Abstract:
Hexavalent chromium (Cr(VI)) is a heavy metal that is well known as a health hazard to
human and animals. The majority of the empirical studies conducted to determine the
ecotoxicity of Cr(VI), exceed levels generally recorded in the environment. The current study
was therefore undertaken to assess lethal and sub-lethal toxicity of environmentally-relevant
levels of Cr(VI) on three faunal species, representing three taxa, inhabiting urbanized
landscapes which are prone to Cr(VI) pollution. The three selected taxa were earthworms
(Eudrilus eugeniae\ Kinberg, 1867), fish (Labeo dussumieri, Valenciennes, 1842) and toads
(Duttaphrynus melanostictus, Schneider, 1799).
Lethal toxicity was evaluated using LC50 values after short (4 days) and long term (21/ 28
days) exposures. Sub-lethal toxicity, both in the short and long term, were evaluated using
alterations in growth, activity, development, histology, haematology and genetic structure.
Adult earthworms, fmgerlings and adult fish, and tadpoles and adult toads were exposed to
five concentrations of Cr(VI) ranging from 0.002 to 20 mg/L, while maintaining a control
group in each case. The exposure concentrations used in the present study were determined
based on the analysis of dissolved Cr concentrations in water samples collected from 94
sampling locations in 18 major water bodies in Colombo and within a radius of 20 km around
Colombo. It is noteworthy that Cr levels in many of the water bodies exceeded the
permissible levels for aquatic life in Sri Lanka provisioned by the Central Environmental
Authority. Chromium levels in some water bodies in Colombo (e.g. Kelani River) which
supplies drinking water, also exceeded the safety levels for drinking water recommended by
WHO (i.e. 0.05 mg/L).
Comparative toxicity assessment based on mortality revealed that amphibian larvae were the
most vulnerable to Cr(VI) exposure. It must be reiterated however that environmentallyrelevant
levels did not induce significantly high lethality in any of the three species. Contrary
to lethal effects, sub-lethal toxicity was evident in all three study species exposed to field
levels of Cr. Histological, haematological and genotoxicity effects were observed at
environmentally relevant concentrations and hence provided better monitoring tools than
changes in growth, development and activity. The latter three was not significantly altered by
exposure to field levels of Cr. However, development of amphibian larvae was seen to be
affected at levels marginally higher than typical field levels, which may occur at points of
effluent discharge. Histological analysis was revealed to be the most sensitive method to
detect Cr(VI) toxicity in the three study species and so could be used as an effective
biomarker. Body wall and intestinal epithelium of earthworms, and gills, liver and muscle
tissue of fish and amphibian larvae were comparatively evaluated in a qualitative and
quantitative manner using several histological indices. Amphibians in comparison to other
two taxa, were more prone to histological damage at environmentally relevant Cr(VI)
concentrations. Similarly, haematological assessments were done using standard parameters
(RBC and WBC counts, PCV, haemoglobin concentration, MCV, MCHC, MHC, differential
WBC counts and RBC morphometry). With the exception of RBC morphometry, all
parameters could be used as suitable biomarkers since alterations occurred in a dosedependent
manner. Genotoxic effects were investigated in vivo by means of micronucleus test
and in vitro by assessing tail DNA percentage and Olive Tail Moment (comet assay), in
earthworm coelomocytes and fish and amphibian RBCs. The present study shows that
amphibians are more susceptible to genotoxicity from Cr(VI) exposure. No published
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information is available to date on the use of the micronucleus test to demonstrate heavy
metal induced genotoxicity and the present study is the first to show Cr(VI) induced
genotoxicity in an amphibian. The present study also investigated the production of
superoxide (a Reactive Oxygen Species - ROS) as a result of exposure to Cr(VI) in both
earthworm (using coelomocytes) and amphibians (using RBC). The study demonstrates that
ROS production correlated strongly and positively with Cr(VI) levels and that genotoxic
effects (tail DNA percentage and Olive Tail Moment) also correlated with ROS levels in the
respective cell types. These results provides evidence to strengthen the claim that ROS
production is a possible mechanism through which damage is elicited when exposed to
Cr(VI).
This present study is the only systematic evaluation of comparative toxicity in three local taxa
exposed to environmentally realistic levels of Cr(VI) in Sri Lanka. The results of the present
study showing differential susceptibility of the taxa highlights the limitation of focusing on
individual species to set safety standards. The results of the study can be effectively utilized in
making judgement for the selection of suitable species for biomonitoring for the reassessment
of water quality standards in the country with regards to Cr pollution. Overall it
was evident that the amphibians are comparatively more sensitive to Cr(VI) exposure and
therefore better suited for toxicity assessments over fish and earthworms. The study is the first
to cover all main waterbodies in Colombo and suburbs in determining levels of dissolved Cr,
which has provided a direct comprehensive assessment of Cr pollution in the Colombo city
and suburbs. Although lethal effects were not prominent on the study species, sub-lethal
impacts will lead to reduction in fitness in the long term. Therefore it is important to closely
monitor the sub-lethal effects to avert Cr(VI) induced mortality