Comparing ecotoxicological and physicochemical indicators of municipal wastewater effluent and river water quality in a Baltic Sea catchment in Poland

While legal regulations require treated wastewater to be tested based only on its physicochemical parameters, surface water assessment also has to include biological indicators. However, neither approach provides a complete picture of water quality due to lack of ecotoxicological information. Theref...

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Bibliographic Details
Main Authors: Kiedrzyńska, E. (Author), Kiedrzyński, M. (Author), Mankiewicz-Boczek, J. (Author), Mitsch, W.J (Author), Szklarek, S. (Author), Zalewski, M. (Author)
Format: Article
Language:English
Published: Elsevier B.V. 2021
Subjects:
Online Access:View Fulltext in Publisher
LEADER 05158nam a2200781Ia 4500
001 10.1016-j.ecolind.2021.107611
008 220427s2021 CNT 000 0 und d
020 |a 1470160X (ISSN) 
245 1 0 |a Comparing ecotoxicological and physicochemical indicators of municipal wastewater effluent and river water quality in a Baltic Sea catchment in Poland 
260 0 |b Elsevier B.V.  |c 2021 
856 |z View Fulltext in Publisher  |u https://doi.org/10.1016/j.ecolind.2021.107611 
520 3 |a While legal regulations require treated wastewater to be tested based only on its physicochemical parameters, surface water assessment also has to include biological indicators. However, neither approach provides a complete picture of water quality due to lack of ecotoxicological information. Therefore, the aim of the study was to perform an ecotoxicological evaluation of treated wastewater and river water in the catchment scale using a battery of biotests. In the period between June 2017 and July 2018, six sets of treated wastewater samples were taken from 17 municipal wastewater treatment plants (WWTPs) of different sizes (small: < 2,000 people equivalent - p.e.; medium size: 2,000–9,999 p.e.; large: 15,000–99,999 p.e.), as well as river water samples from seven sites along the 342 km Pilica River in central Poland. Physical and chemical analysis were performed of total nitrogen (TN), total phosphorus (TP), biochemical oxygen demand (BOD), chemical oxygen demand (COD) and total suspended solids (TSS), as well as organic suspended matter (OSM), ion content (fluorides, nitrates, ammonium, potassium and sulphate), and pH, conductivity and redox potential (RP). Ecotoxicity assessment was performed using a battery of biotests comprising the producer Pseudokirchneriella subcapitata (chronic toxicity biotest), consumer Thamnocephalus platyurus (acute toxicity biotest) and decomposer Tetrahymena thermophila (chronic toxicity biotest). It was found that in small WWTPs, the recommended levels of TN, TP, BOD, COD and TSS were often exceeded. Also, the highest mean toxicity hazard in the ecotoxicological biotests was observed for samples from small WWTPs. No clear dependence was found between any of the studied physicochemical parameters of the water and the ecotoxicity of samples: however, a correlation was observed between growth inhibition of P. subcapitata and TN and NH4+ concentration (r = 0.43 and r = 0.48, respectively). Also, the mortality of T. platyurus was correlated with NH4+(r = 0.72), TN (r = 0.64), BOD (r = 0.52), TSS (r = 0.44) and OSM (r = 0.46). The most sensitive organism in the applied battery of biotests was the alga P. subcapitata (producer), with a 90% toxic response for WWTP samples and 100% for river samples. T. platyurus (consumer) demonstrated a 56% toxic response for WWTP samples and no toxicity (0%) for river samples. In turn, T. thermophila demonstrated a 25% toxic response for WWTP samples and 33% for river samples. The addition of an ecotoxicological evaluation (battery of biotests) to the physicochemical monitoring of treated wastewater and river water delivered new information about the biological impact on organisms related to their different sensitivity. Additionally, the small WWTPs turned out to be the highest source of hazard. © 2021 The Authors 
650 0 4 |a Atlantic Ocean 
650 0 4 |a Baltic Sea 
650 0 4 |a biochemical oxygen demand 
650 0 4 |a Biochemical oxygen demand 
650 0 4 |a Biotest 
650 0 4 |a Biotests 
650 0 4 |a catchment 
650 0 4 |a Catchments 
650 0 4 |a chemical analysis 
650 0 4 |a correlation 
650 0 4 |a Ecohydrology 
650 0 4 |a Eco-hydrology 
650 0 4 |a Ecotoxicological 
650 0 4 |a ecotoxicology 
650 0 4 |a Ecotoxicology 
650 0 4 |a Eco-toxicology 
650 0 4 |a effluent 
650 0 4 |a Effluents 
650 0 4 |a Hazard 
650 0 4 |a Hazards 
650 0 4 |a Laws and legislation 
650 0 4 |a Nitrates 
650 0 4 |a Oxygen 
650 0 4 |a Pilica River 
650 0 4 |a Pilica River catchment 
650 0 4 |a Pilicum river catchment 
650 0 4 |a Poland [Central Europe] 
650 0 4 |a Potassium compounds 
650 0 4 |a Redox reactions 
650 0 4 |a Rivers 
650 0 4 |a Runoff 
650 0 4 |a Selenastrum capricornutum 
650 0 4 |a Sewage pumping plants 
650 0 4 |a Sulfur compounds 
650 0 4 |a surface water 
650 0 4 |a Tetrahymena thermophila 
650 0 4 |a Thamnocephalus platyurus 
650 0 4 |a Total nitrogen 
650 0 4 |a Total suspended solids 
650 0 4 |a Toxic response 
650 0 4 |a Toxicity 
650 0 4 |a Treated wastewater 
650 0 4 |a Waste water treatment plants 
650 0 4 |a Wastewater treatment 
650 0 4 |a wastewater treatment plant 
650 0 4 |a Wastewater treatment plants 
650 0 4 |a water quality 
650 0 4 |a Water quality 
650 0 4 |a Water treatment plants 
700 1 |a Kiedrzyńska, E.  |e author 
700 1 |a Kiedrzyński, M.  |e author 
700 1 |a Mankiewicz-Boczek, J.  |e author 
700 1 |a Mitsch, W.J.  |e author 
700 1 |a Szklarek, S.  |e author 
700 1 |a Zalewski, M.  |e author 
773 |t Ecological Indicators