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Biomonitoring of pesticide pollution in the air

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Responsibility: TIEM integrated environmental monitoring

So far, there are only a few environmental-chemical studies that deal with the pesticide load in nature conservation areas caused by conventional farming methods. The first results of studies on the coexistence of conventional and organic farms in Brandenburg showed that, in addition to direct contamination by drift from conventionally cultivated neighboring fields, long-distance transport of pesticides also takes place.

This work package aims at a spatial representative assessment of air pollution loads within the 21 selected nature reserves as well as in the surrounding agricultural areas. The standardized technique of bark biomonitoring and effective multi-point data collection will be applied to monitor the aerial input of a broad range of pesticides (>500 PSM) and more than 55 elements, including PAHs, PCDDs, PCDFs, and dioxin-like PCBs This allows a fingerprinting of relevant pollution impacts by agriculture and other anthropogenic, industrial and natural pollution sources, e.g. N, P, and other nutrients indicating the intensity of agriculture and fertilization at the sites.

Bark biomonitoring is a standardized method to measure air pollution loads integrating over greater time spans in a comparable way. To integrate volatile as well as semi-volatile and non-volatile contaminants, yearly sub-samples will be taken at the end of each season and combined into one integrated sample. Besides direct and immediate effects, also indirect and time-delayed effects of pollution exposure to insect populations are to be regarded, too. The results of the bark biomonitoring on long-term pollution are valuable to integrate these aspects in the analysis and final assessment.

Results will provide data on the complexity of pollution loads at the sites in a comparable way, allowing an empirical data-based assessment of pollution impacts for the 21 nature reserves and the surrounding landscape and classification in the three exposure categories. Hereby the standardized method enables the assessment in relation to other sites in Germany in form of the statistical data distribution being defined in previous projects. Furthermore, data are valuable for further research such as the definition of representative pollution cocktails to be used in standardized laboratory toxicity tests.

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Spatially representative multi-point sampling plan for the bark biomonitoring of air pollution within the 21 locations (blue points) and outside in the surrounding agricultural landscape (red points) with a schematic transect for certain pesticide gradients from the field to the interior of the nature reserve (NSG).

The investigations will cover the 21 protected areas of the DINA project as well as their agricultural environment. Sampling will be done for a representative survey in the two test years 2019 and 2020.

The analysis of the bark samples will be performed in cooperation with accredited laboratories experienced with the matrix. The analyses are carried out using modern multi-analytics for more than 500 pesticide active ingredients in quality assured procedures. Pesticide active ingredients that are currently approved, including glyphosate and AMPA, as well as environmentally relevant existing substances such as DDT and lindane are analyzed. The latter is still frequently found in the environment as persistent environmental chemicals (POPs), although they have not been approved for a long time.

Furthermore, the samples are analyzed by multi-element analysis (ICP-MS) for more than 60 elements (heavy metals, macronutrients) to characterize and typify the spatial deposition at the respective site. By collecting data on all of these elements, various influences and origins of air constituents at the sites can be tracked and differentiated (e.g. nutrient inputs from intensive land cultivation, pollutant inputs from anthropogenic and natural sources such as industry, traffic, or geogenic sources) and thus hypotheses on territorial influences can be empirically tested and validated.

As a result, the effects of airborne substances can be qualitatively and quantitatively represented and characterized spatially and materially.

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Taking the bark samples, which are evaluated for the detection of pesticides and other pollutants.

Dr. Werner Kratz - Independent assistant

Maximilian Sprenger - Independent assistant

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