Verunreinigte Böden

This article discusses the evaluative criteria which are applied for the assessment of contaminated soils. Guide values for materials in the soil (reference values, test values and action levels). Such guide values can be derived based upon either functional or constitutional criteria. The leachate from the soil must be analyzed for noxious materials in order to ensure the conservation of both ground- and surface-waters. Furthermore, existing concepts and drafts for evaluating soil contamination are discussed. The great diversity of the 37 regulatory publications for evaluating soil contamination is due to 1. different purposes these guidelines are aimend at, and 2. varying philosophies with regard to the degree of safety which is considered to be acceptable:

1. The approach of the LAGA (Länderarbeitsgemeinschaft Abfall-German federal cooperative for waste regulation) is to merely avert dangerous effects of polluted land rather than to take precautionary measures.
2. The approach of the state of Baden-Württemberg is to combine precautionary activities and defensive procedures in one scheme with the technical and financial feasibility as criteria for the final decision.

A summary of the valid legislation is discussed, based on the specific regulatory works of the individual German states:

- The federal soil protection act and the directives based on it

- Inherent problems with deriving test values from basic toxicological data as well as the question of a tolerable cancer risk level

The procedure of linking the test values with a concrete danger to health that was designed for the federal soil protection act is discussed and compared with an alternative procedure. A presentation is given of the LABO (Länderarbeitsgemeinschaft Bodenschutz — German federal and state cooperative on soil conservation) utilization concept for soils: The use of test values for assessing soil materials with regard to particular utilization goals. The article quotes the ?Guideline for monitoring the success in soil cleanup operations” as compiled by the GDCh working group on ?Environmental chemistry and ecotoxicology” (1996). This guideline provides a review of the evaluatory concepts applied in the German states of Hamburg, North Rhine-Westphalia, Brandenburg, Rhineland-Palatinate, Hessen, Baden-Württemberg, as well as those of the German federal cooperative for waste regulation (LAGA). The respective procedures and specifications of Holland, Canada, the USA are also noted in this guideline.     

Langfristigkeit ökosystemarer Forschung

Time in environmental science continues to be almost neglected. In connection with rising ecological problems long-term research, as is necessary for the evaluation and prediction of environmental conditions, seems to be an exception. Complex ecosystems, e.g. terrestrial and marine systems, however, are characterized by long lasting natural time-scales which must be taken into account by analyzing them. In this context the role of time in ecosystems research becomes important. Therefore, a data base was conceptualized that could take up the main characteristics of ecosystematic analyses. Annual research reports of ecosystem research centers were revised for taking them up into the data base. In this way it is possible to evaluate the pool of data on special aspects, especially on the time parameters of the analyses. One result — besides a partial unequality of the time scales in experiment and reality — is that long-term research in terrestrial ecosystems is very rare. The reasons for this are various, but cannot divert from the need for a greater consideration of longterm observation of the ecosystems. Otherwise the ecosystematic research will not be able to meet their tasks of evaluation and prediction.     

Batterienrecycling: Möglichkeiten zur Erhöhung der Rücklaufquote

Separate collection and exploitation of used batteries facilates the recycling and eventual waste management of such heavy metals as mercury and cadmium. It is thereby possible to regain raw materials like zinc, manganese and iron for the raw material cycle. Although the collection and recycling of used batteries in Switzerland is financed by a prepaid disposal fee, their returning rate of almost 60% is too low for several reasons. A questionnaire survey carried out on 2000 households revealed the following frequenthy: People collecting paper, glass, aluminium, compost and tinplate, are more separate used batteries from ordinary garbage. The number of collecting points is supposed to be sufficient, but not all of them are sufficiently marked. The prepaid disposal fee (VEG) should become obligatory so that it would be possible to compensate the collecting points. It is not obvious from the results of the survey if the introduction of a deposit of batteries would raise the retourning rate. As far as advertising is concerned, only the “battery bag” sent to every household by the BESO seemed to influence the collecting behaviour in a positive way, poster advertising had only little effect. Appeals in newspapers, radio and television did not show any changement of the collecting behaviour. However, information and knowledge about batteries and their recycling do have a positive influence in the collecting behaviour of the consumers in this specific case.     

Chlorcarbazole in Böden

Goal and Scope

In soil samples taken from several locations throughout Bavaria, the detection of p,p′-DDT by GC/MS was impeded by a superimposed peak. The authenticity of this compound, which has been identified as dichlorocarbazole by mass spectra databases, is confirmed and some characteristics of its occurrence in soils are described.

Methods

The authenticity of the unknown compound has been checked by comparing the low resolution mass spectra and chromatographic retention times with those of standard compounds. Some methodical studies concerning extraction and clean-up were also carried out.

Results and Conclusion

Mass spectra and retention of the unknown compound are identical with that of the 3,6-dichlorocarbazole standard compound; additionally, a second chlorocarbazole was found with mass spectrum and retention similar to 3-chlorocarbazole. In many topsoils (A-horizons) and subsoils (B-horizons) from 200 locations of different land-uses, the dichlorocarbazole could be detected. In contrast to PAH and other POPs, maximum concentrations occurred in the A- and upper B-horizons of forest soils rather than in the organic layers. Assuming the environmental distribution properties of the chlorocarbazoles to be similar to those of the PAH, this could indicate that the chlorocarbazoles are not deposited from the atmosphere as a result of anthropogenic activities but might be generated by natural processes in situ.

Recommendation and Perspective

To our knowledge, the occurrence of chlorocarbazoles in soils of unpolluted sites has not been previously described. Their widespread occurrence in relatively high concentrations and their detection using analytical standard procedures is surprising and requires further examination.     

Cäsium-137 in Böden saarländischer Waldökosysteme

Scopes and main features

In order to explain the behaviour of the artificial radioisotope¹³⁷Cs towards landscape resources in the Saar-Lor-Lux-Region, the cross-border region between southwestern Germany/ Saarland, France/Lorraine and Luxembourg, regional distribution as well as downward translocation and depth functions of¹³⁷Cs in the main soil substrates of forest ecosystems in the Saarland were investigated.

Results

The study shows that the highest¹³⁷Cs activities are found in the north of the Saarland, whereas the south and south-eastern regions show distinctly lower concentrations of¹³⁷Cs. Migration rates range between 0.25 cm/a and 1.0 cm/a. On an average, the highest migration rates were found in the clayey-silty substrates of the lime stone areas in theMuschelkalk regions (Middle Triassic) (0.66 cm/a), followed by the loamy substrates of Lower Permian clastic sediments (Unterrotliegendes) (0.53 cm/a) and the sandy substrates of theBuntsandstein areas (Lower Triassic sandstone) (0.41 cm/a). 90 to 95% of the¹³⁷Cs activities in the clay-poor soils of the Unterrotliegendes and the Buntsandstein were traced in the upper 10 cm of the humus topsoil. The substrates of the lime stone areas (Muschelkalk), in contrast to this, reveal a¹³⁷Cs activity of only 70–76% at the same depth.

Conclusions

Due to the fact that the primary and secondary pores of the soil pore system, in their function as translocation pathways, decrease with increasing soil depth, a significant reduction in the migration rates of¹³⁷Cs can be expected with increasing soil depth. On the other hand, the maximal migration depth of 40 cm found in shallow soils on jointed parent material, as well as on sites with high groundwater tables, implies a possible contamination of near-surface groundwater.

Future outlook

Based on the results of this study, a permanent monitoring of¹³⁷Cs was added to the long-term Soil Monitoring Program run by the Federal Administrative Office of Environment of the Saarland (Landesamt für Umweltschutz des Saarlandes)     

Zur Humusausstattung ostbayerischer Mittelgebirgsböden

Background

Important properties and processes of soils are influenced by their humus contents. Therefore knowledge about the humus status of soils is an important requirement for a meaningful evaluation on dynamics and risk potentials.

Aim

Based on the extensive database of the Bavarian Environment Agency typical humus content and humus storage are compiled for soils of the Bavarian and Upper Palatinate Fores. Their importance for questions on soil and environment is estimated.

Results and Discussion

The evaluation revealed rising soil organic matter with an increasing cool and moist climate on the mountains of the Bavarian and Upper Palatinate Forest. This is particularly true for the mineral soil above 600 m above sea-level, where more organic matter is stored than in the humus layer. Depending on altitude the calculated total humus stock of soils varies between 12 and 40 kg^*m^?2, which means medium to very high humus contents. The highest humus stock occur between 900 and 1200 m above sea-level, where intensively rooted ‘Lockerbraunerden’ are prevailing. The somewhat lower humus content in soils above 1200 m above sea-level (about 5 kg^* m^?2) is explained by a shallow indurated horizon, that reduce the rooting to the upper 3–5 decimetres. The even though considerable humus stock of this concrete like indurated horizon is therefore explained by infiltration. The remarkable thickness of organic layers above 1200 m above sea-level is probably not only a result of climate, but also of a difficult decomposition of the prevailing spruce litters.

Conclusions

The high contents of organic matter in the examined soil should release appreciable amounts of CO₂ if there will be a change in climate. Furthermore a decomposition of humus may considerably worsen the supply with water and nutrients on these sites.     

Ergebnisorientierte Honorierung ökologischer Leistungen der Landwirtschaft

Background and Objectives

As an instrument of agro-environmental economic policy, remuneration to farmers for implementing ecologically sound practices are often identified as beingthe alternative to inefficient or unpopular legal instruments. This paper shows that such an approach assumes to be an idealized conception of the way in which economic instruments work. Only result-oriented payment is capable of matching such an idealized conception; hence, the conditions are accordingly ambitious.

Key aspects

Starting from a definition of result-oriented remuneration for ecological benefits, this approach is systematically contrasted by action-oriented payments. Either is examined in respect to its comparative efficiency enabling assessment of the potential of both instruments. In the second section, the limits of the approach using result-oriented payments are discussed in relation to the corresponding prerequisites set down for them.

Results

The key criterion for distinguishing between result-oriented payments on the one hand and action-oriented payments and legal instruments on the other is the number of options available to the farmer when he/she chooses to take advantage of the payments. On the basis of this criterion, the following advantages emerge from the economic (rewards-based) approach: it promotes self-interest, increases innovative potential, reduces informational asymmetries, promotes continuity, promotes co-operative practice, promotes intrinsic motivation and, finally, it achieves a distribution of risks between farmers and society. However, one essential requirement for applying such instruments are indicators attached to payment. The attempt to develop such indicators reveal three central problems: the complexity of cause-and-effect relations, the diversity of environmental objectives and the normativity of the process by which indicators are devised. These problems simultaneously define the limits of the instrument of result-oriented payments for ecological benefits.

Conclusions

No general statements can be made about whether result-oriented payments are preferable to other instruments, as this depends on the concrete circumstances and, in particular, on the specific environmental issues involved, along with the possibilities of developing environmental indicators. However, from the economic point of view, the benefits of result-oriented payments are obvious, as long as the prerequisites for the application of this instrument can be met.

Further Research and Recommendations

Given the persuasive benefits of result-oriented payment from an economic point of view, more efforts should in future be made to test the practicability of such instruments. Two examples of result-oriented payment are discussed in this paper.     

Biozönotisches Testverfahren (PICT-Konzept)

Goal and Scope

A community test is introduced usingin situ periphyton communities and the pollution induced community tolerance for ecotoxicological testing. It was the aim of the study to evaluate the feasibility of the test for the assessment of xenobiotics and contaminated environmental aquatic samples.

Methods

The herbicides Isoproturon and Prometryn were tested using standardised microphytobenthic communities of differing contamination. A pulse-amplitude-modulated fluorescence based method was used to detect the impact of the herbicides on the photosynthetic system of the microalgae.

Results and Conclusions

Despite the variability of the ecosystem (samples were taken from different sites and varying taxonomy throughout a period of two months), the tests show high sensitivity and good reproduction features. EC₅₀ values of 0.025 mg L^?1 for Isoproturon and 0.016 mg L^?1 for Prometryn were evaluated. These effect concentrations ranged in the same order of magnitude as the results derived from cell reproduction inhibition tests withScenedesmus vacuolatus (0.029 mg L^?1 for Isoproturon and 0.012 mg L^?1 for Prometryn). For Isoproturon, the test was able to differentiate effect concentrations for single algal classes within natural communities. The test was used to assess a contaminated effluent entering a stream (Spittelwasser) in the region of Bitterfeld. The effluent originate from a local chemical industry site, where Prometryn was produced for 4 decades. According to the PICT-concept (pollution induced community tolerance), we hypothesed that periphyton taken downstream of the effluent was more tolerant to Prometryn than uncontaminated communities. It could be shown that the herbicide caused a shift in the concentration response relationships of communities from different contaminated sites, indicating the development of tolerance. We conclude that the test using periphyton communities and considering the development of tolerance is able to evaluate a causal analysis of chronic effects of pollutants on community level. The multi-species test usingin situ communities reflects a higher biological organisation level than a single species laboratory test.

Outlook

The PICT-concept could be used for ecological risk assessment of pollutants in the environment bridging the gap between single species laboratory testing and time consuming mesocosmos and field studies.     

Messung und Quantifizierung von Mineralölkohlenwasserstoffen

Investigations concerning the measurement and evaluation of mineral oil hydrocarbons using Fourier-transform-infrared (FT/IR-)-spectroscopy,¹H-Nuclear magnetic resonance (¹H-NMR)-spectroscopy and Capillary gas chromatography — Flame ionisation detection (GC-FID) are presented. By means of various mineral oils and three certified reference materials (CRM) all tested methods were within a ±7%-range to the mineral oil nominal value and the 95% confidence intervals of the CRM’s, respectively. The GC-FID evaluation could be done without calibration using an relative response ratio of mineral oil to an internal standard (n-tetracontane). A¹H-NMR-method was developed for the quantitative determination of mineral oil hydrocarbons, successfully applied down to 0.2 mg/ml. Due to the determination limit achieved, the¹H-NMR-spectroscopy gain in importance as a reference method for the analysis of mineral oils.     

Teil V: Bewertung landwirtschaftlich-industrieller Stoffströme

Agricultural and industrial production chains as product lines are connected and their assessment is performed for a varnish based on linseed oil that is almost completely composed of renewable raw materials. Using a production line analysis, the ecological and social effects of the production are assessed, and different assessment techniques for ecological assessment are used as well. The life cycle inventory results from a material flow analysis including pre-production chains. For optimisation, a scenario of conventional agricultural linseed oil production against ecologically produced linseed oil is assessed. All assessment methods identify the same aspect of the product as the most important: The content of volatile organic compounds (VOC), that are released during usage. Further problems such as waste in the oil mill, emittance of acidic substances (mostly NO_x) from burning and heavy metals from tinplate production for containers are identified only from one or another of the assessment methods, a feature which stresses the influence on results from the choice of method. All methods prefer the ecological production of linseed, but the significance regarding the system boundaries is low (0.6% UBP, 1.7% Eco-indicator) due to dominating VOC-emissions. The use of material flow analyses in LCA is possible for agricultural production, especially seamless connection is provided between the different production steps. Also parameterisation is easy so that the defining of scenarios is efficient and transparent.     

Die ökologische Bewertung von Seeufern in Deutschland

Goal and Scope

Details about the ecological function of lake shores as ecotones between land and lakes are not well-known. These ecotones are also heavily exploited and, in part, considerably changed. Whereas anthropogenic nutrient loading is decreasing, structural changes are increasing. Unfortunately, there is a deficit in methods of evaluation and decision processes.

Main Focus

Even the EU-water framework directive was no remedy for this deficit, as lake shores were included only implicitly. In this article several evaluation methods and their conceptual groundwork are presented. However, these methods were not developed for lake shore research. Therefore, criteria are proposed which could fulfill the specific demands of lake shore assessments. The management of lakes shores should consider structural and biological parameters, and be agreeable to local residents.

Results and Conclusions

In addition to conventional biodiversity methods, the ecology of lake shores could also be represented by a functional food net, for example in benthic invertebrates. But even quantification of biodiversity alone creates many problems. A simple biodiversity index cannot meet all the demands placed on a method of evaluation in complex situations, especially when coupled with additional information on structure, practicability, costs, etc. For these reasons, assessments for future management cannot be based on such an index.

Outlook

A possible approach to include this complexity in assessments is to apply mathematical models and theoretical order concepts.     

Entwicklung von ökotoxikologischen Instrumenten und ihre rechtliche Implementierung zur marinen ökologischen Risikobewertung von Chemikalien, Pestiziden und Baggergut

Background, aim, and scope The marine environment is often the final sink for pollutants, especially for persistent organic pollutants (POPs) and for persistent, bioaccumulative and toxic (PBT) substances. The body burden of marine top predators in the Baltic Sea, in the North Sea and also in the Arctic seas is alarming. Thus, the question was investigated if the European environmental law considers a prospective marine ecological risk assessment of chemicals, pesticides and dredged material before they are launched on the market or disposed to the sea. Results The analysis of European environmental law showed that the European environmental protection goals demand a good quality status of coastal waters until 2015 (Waterframework Directive) and a good quality status of European seas until 2020 (Marine Strategy Directive), but a specific marine ecological risk assessment of chemicals and pesticides is not sufficiently required in current European legislation. Discussion It was shown that the ecological risk assessment for freshwater ecosystems is, due to the pecularities of pollutant impacts in the marine environment, not adequate to predict marine effects and to protect the marine environment sufficiently. A statistical analysis of international databases on the relative toxicity of narcotics revealed that marine organisms can be significantly more sensitive than freshwater organisms towards substances with an unspecific mode of action (narcotics). Approximately 60?% of the industrial chemicals are classified as narcotics by their mode of action. Thus, this substance class is of environmental importance. Due to the hydrophobic properties and the low solubility of narcotics in seawater, the ecotoxicological assessment of marine sediments was of interest. An estuarine and marine bioassay test set was established and further developed to assess the ecotoxicological potential of brackish and seawater sediments. It was important that the test procedures were adapted to brackish and marine conditions and were harmonised between each other as well as on the international level. Conclusions Beside two bioassays for the ecotoxicological assessment of elutriates of marine and brackish sediments (bacteria bioluminescence test and marine algae test), the implementation and further development of the whole sediment bioassay with the marine amphipod Corophium volutator was important for enhancing the risk assessment. In order to gain a more standardised, all-season available test organism, the marine amphipod was for the first time reproduced under laboratory conditions the whole year round (also in winter), which is the essential basis for the urgently needed chronic whole sediment bioassay. The results of this investigation were implemented in the international (ISO), European (EN) and national (DIN) standardisations. Therefore, a standardised test set is ready for the implementation in the marine ecological risk assessment of chemicals, pesticides and dredged material in international, European and national legislation. Recommendations and perspectives Recommendations to improve the implementation of a marine risk assessment in European regulations are given with the goal to reach the internationally required objective of a sustainable development of the seas.     

Terrestrische ökotoxikologische Testmethoden für die Tropen

Goal, Scope, and Background

Soil organisms play a crucial role in the terrestrial ecosystem. Plant Protection Products (PPPs) are known to affect soil organisms and might have negative impacts on soil functions influenced by these organisms. Little research has been done to day on the impact of PPs on tropical ecosystems. Therefore, in this study it was investigated whether fate and effects of pesticides differ between tropical and temperate regions and whether data generated under temperate conditions can be used for the Environmental Risk Assessment (ERA) in tropical regions.

Methods

In the first part of this study, the effects of two fungicides (Benomyl and Carbendazim) and one insecticide (lambda-Cyhalothrin) on soil invertebrates (i.e. earthworms and arthropods) were evaluated in laboratory tests modified for tropical conditions (temperature, soil, test species). Besides using some native species, the tests were done mainly with two (temperate and tropical) strains of earthworms (Eisenia fetida) and the peregrine isopod speciesPorcellionides pruinosus as standard test species. The chemicals were spiked in two natural and two artificial soils. A tropical artificial soil (TAS), containing a tropical fern product (Xaxim) or coconut coir dust as organic matter, was developed in this study.

Results and Conclusions

The results from the laboratory tests showed that all three test chemicals differed from those gained under temperate conditions. In the case of the fungicides the toxicity was lower but in the case of the insecticide higher under tropical than under temperate conditions. The native tropical earthwormPontoscolex corethrurus reacted more sensitively against Carbendazim in comparison to the standard test speciesEisenia fetida.

Recommendation and Perspective

Details of the environmental risk assessment of the three model chemicals based on the results of the laboratory described here (and including the results of higher tier tests (semi-field and field tests)) will be described in Part 2 of this series     

Umweltschäden durch Heizöl nach Hochwasserereignissen

Background Due to high safety measures in production, transport and storage of fuel oil it rarely occurs, that fuel oil will be released in the environment. One exception of this experience was the fuel oil releases of private fuel oil tanks during the “century flood” 2002 in Germany. By order of IWO (Institut für wirtschaftliche Oelheizung e.?V.), the authors investigated the environmental behaviour of fuel oil after flood incidents. Aim Due to the fast spreading of the fuel oil on water surfaces and the contamination of huge areas one expects large environmental harm. For appraisal the behaviour of fuel oil in water and soil must be studied in detail as well as the effect on high and low developed animals and plants, on water organisms and on the flora and fauna of soil. From the valuation of the environmental harm official measures and measures of precaution and safety by manufacturer and user of private fuel oil installations can be derived. Main features For considering the various aspects the authors studied the extensive analyses of the special measuring programme of Saxony-Anhalt, used interviews of concerned persons (private persons and officials), aerial photos, extensive study of literature including eco-toxicological investigations, experiences of more than 70-years applications of fuel oil in plant protection and practical experiences at large field redevelopment of oil damages following averages and accidents. The authors valuated on the base of results of analyses and on own calculations. Results The release of fuel oil in the air is no particular problem because about 40?% of the oil fast evaporate and will be decomposed to carbon dioxide and water. In addition to the evaporation a characteristic behaviour is fast spreading of the fuel oil on the water surface to very thin layers. For a typical coloured oil layer e.?g. one cubic meter of oil is spread on a water surface of about 3?km², this corresponds to 3?ml/m² surface and contaminates the soil after drying up with about 3?µg/kg soil some orders less than the natural content of hydrocarbons in soil. Because of the absorption capacity of soil and the microbial decomposition by everywhere existing hydrocarbons decomposing micro-organisms the oil infiltrates only a few centimetre and will be decomposed in a few months, so that ground water detriments not arise practically. By measurements a few months after fuel oil release in the flood 2002 oil components in the soil could not be detected. Discussion Acute injuries of micro-flora and -fauna in soil and water by fuel oil cannot be excluded from the first. Thus the limiting values of injuries for some water organisms are below 1?mg/l. According to the special measuring programme at the flood 2002 in Saxony-Anhalt however the measured values were mostly wide below of this limit. In detail the spreading and evaporation of fuel oil on water surfaces, the propagation and decomposition of fuel oil in soil will be described. A quantitative valuation of fuel oil distribution in a real flood incident will be given. Conclusions Particular measures of redevelopment of soil for fuel oil release after flood incidents are not necessary normally. Even at the redevelopment after transport damages or at devastated sites with essential higher oil contaminations of soil in comparison to fuel oil release after flood incidents high decomposition rates are obtained by normal soil improving measures supporting the natural micro-organisms in reducing the hydrocarbon concentration for 70–90?% after a few months. Perspectives With the described results a realistic valuation of the environmental harm of fuel oil release after flood incidents could be given. From this qualified measures can be derived for official decisions and precautionary and reliable activities at fuel oil installations of flood endangered areas.     

Terrestrische ökotoxikologische Testmethoden für die Tropen

Goal, Scope, and Background

Soil organisms play a crucial role in terrestrial ecosystems. Plant Protection Products (PPPs) are known to affect these organisms and might have negative impacts on soil functions influenced by these organisms. Little research has been done to day on the impact of PPPs on tropical ecosystems. Therefore, in this study it was investigated whether the effects of pesticides differ between tropical and temperate regions and whether data generated under temperate conditions can be used for the Environmental Risk Assessment (ERA) in tropical regions.

Methods

The effects of one fungicide (Carbendazim) and one insecticide (lambda-Cyhalothrin) on soil invertebrates (earthworms and arthropods) and functional parameters (organic matter (OM) breakdown, feeding rate) were evaluated in semi-field tests using Terrestrial Model Ecosystems (TMEs) and in field tests using litter-bags. The soil for the TMEs was extracted from the same site near Manaus (Amazonas, Brazil) where the field test was conducted (see Part 1, Römbke et al. 2005 〈DOI: http://dx.doi.org/10.1065/uswf2004.12.088.1〉). The soil was acid clay, typical for tropical regions. In the TMEs the standard test species as well as native tropical species were introduced. Several application scenarios, selected according to their relevance for practical conditions, were realized in TME-tests and field (duration: 150 and 365 days, respectively). Finally, an Environmental Risk Assessment (ERA) for the two chemicals was performed.

Results and Conclusions

The results from the TME-tests show that both test chemicals (depending on their concentration) had toxic effects on the tested organisms and organic matter breakdown, but not on the feeding rates. In the field organic matter breakdown was affected for some time too, but effects on single species were, with one exception (the native earthworm Andiorrhinus amazonicus) not observed; a result probably influenced by the small size of the test plots. Observed differences in OM breakdown between control and treated TMEs were often significant, while due to the higher variability even with differences >10% between means this was not the case in the field.

Recommendation and Perspective

According to the preliminary results of the Environmental Risk, Assessment presented here, the use of the three model chemicals in the tropics (e.g. in Brazil) can cause a damage to the environmental compartment soil. Therefore, a more detailed investigation of these PPPs is recommended, in particular a better evaluation of the exposure (residue analysis). In general, the work performed in Amazonia can be summarised as follows: (1) Depending on the properties of the PPP, the effects of pesticides in tropical resp, temperate regions can differ. (2) If a PPP is going to be used in the tropics, data from tests modified for these conditions should be performed and their results should be incorporated in an Environmental Risk Assessment (ERA) for tropical regions.