In the last decades, there has been a growing interest in studying particular those arthropods who have an important role in agroecosystems. For example, they are natural enemies of pests and therefore they are considered to be beneficial organisms. However, these beneficial arthropods may be negatively affected by the application of chemicals under the management of agroecosystems and their potential to inhibit pests can be significantly reduced. Such organisms certainly include spiders which occure in abundant numbers practically in all types of terrestrial habitats including agricultural ecosystems where they have a role of very important predators. Therefore, the thesis focused on current issues of pesticides, especially from the view of their negative effects on behavioral modification of beneficial invertebrate organisms in agricultural crops. The theoretical part is devoted to a brief characteristics of pesticides, their sublethal effects on non-target organisms and the importance of spiders as natural regulators of pests in agroecosystems. The practical part describes the experiment whereconventionally used agrochemicals were tested the influence of the herbicide and desiccant Basta 15, the Arrest preparation and their combination (mixture Basta 15 + Arrest) on spiders genus Pardosa. I focused on the side effects of these solutions, specifically on the modification of predatory behavior and on the mortality of spiders. It has been shown that agrochemicals affect the predation successfulness of spiders. From the short term and the long term point of view, it has been shown that spiders treated with the tested preparations killed less prey than the individuals in the control group which were treated only with distilled water. The dependence of mortality and the number of killed prey on the size and sex has not been proved. Preparations Basta 15 and the mixture caused significantly higher mortality of spiders. The Arrest preparation did not increase the mortality.

No description available.

This research deals with impacts of pesticide substances on spider populations. In this case pesticides of the neonicotinoids classes were tested. Specific neonicotinoids were applied to different of spiders which were collected in various localities and at some stage of development - nymph, adult or subadult individuals. The diploma thesis analyzes and the documents the effects of neonicotinoids to spiders. The results show that some pesticides can have a significant negative effect to locomotion, predation, ballooning, drop or to spiders mortality. Keywords: spider, arthropod, pesticides, insecticides, neonicotinoids, sublethal effects, mortality, EthoVision XT, locomotion, drop, ballooning, predation, Philodromus, Oedothorax, Pardosa, Xerolycosa, Phylloneta

Os protocolos de Avaliação de Risco Ambiental (ERA) de Fármacos e Produtos de Cuidados Pessoais (FPCP) recomendam o uso de ensaios ecotoxicológicos tradicionais (por exemplo algas, bactérias, invertebrados, peixes) e a avaliação de efeitos em um único nível de organização biológica para a determinação dos efeitos potenciais dos FPCP à biota. Considerando que efeitos em nível de sub-indivíduo pode afetar igualmente a aptidão ecológica de organismos marinhos, e que os mesmos estão cronicamente expostos aos FPCP, o objetivo do presente estudo foi avaliar o risco ambiental de triclosan (TCS), ibuprofeno (IBU) e 17&alpha;-etinilestradiol (EE2) em sedimentos marinhos utilizando respostas de efeitos sub-individuais e populacionais. Por meio do HPLC-ESI-MS/MS, as concentrações ambientais de TCS e IBU foram quantificadas em sedimentos marinhos coletados no entorno do emissário submarino de esgoto de Santos (Baía de Santos, São Paulo - Brasil) com 15,14 e 49,0 ng.g-1, respectivamente, enquanto o EE2 não foi detectado (<33 ng.g-1). Uma bateria de ensaios de toxicidade crônica (desenvolvimento embriolarval) com ouriços-do-mar (Lytechinus variegatus) e bivalves (Perna perna) foi realizada (efeito a nível de indivíduo) após exposição a sedimentos contaminados com os FPCP. Além disso, foram analisados alguns biomarcadores de Fase I (etoxiresorufina O-deetilase EROD e dibenzilfluoresceína DBF), de Fase II (glutationa S-transferase GST) do metabolismo, do sistema antioxidante (glutationa peroxidase GPx), de neurotoxicidade (colinesterase ChE), de estresse oxidativo (peroxidação lipídica LPO e danos em DNA) e de citotoxicidade que foram selecionados para avaliação das respostas a nível de sub-indivíduo em mexilhões Mytella charruana. Todos os compostos analisados apresentaram efeitos sobre o desenvolvimento embriolarval de L. variegatus e P. perna em concentrações ambientalmente relevantes. Em nível de sub-indivíuo foi possível observar que o TCS causou efeitos cito-genotóxicos (diminuição da estabilidade da membrana lisossomal, peroxidação lipídica e danos em DNA) e neurotóxicos. O IBU causou efeitos citotóxicos e neurotóxicos, enquanto o EE2 apresentou efeitos citotóxicos e danos em DNA. Nesse sentido, mesmo em baixas concentrações os FPCP são potencialmente capazes de alterar os mecanismos de manutenção da homeostase. Os dados químicos e ecotoxicológicos foram integrados e os quocientes de risco estimados para TCS, IBU e EE2 apresentaram valores superiores a 1,0, indicando alto risco ambiental destes compostos em sedimentos marinhos. Estes são os primeiros dados de avaliação de risco ambiental de FPCP em sedimentos de uma zona costeira brasileira. Os resultados sugerem que a ERA de fármacos e produtos de cuidados pessoais deve contemplar, além dos ensaios de toxicidade tradicionais o uso de biomarcadores como indicadores dos primeiros sinais de efeitos e, assim, estabelecer uma avaliação de risco mais efetiva que assegure a proteção e funcionamento dos ecossistemas aquáticos. / The guidelines for the Environmental Risk Assessment (ERA) of pharmaceuticals and personal care products (PPCPs) usually recommend the use of standard ecotoxicity assays (e.g. algae, bacteria, invertebrate, fish) and the assessment of endpoints at individual level for the evaluation of potential effects of PPCPs on biota. Considering that effects at sub-individual level can also affect the ecological fitness of marine organisms, and that marine organisms are chronically exposed to PPCPs, the aim of the current study was to evaluate the environmental risk of triclosan (TCS), ibuprofen (IBU) and 17&alpha;-ethynylestradiol (EE2) in marine sediments using sub-individual and population endpoints. Using LC-ESI-MS/MS, the environmental levels of TCS and IBU were quantified in marine sediments from the vicinities of the Santos submarine sewage outfall (Bay of Santos, São Paulo, Brazil) at 15.14 and 49.0 ng g-1, respectively, while EE2 was not detected (<33ng g-1). A battery (n=3) of chronic bioassays (embryo-larval development) with a sea urchin (Lytechinus variegatus) and a bivalve (Perna perna) were performed at populational level after exposure to spiked sediment. Phases I (ethoxyresorufin O-deethylase EROD and dibenzylfluorescein dealkylase DBF) and II (glutathione S-transferase GST) of the metabolism, antioxidant system (glutathione peroxidase GPX), neurotoxicity (cholinesterase ChE), oxidative effects (lipid peroxidation LPO and DNA damage strand breaks) and cytotoxicity were selected to evaluate the sublethal responses in the bivalve Mytella charruana. These compounds showed developmental effects on L. variegatus and P. perna at environmentally relevant concentrations. At sub-individual level TCS induced cyto-genotoxic (reduction on stability of lysosome membrane, lipid peroxidation and DNA damage) and neurotoxic effects. IBU caused cyto and neurotoxic effect, while EE2 caused cytotoxic and DNA damage. Chemical and ecotoxicological data were integrated and the quotient risk estimated for TCS, IBU and EE2 showed values higher than 1.0, indicating high environmental risks of these compounds in sediments. These are the first data of risk assessment of pharmaceuticals and personal care products in sediments of a Brazilian coastal zone. The results suggests that the ERA of pharmaceuticals and personal care products must include, in addition to the standard toxicity tests, the use of biomarkers as indicators of the early warning signs and thus provide a more effective risk assessment to security the protection and functioning of aquatic ecosystems.

No description available.

Brodifacoum is a highly effective anticoagulant rodenticide that presents a secondary hazard to some non-target wildlife. The high acute toxicity of brodifacoum to mammals and birds, and its prolonged persistence in liver predicates secondary risk to predators and scavengers of poisoned rodents. Hence there is a need to improve ability to monitor and predict hazards of brodifacoum to non-targets, and optimise use patterns accordingly. Use of a less persistent anticoagulant rodenticide, diphacinone, is an alternative approach currently under investigation in New Zealand. This thesis describes a series of laboratory and pen studies that address information gaps relevant to the assessment of non-target hazards in continued use of brodifacoum, and of using diphacinone as an alternative. Non-lethal techniques for determining sublethal brodifacoum exposure in birds was investigated in chickens. Elevation of prothrombin time was a less reliable index than residual concentrations in tissues. Samples requiring less invasive procedures, such as dried blood spots or faeces, have potential to detect recent sublethal brodifacoum exposure and refinement of these indices could be useful in proactive monitoring of avian wildlife. Residual brodifacoum in eggs of sublethally-exposed hens raised further questions regarding wider non-target hazard and adverse effects on development of fertile eggs or chicks. A laboratory trial with rats found a positive correlation between residual brodifacoum concentrations in liver and the amount of brodifacoum ingested as bait. An estimated 14-22% of ingested brodifacoum was excreted in rat faeces in the period between ingestion of a lethal dose and death, indicating another potentially significant environmental pathway for brodifacoum transfer. In considering diphacinone as a less persistent alternative rodenticide to brodifacoum, evaluation of residual concentrations and persistence in pig tissues was required to estimate secondary hazard to human consumers and adequate with-holding periods for hunting feral pigs in areas where diphacinone was applied. A pen trial showed that domestic pigs were more susceptible to diphacinone toxicity, and thus primary poisoning risk, than previously estimated. Hepatic half-life of diphacinone in pigs was approximately 14 days, indicating reduced persistence in comparison to brodifacoum and enabling estimates of with-holding periods for hunting feral pigs from areas where diphacinone baits were applied. To investigate potential hazards of diphacinone use to invertebrates a trial using tree weta, a native New Zealand invertebrate, was undertaken. Weta readily ate diphacinone wax block baits with no mortality or weight loss evident, indicating low susceptibility. Residual whole-body diphacinone concentrations did not increase with the amount of diphacinone bait eaten. A simple, deterministic risk assessment suggested that, as a single secondary exposure, the maximum diphacinone concentration measured in weta would present a low risk to non-target birds. Given international recognition of the high secondary hazard and corresponding restrictions on use of brodifacoum, continued availability of brodifacoum to non-licensed users and sustained field applications for possum and rodent control in New Zealand is an exceptional use pattern. New data in this thesis suggest that baiting strategies that minimise the amount of brodifacoum available in the environment are important and regulatory review of some New Zealand brodifacoum applications should address this. In parallel, development of diphacinone as an alternative to brodifacoum should continue, as new data here confirms lower persistence in mammalian liver than brodifacoum, and also indicates low toxicity to invertebrates. However further investigation of multiple-exposure hazard and potential sublethal effects of diphacinone on non-target mammals and birds is warranted before extensive and sustained field applications of diphacinone are undertaken.

Os protocolos de Avaliação de Risco Ambiental (ERA) de Fármacos e Produtos de Cuidados Pessoais (FPCP) recomendam o uso de ensaios ecotoxicológicos tradicionais (por exemplo algas, bactérias, invertebrados, peixes) e a avaliação de efeitos em um único nível de organização biológica para a determinação dos efeitos potenciais dos FPCP à biota. Considerando que efeitos em nível de sub-indivíduo pode afetar igualmente a aptidão ecológica de organismos marinhos, e que os mesmos estão cronicamente expostos aos FPCP, o objetivo do presente estudo foi avaliar o risco ambiental de triclosan (TCS), ibuprofeno (IBU) e 17&alpha;-etinilestradiol (EE2) em sedimentos marinhos utilizando respostas de efeitos sub-individuais e populacionais. Por meio do HPLC-ESI-MS/MS, as concentrações ambientais de TCS e IBU foram quantificadas em sedimentos marinhos coletados no entorno do emissário submarino de esgoto de Santos (Baía de Santos, São Paulo - Brasil) com 15,14 e 49,0 ng.g-1, respectivamente, enquanto o EE2 não foi detectado (<33 ng.g-1). Uma bateria de ensaios de toxicidade crônica (desenvolvimento embriolarval) com ouriços-do-mar (Lytechinus variegatus) e bivalves (Perna perna) foi realizada (efeito a nível de indivíduo) após exposição a sedimentos contaminados com os FPCP. Além disso, foram analisados alguns biomarcadores de Fase I (etoxiresorufina O-deetilase EROD e dibenzilfluoresceína DBF), de Fase II (glutationa S-transferase GST) do metabolismo, do sistema antioxidante (glutationa peroxidase GPx), de neurotoxicidade (colinesterase ChE), de estresse oxidativo (peroxidação lipídica LPO e danos em DNA) e de citotoxicidade que foram selecionados para avaliação das respostas a nível de sub-indivíduo em mexilhões Mytella charruana. Todos os compostos analisados apresentaram efeitos sobre o desenvolvimento embriolarval de L. variegatus e P. perna em concentrações ambientalmente relevantes. Em nível de sub-indivíuo foi possível observar que o TCS causou efeitos cito-genotóxicos (diminuição da estabilidade da membrana lisossomal, peroxidação lipídica e danos em DNA) e neurotóxicos. O IBU causou efeitos citotóxicos e neurotóxicos, enquanto o EE2 apresentou efeitos citotóxicos e danos em DNA. Nesse sentido, mesmo em baixas concentrações os FPCP são potencialmente capazes de alterar os mecanismos de manutenção da homeostase. Os dados químicos e ecotoxicológicos foram integrados e os quocientes de risco estimados para TCS, IBU e EE2 apresentaram valores superiores a 1,0, indicando alto risco ambiental destes compostos em sedimentos marinhos. Estes são os primeiros dados de avaliação de risco ambiental de FPCP em sedimentos de uma zona costeira brasileira. Os resultados sugerem que a ERA de fármacos e produtos de cuidados pessoais deve contemplar, além dos ensaios de toxicidade tradicionais o uso de biomarcadores como indicadores dos primeiros sinais de efeitos e, assim, estabelecer uma avaliação de risco mais efetiva que assegure a proteção e funcionamento dos ecossistemas aquáticos. / The guidelines for the Environmental Risk Assessment (ERA) of pharmaceuticals and personal care products (PPCPs) usually recommend the use of standard ecotoxicity assays (e.g. algae, bacteria, invertebrate, fish) and the assessment of endpoints at individual level for the evaluation of potential effects of PPCPs on biota. Considering that effects at sub-individual level can also affect the ecological fitness of marine organisms, and that marine organisms are chronically exposed to PPCPs, the aim of the current study was to evaluate the environmental risk of triclosan (TCS), ibuprofen (IBU) and 17&alpha;-ethynylestradiol (EE2) in marine sediments using sub-individual and population endpoints. Using LC-ESI-MS/MS, the environmental levels of TCS and IBU were quantified in marine sediments from the vicinities of the Santos submarine sewage outfall (Bay of Santos, São Paulo, Brazil) at 15.14 and 49.0 ng g-1, respectively, while EE2 was not detected (<33ng g-1). A battery (n=3) of chronic bioassays (embryo-larval development) with a sea urchin (Lytechinus variegatus) and a bivalve (Perna perna) were performed at populational level after exposure to spiked sediment. Phases I (ethoxyresorufin O-deethylase EROD and dibenzylfluorescein dealkylase DBF) and II (glutathione S-transferase GST) of the metabolism, antioxidant system (glutathione peroxidase GPX), neurotoxicity (cholinesterase ChE), oxidative effects (lipid peroxidation LPO and DNA damage strand breaks) and cytotoxicity were selected to evaluate the sublethal responses in the bivalve Mytella charruana. These compounds showed developmental effects on L. variegatus and P. perna at environmentally relevant concentrations. At sub-individual level TCS induced cyto-genotoxic (reduction on stability of lysosome membrane, lipid peroxidation and DNA damage) and neurotoxic effects. IBU caused cyto and neurotoxic effect, while EE2 caused cytotoxic and DNA damage. Chemical and ecotoxicological data were integrated and the quotient risk estimated for TCS, IBU and EE2 showed values higher than 1.0, indicating high environmental risks of these compounds in sediments. These are the first data of risk assessment of pharmaceuticals and personal care products in sediments of a Brazilian coastal zone. The results suggests that the ERA of pharmaceuticals and personal care products must include, in addition to the standard toxicity tests, the use of biomarkers as indicators of the early warning signs and thus provide a more effective risk assessment to security the protection and functioning of aquatic ecosystems.