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Municipal wastewater contains nutrients valuable for a reuse in agriculture and can be the source of a multitude of chemicals used in private households and industry, too. As many of these chemicals are incompletely degraded during wastewater treatment, their residues remain partly in sewage sludge and partly in treated wastewater. Concerns are linked particularly to the so called micropollutants, i.e. anthropogenic organic substances such as personal care products, pharmaceuticals and biocides, for which scarce data on their degradability and environmental fate and particularly on their ecotoxicity are available. Thus, when reusing treated wastewater and sewage sludge for irrigation or as soil amendment for a sustainable land and water management, these wastewater-borne pollutants may enter soil, groundwater and surface water. The present work therefore aimed at assessing potential ecotoxic effects on aquatic and terrestrial organisms of reusing treated wastewater and sewage sludge. To this end, established as well as newly developed experimental approaches were used to investigate the problem on several levels. Individual wastewater-borne substances, samples from field study sites and samples from a soil column experiment simulating prolonged wastewater irrigation were examined.
At the start of the experimental work, the ecotoxicity of climbazole was characterised towards five aquatic and five terrestrial test organisms. Climbazole is an azole antimycotic agent applied in cosmetics and anti-dandruff shampoos and was recently detected in relatively high concentrations in treated wastewater and sewage sludge. In the present work climbazole was found to be particularly toxic towards plants such as water lentils with effective concentrations comparable to those of agricultural azole fungicides. Dwarfism, that is reduced shoot elongation observed in plants, pointed at a specific, phytohormone inhibiting mode of action of climbazole. Furthermore, the expected influence of the soil pH on the phytotoxicity of climbazole was experimentally confirmed.
Based on the findings for climbazole, two additional azole antimycotics, ketoconazole and fluconazole, and the regularly in sewage sludge detected biocide benzyldimethyldodecyl-ammonium chloride (BDDA) were investigated for their toxicity towards plants.
In aqueous medium, an increasing phytotoxicity from fluconazole to BDDA, ketoconazole and climbazole was observed, while in soil, phytotoxicity increased from BDDA to ketoconazole, climbazole and fluconazole. The relatively low terrestrial toxicity of BDDA and ketoconazole probably resulted from their strong binding to soil as well as their good biodegradability. To render the exposure scenario more realistic, sewage sludge was co-applied with the four test substances in a parallel test run. However, as no detectable influence on their effective concentrations was found, it can be assumed that the current practice of assessing sewage sludge borne substances with biotests in standard soil is sufficiently realistic. In a further study, different advanced sludge-treatment technologies were assessed for their efficacy in reducing pollutants. Results from the present work indicated that effects assessed in terrestrial short term biotests only seldom correlated with the concentrations of certain pollutants. Rather, a negative correlation of the stability of the sludges, determined by the ratio of volatile to total solids, to their ecotoxicity was seen.
Another aspect of the present work was the design and performance of an experimental approach to assess the environmental risk of a long-term irrigation with treated wastewater concerning the quality of soil and water in a prospective way, i.e. before the installation at field scale. For the simulation of a continuous irrigation corresponding to approximately 30 years, a percolation apparatus was developed and four different soils were percolated with treated wastewater for three months. Acute and chronic biotests with nine test organisms from different trophic levels (green algae, water lentils and water fleas as well as oilseed rape, oats, bacteria, spring tails, enchytraeids and earthworms) were used to assess the soil percolates as well as the soils with and without percolation. These investigations were accompanied by a comprehensive chemical monitoring conducted by project partners. Results indicated that the soil passage, that is the percolation through the soil, generally improved the quality of the treated wastewater as habitat for aquatic organisms which was visible by a reduction of its phytotoxicity. However, in some cases it deteriorated the water quality, probably resulting from the leaching of metals from pre-contaminated soil. A deteriorated habitat quality of the soil after the percolation with treated wastewater was observed for several test organisms and soils. In the same, mainly peaty soils, the highest accumulation of wastewater-borne micropollutants and of zinc was measured. Yet, their concentrations did not correlate to the observed biological effects. Moreover, data on ecotoxicity were only available for a small fraction of the detected substances so that their concentrations could not successfully be used to predict expected biological effects.
The experimental approach used in the present work demonstrated to be an adequate tool to support the prospective evaluation of environmental risks of treated wastewater irrigation. Overall, it can be concluded that the reuse of treated wastewater on soil can improve the quality of treated wastewater but that this can come at the cost of deteriorating the quality of the soil. As these risks cannot be generalised, a comprehensive biotest battery as well as chemical analysis should be used to assess them on a case-specific basis for each respective wastewater and the respective soil.
To date, chemicals are used ubiquitous in everyday life and an increasing consumption of pharmaceuticals and personal care products and industrial chemicals results in an increased water pollution. Conventional wastewater treatment plants are not able to completely remove the variety of (polar) organic compounds from today’s wastewater and thus serve as constant key point sources for the unintentional release of (micro-)pollutants into the aquatic environment. Anthropogenic micropollutants are detectable in very low concentrations in almost every aquatic compartment and may cause adverse effects on aquatic organisms. Considering the current situation of water pollution and to enhance water quality with regard to environmental and human health, the implementation of advanced wastewater treatment technologies, such as ozonation and activated carbon filtration was extensively discussed and investigated in recent years. Yet, besides their advantages regarding the efficient removal of a variety of recalcitrant, organic compounds as well as pathogens from the wastewater, it is known that especially the treatment with ozone may lead to the formation of largely unknown ozonation by-products with often unknown toxicity and unknown threats to human and the environment. To address these topics the joint research project TransRisk aimed at the “characterization, communication and minimization of risks originating from emerging contaminants and pathogens in the water cycle”. Within this research project the present thesis focuses on the ecotoxicological investigation of emerging waterborne contaminants, including their potential transformation products (TPs). Additionally, focus was laid on the investigation of combined effects of anthropogenic contaminants and pathogens with effects especially on aquatic invertebrate organisms.
The potential ecotoxicological effects of the antiviral drug acyclovir and two of its structurally identified TPs, were investigated on three aquatic organisms (Raphidocelis subcapitata, Daphnia magna and embryos of Danio rerio). While the parent compound acyclovir caused no acute toxicity up to a tested concentration of 100 mg/l on any of the investigated organisms, both TPs were shown to exhibit an increased aquatic toxicity. Carboxy-acyclovir, the biodegradation product of acyclovir, significantly reduced reproduction of D. magna by 40% at 102 mg/l, and the ozonation product COFA significantly inhibited growth of green algae R. subcapitata (EC10 = 14.1 mg/l). In the present case, advanced wastewater treatment was shown to lead to the formation of TPs, that reveal a higher toxicity towards investigated organisms, than the parent compound. Results highlight the necessity of further research related to the topic of identification and characterization of TPs, formed during advanced wastewater treatment processes.
To investigate the potential reduction or enhancement of toxic effects of nine differently treated wastewater effluents, selected bioassays with Daphnia magna, Lumbriculus variegatus and Lemna minor were conducted in flow-through test systems on a pilot treatment plant. The different treatment processes included ozonation of conventional biological treatment, with subsequent filtration processes as well as membrane bioreactor treatment in combination with ozonation. While exposure to the conventionally treated wastewater did not result in significant impairing effects on D. magna and L. minor, a reduced abundance of L. variegatus (by up to 46%) was observed compared to the medium control. Subsequent ozonation and additional filtration of the wastewater enhanced water quality, visible in an improved performance of L. variegatus. In general, direct evidence for the formation of toxic TPs due to the advanced wastewater treatments was not found, at least not in concentrations high enough to cause measurable effects in the investigated test systems. Additionally, no evidence for immunotoxic effects of the investigated wastewater effluents were observed. Yet, study-site- and species-specific effects hindered the definite interpretation of results. That underline the importance of a suitable test battery consisting of representatives of different taxonomic groups and trophic levels, to ensure a comprehensive evaluation of the complex matrix of wastewater and to avoid false-negative or false-positive results.
With aim to improve knowledge regarding immunotoxicity in invertebrates, the potential immunotoxic effects of the immunosuppressive pharmaceutical cyclosporine A (CsA) were investigated by applying the host-parasite model system Daphnia magna – Pasteuria ramosa in an adapted host resistance assay. Co-exposure to CsA and Pasteuria synergistically affected long-term survival of D. magna. Additionally, the enhanced virulence of the pathogen upon chemical co-exposure was expressed in synergistically increased infection rates and an increased speed of Pasteuria-induced host sterilization. In conclusion, results provide evidence for a suppressed disease resistance in a chemically stressed invertebrate host, highlighting the importance of investigating the conjunction of environmental pollutants and pathogens in the environmental risk assessment of anthropogenic pollutants.