Martyna Kasela, Mateusz Ossowski, Łukasz Wlazło, Sylwia Andrzejczuk, Marcin Widomski, Aneta Michalska-Warias, Anna Musz-Pomorska, Paweł Suchorab, Katarzyna Karpińska, Anna Malm, Bożena Nowakowicz-Dębek
{"title":"Management of milking wastewater as a significant control point of microbial pollution in the environment.","authors":"Martyna Kasela, Mateusz Ossowski, Łukasz Wlazło, Sylwia Andrzejczuk, Marcin Widomski, Aneta Michalska-Warias, Anna Musz-Pomorska, Paweł Suchorab, Katarzyna Karpińska, Anna Malm, Bożena Nowakowicz-Dębek","doi":"10.26444/aaem/208761","DOIUrl":null,"url":null,"abstract":"<p><strong>Introduction and objective: </strong>Milking wastewater (MW) is an under-recognised reservoir of antibiotic resistant bacteria (ARB) and antimicrobial resistance genes (ARGs). The aim of the study is to evaluate MW as a point source pollutant for the presence of ARB and ARGs, to develop a treatment plant, and to address current legislation.</p><p><strong>Material and methods: </strong>Milking wastewater was analysed for the total number of bacteria, <i>Enterococcus</i> spp., <i>Staphylococcus</i> spp., Enterobacterales, and <i>Clostridium perfringens</i>. Microbial identification by MALDI-TOF MS was followed by antimicrobial susceptibility testing and detection of ARGs. Wastewater samples were also tested for the antimicrobials presence using immunochromatographic tests. An on-site two-chamber MW treatment plant was designed with consideration of its cost-effectiveness and profitability. The system incorporated filtration through a mixture of fine sand and 10% kaolin, or a fine sand filter bed, yielding hydraulic conductivity coefficients of 5.13 × 10-6 m/s and 5.36 × 10-5 m/s, respectively. The treated effluent was considered suitable for activities not requiring tap water quality.</p><p><strong>Results: </strong><i>Escherichia coli</i> and <i>Enterococcus</i> spp. were identified as ARB. PCR confirmed the presence of ARGs conferring resistance to β-lactams (<i>cphA, bla<sub>GES1-9,11</sub>, bla<sub>TEM1,2</sub></i>) and chloramphenicol (<i>cfr</i>). Milkling wastewater samples also tested positive for chloramphenicol.</p><p><strong>Conclusions: </strong>To mitigate environmental contamination, regulations should be established for the release of bioactive substances, with penalties imposed for non-compliance with recommended safety measures.</p>","PeriodicalId":520557,"journal":{"name":"Annals of agricultural and environmental medicine : AAEM","volume":"33 2","pages":"167-177"},"PeriodicalIF":1.2000,"publicationDate":"2026-06-24","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Annals of agricultural and environmental medicine : AAEM","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.26444/aaem/208761","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"2025/8/25 0:00:00","PubModel":"Epub","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 0
Abstract
Introduction and objective: Milking wastewater (MW) is an under-recognised reservoir of antibiotic resistant bacteria (ARB) and antimicrobial resistance genes (ARGs). The aim of the study is to evaluate MW as a point source pollutant for the presence of ARB and ARGs, to develop a treatment plant, and to address current legislation.
Material and methods: Milking wastewater was analysed for the total number of bacteria, Enterococcus spp., Staphylococcus spp., Enterobacterales, and Clostridium perfringens. Microbial identification by MALDI-TOF MS was followed by antimicrobial susceptibility testing and detection of ARGs. Wastewater samples were also tested for the antimicrobials presence using immunochromatographic tests. An on-site two-chamber MW treatment plant was designed with consideration of its cost-effectiveness and profitability. The system incorporated filtration through a mixture of fine sand and 10% kaolin, or a fine sand filter bed, yielding hydraulic conductivity coefficients of 5.13 × 10-6 m/s and 5.36 × 10-5 m/s, respectively. The treated effluent was considered suitable for activities not requiring tap water quality.
Results: Escherichia coli and Enterococcus spp. were identified as ARB. PCR confirmed the presence of ARGs conferring resistance to β-lactams (cphA, blaGES1-9,11, blaTEM1,2) and chloramphenicol (cfr). Milkling wastewater samples also tested positive for chloramphenicol.
Conclusions: To mitigate environmental contamination, regulations should be established for the release of bioactive substances, with penalties imposed for non-compliance with recommended safety measures.