Pyrethroids are ones of the most used pesticides worldwides. The widespread use and high stability of pyrethroids lead to the assumption of that their occurrence in the environment could be quite frequent. They can reach water ecosystem as pollutants. Residues of pyrethroids are not only detected in the water column, but also in sediments and in fish tissues. The first study was devoted to the product Nexide containing 60 g.l-1 of active substance gamma-cyhalothrin. Tested Nexide concentrations were 5, 25, 50, 100, and 250 &microg.l-1. Early life stage test was used.Common carp (Cyprinus carpio) was tested. There were significant mortalities in all concentrations except the lowest concentration during the trial. The lowest concentration tested 5 &microg.l-1 only caused a slightly increased mortality. This lowest concentration influenced the growth in length and weight negatively, decelerated ontogenetic development, and made the body surface of the individuals darker. Histopathology of individuals from this concentration revealed dystrophy in liver. Examination of kidney, intestine and gills did not show significant histopathological differences compared with control. The evaluation of selected parameters of oxidative stress demonstrated a significantly higher activity of detoxification enzyme glutathione-S.transferase (GST) and a significantly lower activity of defensive enzyme glutathione peroxidase (GPx) compared with the control group. The other examined parameters of oxidative stress such as catalase (CAT), glutation reductase (GR), and lipid peroxidation determined by using the thiobarbituric acid-reactive substances (TBARs) were comparable to the control group. Changes in oxidative stress parameters suggest that exposure of the organism to the product Nexide in the given concentration leads to dysbalance of defensive enzymes. The second study was devoted to the product Cyperkill 25 EC containing 250 g.l-1. Tested Cyperkill 25 EC concentrations were 7.2, 36, 72, 144, and 360 &microg.l-1. The procedure of the trial was the same as the preceded one. There were 100% mortalities in all concentrations except the lowest concentration during the trial. The lowest tested concentration 7.2 &microg.l-1 allowed 90% of individuals to stay alive till the end of experiment. The lowest concentration influenced the growth in length and weight negatively and decelerated ontogenetic development compared with the control. Any individual exposed to this concentration did not reach juvenile stage until the end of the trial. Dark pigmentation was visible in 68% of these exposed individuals on the last day. Similar darkening was visible in individuals from higher concentrations shortly before death too. Histological examination did not revealed significant changes in intestine, liver, kidney, and gills compared with the control group. Evaluation of selected parameters of oxidative stress demonstrated significantly lower activities of GST, GR, and GPx. Activities of CAT and TBARS were comparable with the control group. Changes in oxidative stress parameters suggest that exposure of the organism to the product Cyperkill 25 EC in the given concentration could induce oxidative stress and interfere with the activities of antioxidant enzymes. The presented thesis summarises actual data about pyrethroids and their influence on fish. The demonstrated effects confirm high susceptibility of early developmental stages of fish to tested pesticides. When interpreting the results, we have to take into account the fact that studies showed this risk even on single pyrethroid substances. But water organisms are exposed to many other more or less toxic products and substances in a real environment. These xenobiotics could react with each other and their mixture could even potentiate negative effects. The performed studies also clearly show the significant differences in the sensitivity of embryonic and embryolarval tests.

Um método rápido utilizando cromatografia liquida (LC) foi desenvolvido para determinação simultânea de 7 pesticidas piretróides (bifentrina, cipermetrina, fenpropatrina, fenvalerato, permetrina, lambda-cialotrina, e deltametrina). Os resíduos são extraídos com acetona e a partição realizada de acordo com o método multi-resíduos DFG-S19, substituindo diclorometano por acetato de etila/ciclohexano (1+1) e purificação usando cromatografia de permeação a gel com uma coluna Biobeads SX3 e acetato de etila/ciclohexano (1+1) como eluente. A separação por LC é realizada com uma coluna LiChrospher 100 RP-18 e acetonitrila/água (8+2) como fase móvel. Os pesticidas são detectados em 212nm. As recuperações dos 7 pesticidas piretróides em amostras de feijão fortificadas em 0,010; 0,100; e 1,000 mg/kg ficaram entre 71-105%. A diferença particular deste método é o limite de quantificação, os quais ficaram entre 0,004-0,011 mg/kg, abaixo de muitos outros métodos de LC descritos na literatura. A cromatografia a gás (GC) com detector de captura de elétrons é mais sensível que a LC, mas o método com LC facilita a identificação dos picos. A GC apresenta muitos picos enquanto a LC apresenta apenas um para a maioria dos piretróides. A análise com LC é uma boa alternativa para a determinação de resíduos de piretróides em feijão. Durante o ano de 2005, um total de 48 amostras de feijão comercializadas na cidade de São Paulo, foram analisadas. Nenhum resíduo de pesticida piretróide foi detectado nas amostras. / A rapid liquid chromatographic (LC) method has been developed for simultaneous determination of 7 pyrethroid insecticides (bifenthrin, cypermethrin, fenpropathrin, fenvalerate, permethrin, lambda-cyhalothrin and deltamethrin) in beans. Residues are extracted from beans with acetone and the partition realized according to the multi-residue method DFG-S19, replacing dichloromethane by ethyl acetate/cyclohexane (1+1) and cleaned up using gel-permeation with a Biobeads SX3 column and ethyl acetate/cyclohexane (1+1) as eluant. LC separation is performed on a LiChrospher 100 RP-18 column with acetonitrile/water (8+2) as mobile phase. The pesticides are detected at 212 nm. Recoveries of 7 pyrethroid insecticides from beans fortified at 0.010; 0.100; 1.000 mg/kg levels were 71-105 %. The particular differential of this method is the quantification limits, which were between 0.004-0.011 mg/kg, lower than most of the limits reported for LC methods described in the literature. The gas chromatographic (GC) with electron capture detection is more sensitive than LC, but the LC method facilitates the identification of the peaks. Analysis of pyrethroids by GC shows several peaks, but LC shows only one for most pyrethroids. The analysis by LC was a good alternative for determination pyrethroid residues in beans. During 2005 year, a total of 48 bean samples commercialized in Sao Paulo City were analyzed. No residues of pyrethroids pesticides were detected in the samples.

Les pyréthrinoïdes et les organophosphorés sont des pesticides très utilisés, à l’origine d’une imprégnation forte de la population, exposée à ces contaminants principalement via l’alimentation. De plus en plus d’études scientifiques suggèrent des liens entre l’exposition à ces composés et des maladies chroniques ou des troubles du développement de l’enfant. Paradoxalement, leur devenir biologique chez l’homme est mal connu. Certaines études suggèrent que ces insecticides sont susceptibles d’intéragir avec les transporteurs membranaires ABC et SLC, protéines localisées au niveau d’interfaces hémato-tissulaires qui prennent en charge de nombreux substrats endogènes, médicaments et contaminants de l’environnement. L’objectif de notre étude a été de caractériser les effets d’insecticides des familles des pyréthrinoïdes et des organophosphorés sur l’activité de nombreux transporteurs ABC et SLC prenant en charge des médicaments (P-gp, BCRP, MRPs, OATP-1B1,-2B1,-1B3, OCT1-3, OAT1, OAT3, MATE1 et MATE2K) par une approche in vitro. Nous nous sommes également attachés à caractériser par des expérimentations in vitro et in silico, les mécanismes des interactions et les éléments structuraux des pesticides à l’origine de ces effets. Nous avons montré que de nombreux organophosphorés et pyréthrinoïdes étaient capables d’inhiber des transporteurs d’efflux (MRP, BCRP, P-gp) et d’influx (OATP1B1, OAT3, MATE1, OCT1-2) et de stimuler l’activité de certains OATPs. Les pesticides testés inhibaient très fortement l’activité des transporteurs de cations (OCT1 et OCT2) et ont pu bloquer le transport de catécholamines médiés par ces protéines. Une approche qSAR a permis de définir des paramètres physicochimiques associés aux effets modulateurs des pesticides et une approche d’amarrage moléculaire (docking) a mise en évidence les sites de liaisons de la P-gp impliquées dans ces interactions. Les conséquences des modulations de l’activité des transporteurs, en termes d’effets toxiques et d’interactions médicamenteuses, restent à définir pour les populations exposées à de fortes doses de pesticides. Toutefois, la contribution des interactions observées aux effets toxiques de ces insecticides est peu probable car nécessitant des concentrations nettement supérieures à celles atteintes dans le cadre d’une exposition environnementale de la population générale. / The general population is chronically exposed to pyrethroids and organophosphorus insecticides, mainly through alimentation. Several epidemiological studies have found an association between non-occupational exposure to these pesticides and chronic diseases and developmental disorders. Paradoxically, their biological fate in humans is poorly understood. Some studies suggest that these insecticides could interact with ABC and SLC membrane transporters. These membrane proteins, located at blood-tissue interfaces (liver, kidney, intestine ...), handle many endogenous substrates, drugs and pollutants. The objective of our study was to characterize, using an in vitro approach, the effects of pyrethroid and organophosphorus insecticides on the activity of numerous ABC and SLC human drug-transporters (P-gp, BCRP, MRPs, OATP-1B1, -2B1, -1B3, OCT1-3, OAT1, OAT3, MATE1 and MATE2K). We have also tried to analyze the mechanisms of interactions and the structural requirements for insecticides-mediated modulation of drug transporters activities using in vitro and in silico approach. We have shown that many organophosphorus and pyrethroids are able to inhibit ABC (MRP, BCRP, P-gp) and SLC (OATP1B1, OAT3, MATE1, OCT1-2) transporters and can stimulate the activity of some OATPs. Moreover, the tested pesticides inhibited very strongly the activity of OCT1 and OCT2 and blocked catecholamine transport mediated by these transporters. A qSAR approach allowed to define physicochemical parameters associated with the modulating effects of pesticides and a molecular docking approach revealed the P-gp binding sites involved in these interactions. The consequences of transporter activitie modulation, in terms of toxic effects and drug interactions, remain to be defined for populations exposed to high doses of pesticides, occurring notably in response to poisoning. However the alterations of these transporter activities by insecticides are unlikely to contribute to organophosphorus or pyrethroids toxicities of chronic low-dose exposure.