Hydropsychid (Trichoptera, Hydropsychidae) gill abnormalities as morphological biomarkers of stream pollution

1. The use of morphological gill abnormalities of hydropsychid larvae was assessed in Hydropsyche siltalai larvae exposed to cadmium in the laboratory and Cheumatopsyche lepida and H. pellucidula larvae collected from a polluted river. Two biomarkers were evaluated: (1) Hydropsychid abnormality incidence (HAI), referring to the proportion of individuals with at least some abnormalities, and (2) Hydropsychid gill abnormality indice (HYI), referring to the average number of abnormal gill tufts for all individuals. 2. Abnormality–contaminant relations for both biomarkers were established by studying gill responses along gradients of increasing cadmium and organochlorine concentrations. A cadmium gradient was verified in laboratory exposures, whereas the concentrations of polychlorinated dibenzo‐p‐dioxin (PCDD), dibenzofuran (PCDF) and diphenyl ether (PCDE) of the aquatic moss Fontinalis antipyretica were used as measures of an organochlorine gradient in the field. 3. Morphological abnormalities were easily distinguished as heavy darkening, malformation and/or reduction of single gill tufts. Darkening of the gills appeared to start either at the basal or distal ends. 4. A marked increase of HYI values with increasing Cd concentration reflected a clear abnormality‐contaminant relation, whereas the mere dicotomic classification of larvae as normal or abnormal (HAI) was less informative. High values of both HAI and HYI were associated with high contamination. A significant positive correlation was found between organochlorine concentration in mosses and biomarker values for H. pellucidula, but not for C. lepida. 5. We conclude that HAI indicates deleterious effects, but fails to quantify the severity of degradation. Use of individual gill tufts, as response units in deriving HYI, revealed a simple solution to the quantification problem. Further research into the ecological meaning, physiological background and patterns of gill abnormality is recommended for assessing the applicability and relevance of hydropsychid gill biomarkers.     

Acid-induced acute toxicity of aluminium to three species of filter feeding caddis larvae (Trichoptera, Arctopsychidae and Hydropsychidae)

1. Arctopsyche ladogensis , Hydropsyche angustipennis and Hydropsyche siltalai larvae were exposed to nominal aluminium concentrations of 0, 625, 1250, 2500 and 5000 μg Al l^–1 at pH 5.0 for 96 h. Larvae reared at pH 6.4 and without any aluminium treatment were used as controls. Morphological abnormalities in the anal papillae of the larvae were used as the response variable in estimating the median effective concentrations (EC₅₀) of aluminium.
2. No morphological abnormalities were observed in the control larvae. Only a few individuals of A. ladogensis had darkened anal papillae at pH 5.0 without additional aluminium treatment, whereas increasing aluminium concentrations significantly increased the number of individuals in all species displaying darkening and reduction of the papillae.
3. A. ladogensis appeared to be the most sensitive species to increasing aluminium concentrations, as reflected by the significantly lower mean EC₅₀ value for this species compared with those of H. siltalai and H. angustipennis . H. angustipennis larvae were the most tolerant to aluminium.
4. The results indicate that interspecific differences in sensitivity to aluminium may be a key factor influencing the guild structure of filter feeding caddis flies in acidified streams. The results also imply that toxic effects of aluminium on filter feeding caddis larvae occur due to the impairment of normal osmoregulation processes via damage to the ion-regulatory organs.     

Acid-induced acute toxicity of aluminium to three species of filter feeding caddis larvae (Trichoptera, Arctopsychidae and Hydropsychidae)

1. Arctopsyche ladogensis , Hydropsyche angustipennis and Hydropsyche siltalai larvae were exposed to nominal aluminium concentrations of 0, 625, 1250, 2500 and 5000 μg Al l^–1 at pH 5.0 for 96 h. Larvae reared at pH 6.4 and without any aluminium treatment were used as controls. Morphological abnormalities in the anal papillae of the larvae were used as the response variable in estimating the median effective concentrations (EC₅₀) of aluminium.
2. No morphological abnormalities were observed in the control larvae. Only a few individuals of A. ladogensis had darkened anal papillae at pH 5.0 without additional aluminium treatment, whereas increasing aluminium concentrations significantly increased the number of individuals in all species displaying darkening and reduction of the papillae.
3. A. ladogensis appeared to be the most sensitive species to increasing aluminium concentrations, as reflected by the significantly lower mean EC₅₀ value for this species compared with those of H. siltalai and H. angustipennis . H. angustipennis larvae were the most tolerant to aluminium.
4. The results indicate that interspecific differences in sensitivity to aluminium may be a key factor influencing the guild structure of filter feeding caddis flies in acidified streams. The results also imply that toxic effects of aluminium on filter feeding caddis larvae occur due to the impairment of normal osmoregulation processes via damage to the ion-regulatory organs.     

APPLIED ISSUES Species- and population-specific responses of translocated hydropsychid larvae (Trichoptera, Hydropsychidae) to runoff from acid sulphate soils in tin River Kyrönjoki, western Finland

1. The effects of runoff from acid sulphate soils on Hydropsyche angustipennis, H. siltatai and Ceratopsyche nevae larvae were studied. H. angustipennis occurs in both contaminated and uncontaminated rivers, whereas H. siltalai and C. nevae occur only in uncontaminated rivers. Larvae were translocated in PVC-tubes to contaminated sites. Larvae returned to an uncontaminated river were used as a control. 2. Heavy larval mortality and a high incidence of morphological abnormalities were observed in larvae translocated to the contaminated, acid dyers. In the control river pH remained near 6 and no larval mortality or morphological abnormalities were observed. In the most contaminated river nutrient concentrations, amount of organic matter and pH increased substantially after the flood. 3. Mortality and incidence of abnormalities were significantly higher in H. siltalai and C. nevae than in H. angustipennis. As metal concentrations decreased and pH increased, the larvae of all species developed normally, except in the most contaminated river, where only H. angustipennis appeared to tolerate the increasing load of nutrients and organic matter. 4. Reciprocal translocation of H. angustipennis larvae between contaminated and uncontaminated rivers revealed significant differences in larval development and the occurrence of abnormalities among sites and populations. At both sites, larvae originating from the contaminated site grew more slowly than did larvae from the uncontaminated site. Morphological abnormalities were detected only in H. angustipennis larvae translocated from the uncontaminated to the contaminated site. 5. The results suggest that species-specific differences in sensitivity to acidification, metal contamination and eutrophication are the major determinants of hydropsychid guild structure in the River Kyrönjoki. Further, population-specific differences in growth and occurrence of morphological abnormalities in the H. angustipennis larvae may reveal either phenotypic adaptation or evolution of resistance to runoff from acid sulphate soils.