouthed
mason jar) that contains between 350
to 400 mL of test soil. After 28 or 35
days, the adults are removed from the
test units, and their survival rate measured.
At the end of the test, the number
of juveniles produced, juvenile wet
and dry mass, and the number of
hatched and unhatched cocoons are
measured.
The behaviour test is used to measure
the avoidance-response of earthworms
to potentially contaminated
soils. It is a short test, with a 72-hour
duration, and has been shown to be
predictive (i.e., as sensitive) of the
results of the much longer-term (56 to
63 day), reproduction tests. The
behaviour test method has been evaluated
with two different earthworm
species, five different soil types, and
with organic (petroleum hydrocarbons,
pesticides) and inorganic (heavy metals)
contaminants. The soils tested
were either uncontaminated field-collected
soils amended with a toxicant,
or were site-specific contaminated
soils collected from the field.
The behaviour test unit has a unique
circular design, and consists of six
equally-sized, pie-shaped compartments
that surround a central hollow
chamber (Figure 1). Each compartment
is connected to the central chamber
and adjacent compartments by two
or three holes at the bottom of the
compartment walls. As a result, earthworms
can move freely among all
compartments.
At the beginning of a test, 350 mL
of soil is added to each compartment.
Soil treatments (i.e., soils with different
levels of contamination) can be
assigned to compartments in a random,
alternating or stratified pattern. A
control treatment (soil with no contamination)
is always included. Ten
earthworms are added to the test unit
one at a time in order to avoid a potential
“clustering” effect. The compartment
entered by each worm is recorded
at the beginning of the test (e.g., t =
0 hours). The test temperature is controlled
at 20 ± 3° C. After 72 hours, at
the end of the test, compartments are
isolated by inserting metal sheets to
prevent worms from moving among
compartments. The distribution of the
earthworms among the soil treatments
is recorded.
Figure 1. Avoidance-response test unit constructed of stainless steel.
The experimental design of the
avoidance behaviour test has been
under development for the last five
years, and, depending on the design,
the results have been analyzed either
using Chi-square distribution analysis
or, more recently, by estimating a
50% avoidance effect concentration
(EC50). An EC50 for avoidance is the
concentration of soil that causes an
avoidance response in 50% of the
worm test population.
The relationship between earthworm
avoidance and adverse effects on
reproduction was directly compared
using the earthworm species Eisenia
andrei, or compost worm, a commonly
used invertebrate species for soil toxicity
assessments. The contaminants
assessed included the fungicide benomyl,
copper sulphate, crude oil,
amines, and condensates.
For each contaminant, the highest
concentration at which E. andrei did
not display a significant avoidance
response (“avoidance threshold”) was
compared with the EC20s or NOAECs
determined for each of the five reproductive
endpoints. EC20s are soil concentrations
at which there is a 20%
reduction in the reproduction endpoint
relative to the control value, and
NOAECs are no-observable-adverse-effect
concentrations. The results
illustrate how closely related the avoidance-
response test results are to those
of the reproduction tests. It is important
to note that the concentrations did
not cause direct mortality to adult
worms in either acute or chronic tests.
The practical significance of the
relationship between earthworm avoidance
and reproduction is that the sensitive
avoidance-response test can be
used as a quick and economical substitute
for reproduction tests in the initial
screening of contaminated site soils.
One significant limitation with application
of the avoidance–response test
method, however, is the fact that the
relationship between earthworm avoidance
and effects on reproduction must
be empirically determined until a large
enough database of different types of
contaminants and soil types is sufficiently
large to minimize uncertainty.
ESG International, Inc., recently
represented Environment Canada at
the International Standards Organisation
(ISO) Meetings on Soil Quality
in Olso, Norway. Researchers in
Germany have also developed an
earthworm avoidance–response test
method that is quite different in design
from the Environment Canada method.
Both the Canadian and German methods
are scheduled by the ISO Technical
Committee 190 (Soil Quality) to
become new international test methods.
The Environment Canada earthworm
acute, avoidance and reproduction
test methods are currently undergoing
scientific review and should be
publicly available sometime in 2003.
Natalie Feisthauer is Manager of the
Soil Ecotoxicity Laboratory at ESG
International Inc.
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