The degradation of soils due to various anthropogenic stress factors is alarming. Although chemicals are a major reason for soil degradation, most ecologists are not interested in studying such effects. We try to wake their interest by addressing a number of unsolved soil ecotoxicological problems that are related to disturbance ecology, biodiversity, ecosystem functioning and modelling. Features distinguishing chemical from natural stress render promising new aspects in disturbance ecology. Ecotoxicological studies are ideal models of disturbance, particularly regarding frequency, intensity or multitude of stress. Patterns of secondary succession after a major chemical damage can directly be related to the intermediate disturbance hypothesis. More knowledge on altered life history patterns following stress could support both evolutionary ecology and risk assessment. We raise the question if inherent resource competition makes communities more vulnerable to stress. Three aspects of ecotoxicological risk assessment are introduced: (1) exposure and bioavailability, which is directly connected to environmental heterogeneity; (2) tests on ecosystem functioning, suffering from major drawbacks; and (3) modelling. Here, promising approaches exist but need substantial input for being applicable to soils. Ecological modelling should put more emphasis on simulating both natural and chemical disturbances, including behavioural aspects and environmental variability. Finally, research needs for ecological risk assessment in soils are derived such as a simple system to assess the impact of chemicals on soil biodiversity, the inclusion of behavioural changes of keystone species or the consideration of density-dependent effects. Common research efforts of basic ecologists and soil ecotoxicologists could render a lot of mutual, benefits. (C) 2007 Gesellschaft fur Okologie. Published by Elsevier GmbH. All rights reserved.

Certain substances may be hazardous to ecosystems. To be able to preserve the structures and functions of ecosystems, knowledge is required to qualify and quantify such hazards. To this end, biotests are indispensable tools. For the development and/or choice of biotests, special attention has to be drawn to conflicts between scientific demands and practical constraints. From a purely scientific point of view, experiments should be designed to maximise the ecological relevance of the obtained results. However, this often collides with the limited resources (budget, time, manpower) available. Furthermore, societal issues (e.g. animal welfare) have to be taken into account. Thus, it is necessary to develop a scientifically sound testing approach that avoids unnecessary animal testing, keeps the costs low, and can be performed within a short timeframe. The different perspectives of ecology, environmental toxicology, and environmental chemistry should be integrated into a balanced ecotoxicological approach. Accordingly, we propose a dynamic testing strategy, which is adapted to the substance (or substance group) in question and its mode(s) of action. (C) 2007 Gesellschaft fur Okologie. Published by Elsevier GmbH. All rights reserved.

Oil pollution is a world-wide prevalent threat to the environment and the remediation of oil contaminated soils, sediments and water is a major challenge for environmental research. Bioremediation is a useful method for soil remediation, if pollutant concentrations are moderate and non-biological techniques are not economical. The scope of this study was to investigate if earthworms and/or additives (organic material) can enhance the microbial degradation of petroleum hydrocarbons in soil.Two experiments were conducted. The aim of the first was to investigate the influence of three different earthworm species (Eisenia fetida, Allolobophora chlorotica, and Lumbricus terrestris) on the degradation of a crude oil contaminated soil (9500 mg total petroleum hydrocarbons (TPH)/kg soil dry wt.). A significant decrease in the TPH concentration was observed in treatments with earthworms, compared with the samples without worms. A decrease of the marker components phytane and pristane in the earthworm treatments indicated microbial degradation. Correspondingly, increased microbial activity (soil respiration) was observed in these samples, probably due to earthworm stimulation. Mixing of the soil (simulating burrowing activities of the earthworms), however, did not lead to a decrease in the TPH concentration.The aim of the second experiment was to investigate the influence of additives and/or earthworms (Lumbricus terrestris) on TPH degradation in a crude oil polluted soil (5000 mg/kg TPH). Criteria for the choice of the additives were cost effectiveness and short transport distances. Industrial waste products were therefore chosen: (i) coffee grounds; (ii) horticultural waste (grass and wood chips); and (iii) brewery mash. Additives were either mixed into the soil or dispersed on the soil surface in mass concentrations 1:10 (additive: soil). After 28 days, significant TPH degradation (30-35%) was only observed in treatments with mash (mixed) and with earthworms without additives, although soil respiration measurements showed enhanced microbial activity in all treatments with worms or additives. It was assumed that micro-organisms prefer the more easily available additives as nutrient sources over the less easily degradable, nitrogen deficient, long-chain crude oil. Thus, the application of additives does not necessarily enhance bioremediation. Despite high mortality, earthworms may trigger the degradation process and might therefore, be applied in the remediation of oil contaminated soil with moderate TPH concentrations. (c) 2006 Elsevier B.V. All rights reserved.

Despite the cutback of the use of antifouling paints containing tributyltin (TBT), harbour sediments are still “hot spots” for organotin pollution, which is one of the most toxic substances for aquatic organisms. Harbours have to be freed constantly of suspended sediments, to guarantee unhindered shipping. The deposition of these TBT contaminated sediments on rinsing fields is supposed to comprise a minimisation of the risk potential for humans and environment. To investigate if TBT contaminated sediment might present a hazard to the existing soil fauna, a risk assessment with earthworms was performed. The original TBT contaminated sediment induced 94% mortality, compared to 2% in the uncontaminated standard Lufa soil. It was assumed that the high salinity (23 dS/m) was the reason for the mortality rather than the TBT concentration of 600 μg/kg soil (dry weight). To reduce the soil salinity, the TBT substrate was first washed with deionised water and then mixed with the uncontaminated artificial OECD soil (=TBTmix), which resulted, however, in a lower TBT concentration (132 μg/kg soil dw.). The uncontaminated OECD reference soil resulted in high earthworm mortality (34%). Despite the reduced salinity (10 dS/m) and lower TBT concentration, the TBTmix substrate induced high mortality rates (42%), reduced reproduction (17% compared to the control) and resulted in a significant substrate avoidance of 92%. Consequently, the landfilling of the TBT contaminated harbour sludge might (i) present a hazard to the existing soil fauna at the rinsing fields due to high salinity and the TBT contamination, and (ii) a quick recolonisation of the contaminated substrate by earthworms can not be expected.

Oil spills are one of the most common types of soil pollution. Bioremediation has become an attractive alternative to physicochemical methods of remediation, where feasible. Earthworms have been shown to stimulate the degradation of petroleum hydrocarbons in soil, and it was hypothesized that the role of earthworms in remediation lies in the enhancement of an oil degrading microbial community. The aim of this study was to characterize microbial activity and community dynamics in oil-contaminated soil incubated with or without earthworms. Three earthworm species (Eisenia fetida, Allolobophora chlorotica and Lumbricus terrestris) were incubated in crude oil polluted soil (ca. 10,000mg/kg total petroleum hydrocarbons (TPH)) and a reference soil for 28d. Control treatments with manual mixing and/or cattle dung amendment were also included. In the oil-contaminated soil, respiration and concentration of microbial biomass was significantly enhanced by earthworm amendment, and TPH concentrations decreased significantly. These effects were less evident in treatments with A. chlorotica, possibly due to a difference in behavior, since individuals of this endogeic species were found in a state of inactivity (aestivation). Microbial community dynamics were described by phospholipid fatty acid (PLFA) analyses. After 28d, similar shifts in the soil PLFA composition were observed in the oil-contaminated soil irrespective of worm species. Fungal:bacterial ratios were increased in the presence of worms, but also by addition of dung as a food source, indicating a non-specific effect of metabolizable substrates. In contrast, the fatty acids 17:1ω8 (=Δ9-heptadecenoic acid) and 20:4ω6c (arachidonic acid) were specifically stimulated by the presence of earthworms in the oil-contaminated soil. The results showed that earthworms can contribute positively to bioremediation of oil-contaminated soil, but that the effect may be species-dependent.

Motivated by the prevailing need for a sustainable development and taking the principles of Green Chemistry as a starting point, the present paper describes new and updated findings regarding a sustainable product design for ionic liquids. The focus is on environmental risk. Nevertheless, cytotoxicity testing and first indicative results from a genotoxicity study extend present knowledge also with regard to possible effects on humans. The structural variability of commercially available ionic liquids as well as the abundance of theoretically accessible ionic liquids is illustrated and the consequences for an integrated risk assessment accompanying the development process are discussed. The side chain effect on toxicity for imidazolium type ionic liquids was confounded by more complex biological testing. Also, an influence of an anion on cytotoxicity is shown for the first time. Testing of presumed metabolites of the imidazolium type cations showed a significantly lower biological activity in cytotoxicity studies than their parent compounds. The importance of a purity assessment for ionic liquids is pointed out and a collection of methods that is believed to be adequate is presented. In addition to risk analysis, the use of life cycle analysis for the multi-objective problem of designing ionic liquids is sketched and an eco-design scheme for ionic liquids is proposed. In conclusion, the paper illustrates the complex nature of the development processes ionic liquids are currently undergoing and provides guidance on which aspects have to be kept in mind.

Within the scope of a phytoremediation project, the toxicity of 2,4,6-trinitrotoluene (TNT) contaminated soil (and its toxic metabolites) on earthworms was assessed. In addition to the standard acute and reproduction tests (ISO 11268), an avoidance response test was applied. The test methods covered all important ecological relevant endpoints (acute, chronic, behavioral). At a concentration of 1142 mg/kg, TNT caused significant toxic effects in all test methods, but at lower test concentrations no significant acute or reproduction toxic effects could be observed. The avoidance response test, however, showed significant repellent effects at a concentration of 29 mg/kg TNT and therefore proved to be more sensitive than the other tests in this case. Results of the earthworm tests compared well with results of an ecotoxicological biotest battery. Thus, earthworm toxicity tests are useful tools for terrestrial risk assessment but require a hierarchy of test designs that differ in effect levels (behavior, sublethal, lethal). Whereas higher concentrations of a pollutant can easily be assessed with the acute test (which requires lethal concentrations to show an effect), contaminated soils with lower (sublethal) pollutant concentrations require more sensitive test methods such as reproduction or behavioral tests in their risk assessment.

Endpoints in earthworm ecotoxicology scheduled in guidelines are mortality and reproduction rates. However, not only the direct influence of pollutants on population parameters but also changes in behaviour such as substrate avoidance can have an important impact on soil ecosystems. In practice two different avoidance response tests are applied in earthworm ecotoxicology: (i) a six-chamber test system and (ii) a two-chamber test system. Both avoidance response-test systems were compared to establish their respective advantages and disadvantages in order to advance the standardisation of behavioural tests. The earthworm avoidance-response tests were applied in addition to the standard acute and chronic earthworm toxicity tests (ISO 11268) in order to compare the sensitivity of the test endpoints.