The development of genetically inherited resistance to zinc in laboratory-selected generations of the earthworm Eisenia fetida

The capacity of species to adapt both physiologically and genetically to contaminants may allow populations to persist in polluted environments. Such 'adaptation' can have important implications for risk assessment, since it may mean that prediction based on extrapolation of toxicity studies with na?ve populations may prove invalid for long-term contaminated sites. To investigate the evolution of zinc resistance in Eisenia fetida, worms from a previously unexposed population (parent) were selected and reared over two generations (F1, F2) while exposed to zinc in the laboratory. Relative sensitivities of unexposed and selected generations were then compared by exposing parent, F1 and F2 individuals to zinc in contact filter papers tests. Calculation of effect concentrations from this work indicated differences in sensitivity to zinc for successive generations, with higher toxicity values (LC(50), LC(90), LC(99)) found for the selected worms. The increases in resistance found for F1 and F2 worms were confirmed in a discriminating dose study. In addition to comparing the sensitivities of the parent, F1 and F2 generations for zinc, toxicity tests were also conducted with copper to assess if there was evidence of cross-resistance between the two metals. Results indicated similar increases in resistance to copper to those found for zinc. Mechanisms underlying the increased metal resistance were studied in toxicokinetic experiments. Results indicated no clear trends between the three generations indicating that physiological responses, other than differences in kinetic parameters, are responsible for the increased resistance found in the selected worms.     

Effects of pH on the toxicity of cadmium, copper, lead and zinc to Folsomia candida Willem, 1902 (Collembola) in a standard laboratory test system

EC₅₀s for cadmium, copper, lead and zinc were determined for juvenile production of Folsomia candida at pH6.0, 5.0 and 4.5 in a standard laboratory test system. In contrast to most previous studies where metal toxicity was increased at low pHs, in our experiments there was no clear relationship between soil acidity and EC_{50-reproduction} in this species. The EC_{50-reproduction} values (μg g⁻¹) for cadmium and zinc were similar at all three pHs (pH6.0: Cd 590, Zn 900; pH5.0: Cd 780, Zn 600; pH4.5: Cd 480, Zn 590). In contaminated field sites adjacent to primary zinc smelters, zinc is invariably present in soils at concentrations of at least 50 times that of cadmium Thus deleterious effects of mixtures of these metals on populations of Collembola in such sites can be attributed to zinc rather than cadmium.     

Effects of cadmium, copper, lead and zinc on growth, reproduction and survival of the earthworm Eisenia fetida (Savigny): Assessing the environmental impact of point-source metal contamination in terrestrial ecosystems

The earthworm Eisenia fetida (Annelida: Oligochaeta) was exposed to a geometric series of concentrations of cadmium, copper, lead and zinc in artificial soil using the OECD recommended protocol. Mortality, growth and cocoon production were measured over 56 days to determine LC50 and EC50 values. No observed effect concentrations (NOECs) were also estimated. Furthermore, the percentage of viable cocoons and number of juveniles emerging per cocoon was recorded. Cocoon production was more sensitive than mortality for all the metals, particularly cadmium and copper for which NOEC reproduction values were an order of magnitude lower than those for NOEC mortality. However, there was no significant effect of metals on the viability of cocoons. The weights of earthworms declined in all treatments (including the controls) during the experiment. This was probably due to the lack of suitable food in the OECD standard soil medium used. It was concluded that future experiments should include animal manure in the test medium. The LC50, EC50 and NOEC values determined in this study were compared with concentrations of metals in soils in the vicinity of a smelting works at Avonmouth, southwest England. The 14-day LC50 for zinc in Eisenia fetida was exceeded in soils covering an area of 75 km2 around the works, compared to 4.2 km2 for copper and 4.7 km2 for lead. Soil values for cadmium did not exceed the LC50 value anywhere in the region. Similar estimates of relative effects on reproduction confirmed that zinc is most likely to be responsible for the absence of earthworms from sites close to the Avonmouth works. However, the OECD standard test overestimated the potential effects of metals on populations, since earthworms can be found as close as 1 km from the smelting works. The discrepancy between test and field observations was probably due to the greater availability of the metals in the artificial soil.     

Reduced survival and body size in the terrestrial isopod Porcellio scaber from a metal-polluted environment

Terrestrial isopods (woodlice) may show trade-offs in life history parameters when exposed to toxins. We have shown previously [Jones and Hopkin (1996) Functional Ecology 10, 741-750] that woodlice which survive to reproduce in sites heavily polluted with metals from an industrial smelting works do not alter their reproductive allocation. This study investigates whether there are differences in the survival and body size of Porcellio scaber from these same populations. Specimens were collected from eight sites at different distances from the Avonmouth smelter, UK. The sites represented a gradient of concentrations of Zn, Cd, Pb and Cu in the woodlice, from background levels to a grossly contaminated sites close to the smelter. In laboratory trials, the number of days survived by starved males showed a significant decline with increased concentrations of Zn in those animals. The maximum size of both sexes declined significantly from the least to the most polluted sites. The most polluted sites had significantly fewer large animals. The cost of detoxifying assimilated metals appears to be reduced energy reserves and smaller body size.     

Opportunities for Improved Risk Assessments of Exotic Species in Canada Using Bioclimatic Modeling

This paper briefly reviews the process of exotic pest risk assessments and presents some examples of emerging opportunities for spatial bioclimatic modeling of exotic species in Canada. This type of analysis can support risk assessments but does not replace the need for on-going high quality field-based observations to validate and update models. Bioclimatic analysis of several exotic pests is provided to illustrate both opportunities and limits. A link is demonstrated to the National Forest Inventory to characterize timber volumes at risk for one exotic species. Challenges' are both scientific and administrative. More accessible and current field survey data are required to improve models. Our experience is that for many exotic species, historical, and even current, data are not always digital or quality controlled for taxonomic identity and accurate geo-referencing. This inhibits their use for integrated spatial modeling applications.     

The problem of arsenic disposal in non-ferrous metals production

Arsenic is a minor and inevitable component of all inputs to the non-ferrous metals extraction industry but sales are only a small proportion of input. Safe disposal of the excess is a substantial problem. Public perception exaggerates the toxicity of arsenic and generates emotional reactions, whereas arsenic has a natural cycle in the environment and all life is tolerant to traces with detoxication processes to deal with excess. Toxicity data for overload doses to biota in general are poor when required for the formulation of standards for disposal of waste thus making difficult the legal definition of hazardous wastes for appropriate regulation. Suitable tests to determine the stability of a waste for safe disposal are complex, costly, and uncertain against the need for the waste to be in place for a very long time. Further, there is no universal agreement on the principles which should govern the means of disposal of hazardous wastes. Safe disposal of arsenical wastes is thus difficult but practical and convincing solutions must still be devised, guided by thermodynamics and by natural processes. Much judgement and goodwill are required. However, few if any arsenical substances are so stable to moist air that they will not release unacceptable concentrations of arsenic when left in a thermodynamically open dump. Control of hot spot dumps must therefore start with planning of location and configuration, and the wastes must be sealed to exclude air and water and to contain leachates indefinitely. This is very difficult to ensure. Registration, control and testing of waste stability and dump behaviour must be planned on the assumption that leakage will arise at some time in future millennia, a major and expensive logistical problem. Adsorption of arsenate by soils and aquatic sediments is an important buffering and fixing process for any leakage, but waters can still be polluted. It is, however, argued that deliberate retention of leachate can lead to problems from uncontrolled future leakages, and thus that "hot spot dumps should be designed to allow controlled leakage within the capacity of the receiving environment. Better still would be efficient dilution and dispersal. Marine disposal may be politically unattractive, but the arsenic reports to sediments and the process copies nature. It is probably the best environmental disposal option where practicable.