Ecotoxicity of raw and treated effluents generated by a veterinary medicine industry

Effluents from veterinary pharmaceutical industries that formulate medicines are mainly generated during the washing of equipment. The aim of this work was to evaluate the acute toxicity to Daphnia similis and chronic toxicity to Ceriodaphnia dubia of raw and treated effluents generated by a veterinary pharmaceutical industry. The industrial effluent treatment system comprises a step of chemical treatment (coagulation-sedimentation forced) followed by aerobic biological treatment (activated sludge process). Five samplings campaigns were performed from October 2011 to July 2012. The raw effluent samples showed high acute and chronic toxicity (acute: fourth sampling with EC50 - 48-h of <0.001% and chronic: third sampling with IC50 - 7-d of <0.0001%). The chemically treated effluent samples were the most toxic with EC50 - 48-h between <0.001 and 0.1% and IC50 - 7-d between 0.00001 and 0.0001%. This increase in toxicity is probably related to the use of aluminum sulfate as flocculating agent. The biological treatment led to a small reduction in toxicity of the effluents. The selected ecotoxicological tests were adequate for detecting the effluent toxicity and useful for evaluating the efficiency of the steps of the effluent treatment. Improvements in the industrial wastewater treatment system should be implemented in order to reduce the observed toxicity of the final effluent.Efluentes de indústrias farmacêuticas veterinárias, que formulam medicamentos, são gerados principalmente durante a lavagem dos equipamentos. O objetivo desse trabalho foi avaliar a toxicidade aguda para Daphnia similis e crônica para Ceriodaphnia dubia, dos efluentes brutos e tratados gerados por uma indústria farmacêutica veterinária. O sistema de tratamento de efluentes usado é composto por uma etapa de tratamento químico (coagulação-sedimentação forçada) seguida do tratamento biológico aeróbio (processo de lodos ativados). Foram realizadas 5 campanhas de amostragens entre outubro de 2011 e julho de 2012. As amostras de efluentes brutos apresentaram elevada toxicidade aguda e crônica (aguda: quarta campanha com CE50 - 48-h de <0,001% e crônica: terceira campanha com CI50 - 7d <0,0001%). As amostras de efluentes tratados quimicamente foram as mais tóxicas com CE50 - 48-h entre <0,001 e 0,1% e CI50 - 7-d entre 0,00001 e 0,0001%, provavelmente relacionada ao uso de sulfato de alumínio como agente floculante. O tratamento biológico levou a uma pequena diminuição da toxicidade dos efluentes. Os testes ecotoxicológicos foram adequados para detectar a toxicidade dos efluentes e úteis para avaliar a eficiência das etapas do tratamento. Melhorias no sistema de tratamento de efluentes da indústria estudada deveriam ser implementadas visando à redução da toxicidade observada nos efluentes finais.Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq)Fundação de Amparo à Pesquisa do Estado de Minas Gerais (FAPEMIG)Universidade Federal de Alfenas Instituto de Ciências da NaturezaUniversidade Estadual de Campinas Laboratório de Ecotoxicologia Aquática e Limnologia Prof. Dr. Abílio LopesUniversidade Federal de São Paulo (UNIFESP) Instituto de Ciências Ambientais, Químicas e FarmacêuticasUNIFESP, Instituto de Ciências Ambientais, Químicas e FarmacêuticasSciEL

Caminhos percorridos no mapa da portuguesificação: A Linguateca em perspectiva

This study evaluated the ecotoxicity of five dyes to freshwater organisms before and during their photo-Fenton degradation. EC50 (48 h) of the five tested dyes ranged from of 6.9 to >1000 mg L-1 for Daphnia similis. In the chronic tests IC50 (72 h) varied from 65 to >100 mg L-1 for Pseudokirchneriella subcapitata and IC50 (8 days) from 0.5 to 410 mg L-1 for Ceriodaphnia dubia. Toxicity tests revealed that although the applied treatment was effective for decolorization of the dye, the partial mineralization may be responsible for the presence of degradation products which can be either more toxic than the original dye, as is the case of Vat Green 3 and Reactive Black 5, lead to initially toxic products which may be further degraded to non toxic products (acid Orange 7 and Food Red 17), or generate non toxic products as in the case of Food Yellow 3. The results highlighted the importance of assessing both acute and chronic toxicity tests of treated sample before effluent discharge. (C) 2014 Elsevier B.V. All rights reserved.Fundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP

Obituary for Tamara Grummt

Tamara Grummt passed away on January 26, 2020 in Oelsnitz/Vogtland, Germany. Tamara was one of the scientific pioneers in the field of environmental toxicology, namely genotoxicity and hygiene of drinking and bathing waters. Her passing is not only a great loss to environmental research and to the global environmental toxicology community—we have lost an outstanding personality with the heart in the right place, who has become, for many of us, a wonderful friend

Ecotoxicity of raw and treated effluents generated by a veterinary medicine industry

Effluents from veterinary pharmaceutical industries that formulate medicines are mainly generated during the washing of equipment. The aim of this work was to evaluate the acute toxicity to Daphnia similis and chronic toxicity to Ceriodaphnia dubia of raw and treated effluents generated by a veterinary pharmaceutical industry. The industrial effluent treatment system comprises a step of chemical treatment (coagulation-sedimentation forced) followed by aerobic biological treatment (activated sludge process). Five samplings campaigns were performed from October 2011 to July 2012. The raw effluent samples showed high acute and chronic toxicity (acute: fourth sampling with EC50 - 48-h of <0.001% and chronic: third sampling with IC50 - 7-d of <0.0001%). The chemically treated effluent samples were the most toxic with EC50 - 48-h between <0.001 and 0.1% and IC50 - 7-d between 0.00001 and 0.0001%. This increase in toxicity is probably related to the use of aluminum sulfate as flocculating agent. The biological treatment led to a small reduction in toxicity of the effluents. The selected ecotoxicological tests were adequate for detecting the effluent toxicity and useful for evaluating the efficiency of the steps of the effluent treatment. Improvements in the industrial wastewater treatment system should be implemented in order to reduce the observed toxicity of the final effluent.Efluentes de indústrias farmacêuticas veterinárias, que formulam medicamentos, são gerados principalmente durante a lavagem dos equipamentos. O objetivo desse trabalho foi avaliar a toxicidade aguda para Daphnia similis e crônica para Ceriodaphnia dubia, dos efluentes brutos e tratados gerados por uma indústria farmacêutica veterinária. O sistema de tratamento de efluentes usado é composto por uma etapa de tratamento químico (coagulação-sedimentação forçada) seguida do tratamento biológico aeróbio (processo de lodos ativados). Foram realizadas 5 campanhas de amostragens entre outubro de 2011 e julho de 2012. As amostras de efluentes brutos apresentaram elevada toxicidade aguda e crônica (aguda: quarta campanha com CE50 - 48-h de <0,001% e crônica: terceira campanha com CI50 - 7d <0,0001%). As amostras de efluentes tratados quimicamente foram as mais tóxicas com CE50 - 48-h entre <0,001 e 0,1% e CI50 - 7-d entre 0,00001 e 0,0001%, provavelmente relacionada ao uso de sulfato de alumínio como agente floculante. O tratamento biológico levou a uma pequena diminuição da toxicidade dos efluentes. Os testes ecotoxicológicos foram adequados para detectar a toxicidade dos efluentes e úteis para avaliar a eficiência das etapas do tratamento. Melhorias no sistema de tratamento de efluentes da indústria estudada deveriam ser implementadas visando à redução da toxicidade observada nos efluentes finais.168179Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq

Ten years-snapshot of the occurrence of emerging contaminants in drinking, surface and ground waters and wastewaters from São Paulo state, Brazil

Emerging contaminants have been considered one of the main concerns for ensuring the quality of water around the world. This work presents the results of 10 years of analyses carried out in the state of São Paulo (Brazil) that has the high population density and intense agricultural and industrial activities. In this work 58 compounds (9 hormones, 14 pharmaceuticals and personal care products, 8 industrial compounds, 17 pesticides and 10 illicit drugs) were determined from 2006 to 2015 in 708 samples including raw and treated sewage, surface and ground and drinking waters. A preliminary risk assessment for aquatic life protection identified potential risks for caffeine, paracetamol, diclofenac, 17α-ethynylestradiol, 17β-estradiol, estriol, estrone, testosterone, triclosan, 4-n-nonylphenol, bisphenol A, atrazine, azoxystrobin, carbendazim, fipronil, imidacloprid, malathion and tebuconazole. Drinking water criteria were available only for 22 compounds and for them no adverse effects were expected at the concentrations found, except for 17β-estradiol

Interlab study on nanotoxicology of representative graphene oxide

The graphene sample GO: Single-layer graphene oxide, purity 99%, thickness 0.7-1.2 nm (AFM); similar to 300-800nm X&Y dimensions is the standard size 50 mu g/mL) were observed. Genotoxic study using the Comet assay showed slight DNA damage in lymphocytes at all concentrations tested, while more significant effects was observed in CHO cells. Econanotoxicity was carried out by lethality assays in the nematode Caenorhabditis elegans, d in the freshwater coelenterate Hydra, Daphania amd in Shrimp with no signs of toxicity at concentrations varying from 0.1-100 mu g/mL of GO. However, death and disintegration of Hydra was observed after exposition to 100 mu g/mL for 72 h. In in vivo studies, no changes in biochemical parameters of Fischer 344 rats were observed after the i. p. administration of GO. Some black agglomerates were found in the intraperitoneal cavity of rats injected with GO. However, in Fisher 344 rats-bearing prostate tumors, treatment with GO (up to 100 mu g/mL) negatively affected the hepatic parameters, whilst in the renal ones, an improvement was observed. Studies are in progress to understand the mechanisms involved in the uptake of GO by RES. GO appears as a potential non-toxic in vitro and in vivo assays at the concentrations used in this interlab experiments.The graphene sample GO:Single-layer graphene oxide, purity 99%, thickness 0.7-1.2 nm (AFM); ~300-800nm X&Y dimensions is the standard size <450 nm & 1-20 μm lateral dimensions. Cheap Tubes Inc., Bratleboro, USA was selected for our study. Exhaustive chara617CNPQ - CONSELHO NACIONAL DE DESENVOLVIMENTO CIENTÍFICO E TECNOLÓGICOFAPESP - FUNDAÇÃO DE AMPARO À PESQUISA DO ESTADO DE SÃO PAULOsem informaçãosem informação4th International Conference on Safe Production and Use of NanomaterialsSupport from the Brazilian Network of Nanotoxicology (CIGENANOTOX) (MCTI/CNPq), INOMAT (MCTI/CNPq), NanoBioss (MCTI) and FAPESP are acknowledged

The Salmonella Mutagenicity Assay: The Stethoscope of Genetic Toxicology for the 21st Century

Objectives: According to the 2007 National Research Council report Toxicology for the Twenty-First Century, modern methods (e.g., "omics," in vitro assays, high-throughput testing, computational methods) will lead to the emergence of a new approach to toxicology. The Salmonella mammalian microsome mutagenicity assay has been central to the field of genetic toxicology since the 1970s. Here we document the paradigm shifts engendered by the assay, the validation and applications of the assay, and how the assay is a model for future in vitro toxicology assays. Data sources: We searched PubMed, Scopus, and Web of Knowledge using key words relevant to the Salmonella assay and additional genotoxicity assays. Data extraction: We merged the citations, removing duplicates, and categorized the papers by year and topic. Data synthesis: The Salmonella assay led to two paradigm shifts: that some carcinogens were mutagens and that some environmental samples (e.g., air, water, soil, food, combustion emissions) were mutagenic. Although there are > 10,000 publications on the Salmonella assay, covering tens of thousands of agents, data on even more agents probably exist in unpublished form, largely as proprietary studies by industry. The Salmonella assay is a model for the development of 21st century in vitro toxicology assays in terms of the establishment of standard procedures, ability to test various agents, transferability across laboratories, validation and testing, and structure-activity analysis. Conclusions: Similar to a stethoscope as a first-line, inexpensive tool in medicine, the Salmonella assay can serve a similar, indispensable role in the foreseeable future of 21st century toxicology

Relatório de estágio profissional

O presente Relatório foi realizado no âmbito do Estágio Profissional I e II. Trata-se de um trabalho elaborado com base na observação de aulas e na experimentação didática; os materiais obtidos (como, por exemplo, horários, dados sobre as turmas, fichas, etc.) foram submetidos a uma análise documental

Mixture effects in samples of multiple contaminants – An inter-laboratory study with manifold bioassays

© 2018 Chemicals in the environment occur in mixtures rather than as individual entities. Environmental quality monitoring thus faces the challenge to comprehensively assess a multitude of contaminants and potential adverse effects. Effect-based methods have been suggested as complements to chemical analytical characterisation of complex pollution patterns. The regularly observed discrepancy between chemical and biological assessments of adverse effects due to contaminants in the field may be either due to unidentified contaminants or result from interactions of compounds in mixtures. Here, we present an interlaboratory study where individual compounds and their mixtures were investigated by extensive concentration-effect analysis using 19 different bioassays. The assay panel consisted of 5 whole organism assays measuring apical effects and 14 cell- and organism-based bioassays with more specific effect observations. Twelve organic water pollutants of diverse structure and unique known modes of action were studied individually and as mixtures mirroring exposure scenarios in freshwaters. We compared the observed mixture effects against component-based mixture effect predictions derived from additivity expectations (assumption of non-interaction). Most of the assays detected the mixture response of the active components as predicted even against a background of other inactive contaminants. When none of the mixture components showed any activity by themselves then the mixture also was without effects. The mixture effects observed using apical endpoints fell in the middle of a prediction window defined by the additivity predictions for concentration addition and independent action, reflecting well the diversity of the anticipated modes of action. In one case, an unexpectedly reduced solubility of one of the mixture components led to mixture responses that fell short of the predictions of both additivity mixture models. The majority of the specific cell- and organism-based endpoints produced mixture responses in agreement with the additivity expectation of concentration addition. Exceptionally, expected (additive) mixture response did not occur due to masking effects such as general toxicity from other compounds. Generally, deviations from an additivity expectation could be explained due to experimental factors, specific limitations of the effect endpoint or masking side effects such as cytotoxicity in in vitro assays. The majority of bioassays were able to quantitatively detect the predicted non-interactive, additive combined effect of the specifically bioactive compounds against a background of complex mixture of other chemicals in the sample. This supports the use of a combination of chemical and bioanalytical monitoring tools for the identification of chemicals that drive a specific mixture effect. Furthermore, we demonstrated that a panel of bioassays can provide a diverse profile of effect responses to a complex contaminated sample. This could be extended towards representing mixture adverse outcome pathways. Our findings support the ongoing development of bioanalytical tools for (i) compiling comprehensive effect-based batteries for water quality assessment, (ii) designing tailored surveillance methods to safeguard specific water uses, and (iii) devising strategies for effect-based diagnosis of complex contamination