Incorporating toxicokinetics into an individual-based model for more realistic pesticide exposure estimates: A case study of the wood mouse

The potential risk of agricultural pesticides to mammals typically depends on internal concentrations within individuals, and these are determined by the amount ingested and by absorption, distribution, metabolism, and excretion (ADME). Pesticide residues ingested depend, amongst other things, on individual spatial choices which determine how much and when feeding sites and areas of pesticide application overlap, and can be calculated using individual-based models (IBMs). Internal concentrations can be calculated using toxicokinetic (TK) models, which are quantitative representations of ADME processes. Here we provide a population model for the wood mouse (Apodemus sylvaticus) in which TK submodels were incorporated into an IBM representation of individuals making choices about where to feed. This allows us to estimate the contribution of individual spatial choice and TK processes to risk. We compared the risk predicted by four IBMs: (i) “AllExposed-NonTK”: assuming no spatial choice so all mice have 100% exposure, no TK, (ii) “AllExposed-TK”: identical to (i) except that the TK processes are included where individuals vary because they have different temporal patterns of ingestion in the IBM, (iii) “Spatial-NonTK”: individual spatial choice, no TK, and (iv) “Spatial-TK”: individual spatial choice and with TK. The TK parameters for hypothetical pesticides used in this study were selected such that a conventional risk assessment would fail. Exposures were standardised using risk quotients (RQ; exposure divided by LD50 or LC50). We found that for the exposed sub-population including either spatial choice or TK reduced the RQ by 37–85%, and for the total population the reduction was 37–94%. However spatial choice and TK together had little further effect in reducing RQ. The reasons for this are that when the proportion of time spent in treated crop (PT) approaches 1, TK processes dominate and spatial choice has very little effect, and conversely if PT is small spatial choice dominates and TK makes little contribution to exposure reduction. The latter situation means that a short time spent in the pesticide-treated field mimics exposure from a small gavage dose, but TK only makes a substantial difference when the dose was consumed over a longer period. We concluded that a combined TK-IBM is most likely to bring added value to the risk assessment process when the temporal pattern of feeding, time spent in exposed area and TK parameters are at an intermediate level; for instance wood mice in foliar spray scenarios spending more time in crop fields because of better plant cover.

Toxicokinetics and toxicological effects of single oral dose of fumonisin B1 containing Fusarium verticillioides culture material in weaned piglets

Toxicokinetics and the toxicological effects of culture material containing fumonisin B(1) (FB(1)) were studied in male weaned piglets by clinical, pathological, biochemical and sphingolipid analyses. The animals received a single oral dose of 5 mg FB(1)/kg of body weight. obtained from Fusarium verticillioides culture material. FB(1) was detected by H PLC in plasma collected at 1-h intervals up to 6 h and at 12-h intervals up to 96 h. FB(1) eliminated in feces and urine was quantified over a 96-h period and in liver samples collected 96 h post-intoxication. Blood samples were obtained at the beginning and end of the experiment to determine serum enzyme activity, total bilirubin, cholesterol, sphinganine (Sa), sphingosine (So) and the Sa/So ratio. FB(1) was detected in plasma between 30 min and 36 h after administration. The highest concentration of FB(1) was observed after 2 h, with a mean concentration of 282 mu g/ml. Only 0.93% of the total FB(1) was detected in urine between 75 min and 41 h after administration, the highest mean concentration (561 mu g/ml) was observed during the interval after 8 at 24 h. Approximately 76.5% of FB(1) was detected in feces eliminated between 8 and 84 h after administration, with the highest levels observed between 8 and 24 h. Considering the biochemical parameters, a significant increase only occurred in cholesterol, alkaline phosphatase and aspartate aminotransferase activities. In plasma and urine, the highest Sa and Sa/So ratios were obtained at 12 and 48 h, respectively. (C) 2010 Elsevier Ireland Ltd. All rights reserved.

Nickel chloride: potential accumulation from the airway. Toxicokinetics in rats.

The rate removal of nickel from the airway was measured in vivo. Removal in vivo was studied by intratracheal injection of nickel chloride solutions. Regardless of time after injection, the lungs and heart retained the greatest concentration of nickel and 40 days after 1.68 mumol administration they were the organs where nickel was still significantly measurable. The slow removal of nickel may indicate the presence of high affinity binding sites in the lung. Nickel can interact with others metals, such as copper and zinc, so that nickel exposure may have public health implications.

Toxicokinetics of domoic acid in a nonhuman primate model (Macaca fascicularis)

Thesis (Master's)--University of Washington, 2016-06

Catchment-specific element signatures in estuarine crocodiles (Crocodylus porosus) from the Alligator Rivers Region, northern Australia

The concentrations of Na, K, Ca, Mg, Ba, Sr, Fe, Al, Mn, Zn, Pb, Cu, Ni, Cr, Co, Se, U and Ti were determined in the osteoderms and/or flesh of estuarine crocodiles (Crocodylus porosus) captured in three adjacent catchments within the Alligator Rivers Region (ARR) of northern Australia. Results from multivariate analysis of variance showed that when all metals were considered simultaneously, catchment effects were significant (P≤0.05). Despite considerable within-catchment variability, linear discriminant analysis (LDA) showed that differences in elemental signatures in the osteoderms and/or flesh of C. porosus amongst the catchments were sufficient to classify individuals accurately to their catchment of occurrence. Using cross-validation, the accuracy of classifying a crocodile to its catchment of occurrence was 76% for osteoderms and 60% for flesh. These data suggest that osteoderms provide better predictive accuracy than flesh for discriminating crocodiles amongst catchments. There was no advantage in combining the osteoderm and flesh results to increase the accuracy of classification (i.e. 67%). Based on the discriminant function coefficients for the osteoderm data, Ca, Co, Mg and U were the most important elements for discriminating amongst the three catchments. For flesh data, Ca, K, Mg, Na, Ni and Pb were the most important metals for discriminating amongst the catchments. Reasons for differences in the elemental signatures of crocodiles between catchments are generally not interpretable, due to limited data on surface water and sediment chemistry of the catchments or chemical composition of dietary items of C. porosus. From a wildlife management perspective, the provenance or source catchment(s) of 'problem' crocodiles captured at settlements or recreational areas along the ARR coastline may be established using catchment-specific elemental signatures. If the incidence of problem crocodiles can be reduced in settled or recreational areas by effective management at their source, then public safety concerns about these predators may be moderated, as well as the cost of their capture and removal. Copyright © 2002 Elsevier Science B.V.

Glutathione transferase activities in renal carcinomas and adjacent normal renal tissues : factors influencing renal carcinogenesis induced by xenobiotics

In general, the biological activation of nephrocarcinogenic chlorinated hydrocarbons proceeds via conjugatiton with glutathione. It has mostly been assamed that the main site of initial conjugation is the liver, followed by a mandatory transfer of intermediates to the kidney. It was therefore of interest to study the enzyme activities of subgroups of glutathione transferases (GSTs) in renal cancers and the surrounding normal renal tissues of the same individuals (n = 21). For genotyping the individuals with respect to known polymorphic GST isozymes the following substrates with differential specificity were used: 1-chloro-2,4-dinitrobenzene for overall GST activity (except GST θ); 7-chloro-4-nitrobenzo-2-oxa-1,3-diazole for GST α; 1,2-dichloro-4-nitro-benzene for GST μ; ethacrynic acid and 4-vinylpyridine for GST π; and methyl chloride for GST θ. In general, the normal tissues were able to metabolize the test substrates. A general decrease in individual GST enzyme activities was apparent in the course of cancerization, and in some (exceptional) cases individual activities, expressed in the normal renal tissue, were lost in the tumour tissue. The GST enzyme activities in tumours were independent of tumour stage, or the age and gender of the patients. There was little influence of known polymorphisms of GSTM1, GSTM3 and GSTP1 upon the activities towards the test substrates, whereas the influence of GSTT1 polymorphism on the activity towads methyl chloride was straightforward. In general, the present findings support the concept that the initial GST-dependent bioactivation step of nephrocarcinogenic chlorinated hydrocarbons may take place in the kidney itself. This should be a consideration in toxicokinetic modelling.

Differential substrate behaviours of ethylene oxide and propylene oxide towards human glutathione transferase theta hGSTT1-1

The transformation of ethylene oxide (EO), propylene oxide (PO) and 1- butylene oxide (1-BuO) by human glutathione transferase theta (hGSTT1-1) was studied comparatively using 'conjugator' (GSTT1 + individuals) erythrocyte lysates. The relative sequence of velocity of enzymic transformation was PO > EO >> 1-BuO. The faster transformation of PO compared to EO was corroborated in studies with human and rat GSTT1-1 (hGSTT1-1 and rGSTT1-1, respectively) expressed by Salmonella typhimurium TA1535. This sequence of reactivities of homologous epoxides towards GSTT1-1 contrasts to the sequence observed in homologous alkyl halides (methyl bromide, MBr; ethyl bromide, EtBr; n-propyl bromide, PrBr) where the relative sequence MeBr >> EtBr > PrBr is observed. The higher reactivity towards GSTT1-1 of propylene oxide compared to ethylene oxide is consistent with a higher chemical reactivity. This is corroborated by experimental data of acid-catalysed hydrolysis of a number of aliphatic epoxides, including ethylene oxide and propylene oxide and consistent with semi-empirical molecular orbital modelings.

The toxicology of climate change: environmental contaminants in a warming world.

Climate change induced by anthropogenic warming of the earth's atmosphere is a daunting problem. This review examines one of the consequences of climate change that has only recently attracted attention: namely, the effects of climate change on the environmental distribution and toxicity of chemical pollutants. A review was undertaken of the scientific literature (original research articles, reviews, government and intergovernmental reports) focusing on the interactions of toxicants with the environmental parameters, temperature, precipitation, and salinity, as altered by climate change. Three broad classes of chemical toxicants of global significance were the focus: air pollutants, persistent organic pollutants (POPs), including some organochlorine pesticides, and other classes of pesticides. Generally, increases in temperature will enhance the toxicity of contaminants and increase concentrations of tropospheric ozone regionally, but will also likely increase rates of chemical degradation. While further research is needed, climate change coupled with air pollutant exposures may have potentially serious adverse consequences for human health in urban and polluted regions. Climate change producing alterations in: food webs, lipid dynamics, ice and snow melt, and organic carbon cycling could result in increased POP levels in water, soil, and biota. There is also compelling evidence that increasing temperatures could be deleterious to pollutant-exposed wildlife. For example, elevated water temperatures may alter the biotransformation of contaminants to more bioactive metabolites and impair homeostasis. The complex interactions between climate change and pollutants may be particularly problematic for species living at the edge of their physiological tolerance range where acclimation capacity may be limited. In addition to temperature increases, regional precipitation patterns are projected to be altered with climate change. Regions subject to decreases in precipitation may experience enhanced volatilization of POPs and pesticides to the atmosphere. Reduced precipitation will also increase air pollution in urbanized regions resulting in negative health effects, which may be exacerbated by temperature increases. Regions subject to increased precipitation will have lower levels of air pollution, but will likely experience enhanced surface deposition of airborne POPs and increased run-off of pesticides. Moreover, increases in the intensity and frequency of storm events linked to climate change could lead to more severe episodes of chemical contamination of water bodies and surrounding watersheds. Changes in salinity may affect aquatic organisms as an independent stressor as well as by altering the bioavailability and in some instances increasing the toxicity of chemicals. A paramount issue will be to identify species and populations especially vulnerable to climate-pollutant interactions, in the context of the many other physical, chemical, and biological stressors that will be altered with climate change. Moreover, it will be important to predict tipping points that might trigger or accelerate synergistic interactions between climate change and contaminant exposures.

Mercury in feral fish: distribution, accumulation and toxicity

O principal objectivo desta dissertação foi estudar a acumulação de mercúrio em vários tecidos de peixes marinhos, a sua relação com factores biológicos e as respectivas respostas bioquímicas. O trabalho realizado permitiu obter novos conhecimentos sobre a acumulação de mercúrio em peixes, possibilitando avaliar a influência da biodisponibilidade do elemento e as suas possíveis implicações no ambiente. O trabalho foi desenvolvido na Ria de Aveiro (Portugal), uma zona costeira onde existe um gradiente ambiental de mercúrio, o que oferece a oportunidade de estudar a sua acumulação e os seus efeitos tóxicos em condições realísticas. As amostragens foram efectuadas em dois locais considerados críticos em termos de contaminação por mercúrio – Largo do Laranjo (L1 e L2) e num local afastado da principal fonte de poluição, usado como termo de comparação (Referência; R); L1 e L2 corresponderam a locais moderadamente e altamente contaminados, respectivamente. Foram escolhidos juvenis de duas espécies ecologicamente diferentes e representativas da comunidade piscícola local, a tainha garrento (Liza aurata) e o robalo (Dicentrarchus labrax). Em cada local foram recolhidas amostras de água e de sedimento para determinação de mercúrio. Foram quantificadas as concentrações de mercúrio total (T-Hg) e orgânico (O-Hg) em vários tecidos dos peixes, escolhidos tendo em conta a sua função relativamente à toxicocinética e toxicodinâmica de metais. As respostas antioxidantes (Catalase- CAT, glutationa peroxidase- GPx, glutationa reductase- GR, glutationa –S-transferase- GST e conteúdo em glutationa total- GSHt), o dano peroxidativo (LPO) e o conteúdo em metalotioninas (MTs) foram também avaliados. A acumulação de T-Hg foi semelhante para as duas espécies de peixes estudadas, embora D. labrax tenha apresentado concentrações tendencialmente maiores. Ambas as espécies demonstraram capacidade de reflectir o grau de contaminação ambiental existente, indicando claramente que a acumulação depende da concentração ambiental. A acumulação revelou-se específica de cada tecido. O padrão da acumulação em L. aurata foi rim > fígado > músculo > cérebro > guelras > sangue e em D. labrax foi fígado > rim > músculo > cérebro ≈ guelras > sangue. Relativamente à acumulação de OHg, verificou-se que D. labrax exibiu concentrações mais elevadas que L. aurata. Todos os tecidos foram capazes de reflectir diferenças entre R e L2. Os níveis de O-Hg no fígado, músculo e nos conteúdos intestinais foram diferentes entre espécies, sendo mais elevados para D. labrax. As guelras e o intestino foram os tecidos onde se obtiveram os valores mais baixos de O-Hg e observaram-se valores idênticos para as duas espécies. Com excepção das guelras, as concentrações de O-Hg variaram em função do valor observado nos conteúdos intestinais, indicando que a alimentação é a via dominante da acumulação. As concentrações de O-Hg nos conteúdos intestinais revelaram ser uma informação relevante para prever a acumulação de O-Hg nos tecidos, pois verificou-se uma razão praticamente constante entre o teor de mercúrio no fígado, no músculo e nos conteúdos intestinais. A percentagem de O-Hg no músculo e no fígado variou de acordo com o grau de contaminação ambiental e com o tipo de assimilação preferencial do elemento (alimentação vs. água), sugerindo que o fígado exerce um papel protector em relação à acumulação de mercúrio nos outros órgãos. Ambas as espécies de peixes demonstraram ser boas sentinelas da contaminação ambiental com mercúrio (T-Hg e O-Hg), sendo o cérebro e o músculo os tecidos que melhor reflectiram o grau de acumulação com o elemento. A análise conjunta dos dados de bioacumulação e de respostas ao stress oxidativo permitiram estabelecer uma relação entre as concentrações de mercúrio nas guelras, fígado, rim e cérebro e a sua toxicidade. As respostas do cérebro aos efeitos tóxicos do mercúrio revelaram ser específicas de cada espécie. Enquanto que para o cérebro de L. aurata se verificou um decréscimo de todos os parâmetros antioxidantes estudados nos locais contaminados, sem haver evidência de qualquer mecanismo compensatório, no D. labrax observaram-se respostas ambivalentes, que indicam por um lado a activação de mecanismos adaptativos e, por outro, o decréscimo das respostas antioxidantes, ou seja, sinais de toxicidade. Embora em ambas as espécies de peixe fosse evidente uma condição pró-oxidante, o cérebro parece possuir mecanismos compensatórios eficientes, uma vez que não se verificou peroxidação lipídica. As respostas antioxidantes do cérebro de D. labrax foram comparadas em diferentes períodos do ano - quente vs. frio. O período quente mostrou ser mais crítico, uma vez que no período frio não se verificaram diferenças nas respostas entre locais, ou seja, a capacidade antioxidante do cérebro parece ser influenciada pelos factores ambientais. As guelras revelaram susceptibilidade à contaminação por mercúrio, uma vez que se verificou uma tendência para o decréscimo da actividade de CAT em L2 e ausência de indução em L1. O fígado e o rim demonstraram mecanismos adaptativos face ao grau de contaminação moderada (L1), evidenciados pelo aumento de CAT. O rim também demonstrou adaptabilidade face ao grau elevado de contaminação (L2), uma vez que se verificou um aumento GST. Embora o grau de susceptibilidade tenha sido diferente entre os órgãos, não se verificou peroxidação lipídica em nenhum. A determinação do conteúdo em MTs em D. labrax e em L. aurata revelou que este parâmetro depende não só da espécie, mas também do tecido em causa. Assim, em D. labrax foi observado um decréscimo de MTs no cérebro, bem como a incapacidade de síntese de MTs no sangue, guelras, fígado, rim e músculo. Em L. aurata observou-se um aumento do conteúdo em MTs no fígado e no músculo. Estes resultados indicam que a aplicabilidade das MTs como biomarcador de exposição ao mercúrio parece ser incerta, revelando limitações na capacidade de reflectir os níveis de exposição ao metal e por consequência o grau de acumulação. Este trabalho comprova a necessidade de se integrarem estudos de bioacumulação com biomarcadores de efeitos, de modo a reduzir os riscos de interpretações erróneas, uma vez que as respostas nem sempre ocorrem para os níveis mais altos de contaminação ambiental com mercúrio.

Liquid chromatography-tandem mass spectrometry (LC/APCI-MS/MS) methods for the quantification of captan and folpet phthalimide metabolites in human plasma and urine.

Captan and folpet are fungicides largely used in agriculture. They have similar chemical structures, except that folpet has an aromatic ring unlike captan. Their half-lives in blood are very short, given that they are readily broken down to tetrahydrophthalimide (THPI) and phthalimide (PI), respectively. Few authors measured these biomarkers in plasma or urine, and analysis was conducted either by gas chromatography coupled to mass spectrometry or liquid chromatography with UV detection. The objective of this study was thus to develop simple, sensitive and specific liquid chromatography-atmospheric pressure chemical ionization-tandem mass spectrometry (LC/APCI-MS/MS) methods to quantify both THPI and PI in human plasma and urine. Briefly, deuterated THPI was added as an internal standard and purification was performed by solid-phase extraction followed by LC/APCI-MS/MS analysis in negative ion mode for both compounds. Validation of the methods was conducted using spiked blank plasma and urine samples at concentrations ranging from 1 to 250 μg/L and 1 to 50 μg/L, respectively, along with samples of volunteers and workers exposed to captan or folpet. The methods showed a good linearity (R (2) > 0.99), recovery (on average 90% for THPI and 75% for PI), intra- and inter-day precision (RSD, <15%) and accuracy (<20%), and stability. The limit of detection was 0.58 μg/L in urine and 1.47 μg/L in plasma for THPI and 1.14 and 2.17 μg/L, respectively, for PI. The described methods proved to be accurate and suitable to determine the toxicokinetics of both metabolites in human plasma and urine.

Caractérisation de la toxicocinétique de l’octylphénol chez le rat en vue d’une meilleure analyse de risque toxicologique des perturbateurs endocriniens

Le p-tert-octylphénol est un produit présent dans l’environnement et issu de la dégradation des alkylphénols éthoxylés. Ce composé a la capacité de se lier au récepteur œstrogénique et d’exercer ainsi un léger effet œstrogénique. Les objectifs de cette étude étaient de 1) développer une méthode d'identification de l'octylphénol dans le sang et les tissus à l'aide de la chromatographie en phase gazeuse jumelée à la spectrométrie de masse, 2) caractériser la toxicocinétique sanguine et tissulaire de l’octylphénol chez le rat Sprague-Dawley mâle et femelle et 3) développer un modèle toxicocinétique à base physiologique permettant de décrire la cinétique sanguine et tissulaire de l’octylphénol inchangé. Pour ce faire, des rats mâle et femelle Sprague-Dawley ont reçu des doses uniques d’octylphénol par les voies intraveineuse, orale et sous-cutanée. Deux autres groupes ont reçu des doses répétées d'octylphénol par voie orale pour une durée de 35 jours consécutifs pour les femelles ou 60 jours pour les mâles. Les concentrations sanguines et tissulaires d’octylphénol ont été mesurées à différents moments après administration à partir d’une méthode d’analyse développée dans nos laboratoires dans le cadre de ce projet. Les expériences impliquant des administrations uniques ont montré que les concentrations sanguines et tissulaires d'octylphénol étaient en général plus élevées chez les femelles que chez les mâles. Des expériences réalisées avec des microsomes hépatiques ont confirmé que ces différences étaient vraisemblablement reliées au métabolisme de l'octylphénol. Les expériences impliquant des administrations répétées ont montré qu'il n'y avait pas d'accumulation d'octylphénol dans l'organisme aux doses étudiées. Les résultats obtenus expérimentalement ont servi à développer et valider un modèle toxicocinétique à base physiologique. Ce modèle a permis de simuler adéquatement les concentrations sanguines et tissulaires d'octylphénol suite à des expositions intraveineuses, orales et sous-cutanées. En conclusion, cette étude a fourni des données essentielles sur la toxicocinétique de l'octylphénol. Ces données sont nécessaires pour établir la relation entre la dose externe et la dose interne et vont contribuer à une meilleure évaluation des risques liés à l'octylphénol.

Développement d'outils de surveillance biologique pour l'évaluation des risques à la santé des travailleurs en arboriculture et en viticulture exposés aux fongicides

De nombreux travailleurs utilisent le captan et le folpet comme fongicides en agriculture, mais leur exposition n’est pas toujours mesurée de manière spécifique et précise. La surveillance biologique est un excellent outil à cet effet puisqu’elle permet de quantifier l’exposition réelle. Toutefois, la majorité des connaissances toxicologiques pour ces fongicides proviennent d’études sur les animaux, et les données chez l’humain sont limitées. Le but du présent projet est donc de développer des outils de surveillance biologique pour évaluer l’exposition de travailleurs au captan et au folpet. Dans cette perspective, le projet a été subdivisé en trois parties complémentaires, soit i) de développer des méthodes analytiques spécifiques pour quantifier les biomarqueurs d’intérêt du captan, à savoir le tétrahydrophtalimide (THPI), et du folpet, à savoir le phtalimide (PI) et l’acide phtalique, dans le plasma et l’urine; ii) de déterminer la toxicocinétique des deux fongicides en exposant des volontaires de façon aigüe à de faibles doses de captan ou de folpet par voie orale et cutanée dans des conditions semi-contrôlées et en quantifiant les biomarqueurs dans chacune des deux matrices, excepté l’acide phtalique qui a été mesuré seulement dans l’urine; iii) de valider les biomarqueurs d’exposition sélectionnés et d’évaluer l’exposition réelle des travailleurs et les voies prédominantes d’exposition au captan et au folpet en collectant des données biologiques chez des travailleurs en arboriculture et en viticulture lors d’activités de traitement et d’effeuillage pendant sept jours consécutifs. Selon ces travaux, le THPI et le PI sont deux biomarqueurs valides et spécifiques pour quantifier l’exposition au captan et au folpet, respectivement, chez l’humain. En effet, les méthodes développées pour ces deux métabolites sont robustes avec des limites de détection plus sensibles que celles rapportées dans la littérature, un taux de recouvrement de 90% pour le THPI et de 75% pour le PI, une très bonne linéarité (R2>0,99) et une bonne stabilité avec des variations intra- et inter-journalières faibles (RSD<15%). Elles ont permis de déterminer les profils cinétiques des deux métabolites chez les volontaires et chez les travailleurs. Ces derniers indiquent d’ailleurs une élimination rapide, avec une demi-vie d’élimination dans l’urine de 11,7 h et 18,7 h pour le THPI et de 27,3 h et 28,8 h pour le PI, respectivement après une absorption par voie orale et cutanée, ainsi qu’une faible absorption cutanée lorsque les valeurs sont comparées pour les deux voies d’exposition. Des profils parallèles sont aussi observés entre le PI et l’acide phtalique pour les volontaires et les agriculteurs, mais le folpet se retrouve davantage métabolisé sous forme d’acide phtalique que de PI. Quant à l’étude des agriculteurs, elle montre que la voie principale d’exposition de ces travailleurs est la voie cutanée. Il est aussi souligné qu’il est important 1) de favoriser les collectes d’urines complètes sur 24 h au urines ponctuelles, 2) de mesurer plusieurs métabolites, et 3) d’associer les données de surveillance biologique à la toxicocinétique. Ainsi, les connaissances acquises par cette étude peuvent s’appliquer à d’autres fongicides, voire d’autres substances.

Développement de modèles prédictifs de la toxicocinétique de substances organiques

Les modèles pharmacocinétiques à base physiologique (PBPK) permettent de simuler la dose interne de substances chimiques sur la base de paramètres spécifiques à l’espèce et à la substance. Les modèles de relation quantitative structure-propriété (QSPR) existants permettent d’estimer les paramètres spécifiques au produit (coefficients de partage (PC) et constantes de métabolisme) mais leur domaine d’application est limité par leur manque de considération de la variabilité de leurs paramètres d’entrée ainsi que par leur domaine d’application restreint (c. à d., substances contenant CH3, CH2, CH, C, C=C, H, Cl, F, Br, cycle benzénique et H sur le cycle benzénique). L’objectif de cette étude est de développer de nouvelles connaissances et des outils afin d’élargir le domaine d’application des modèles QSPR-PBPK pour prédire la toxicocinétique de substances organiques inhalées chez l’humain. D’abord, un algorithme mécaniste unifié a été développé à partir de modèles existants pour prédire les PC de 142 médicaments et polluants environnementaux aux niveaux macro (tissu et sang) et micro (cellule et fluides biologiques) à partir de la composition du tissu et du sang et de propriétés physicochimiques. L’algorithme résultant a été appliqué pour prédire les PC tissu:sang, tissu:plasma et tissu:air du muscle (n = 174), du foie (n = 139) et du tissu adipeux (n = 141) du rat pour des médicaments acides, basiques et neutres ainsi que pour des cétones, esters d’acétate, éthers, alcools, hydrocarbures aliphatiques et aromatiques. Un modèle de relation quantitative propriété-propriété (QPPR) a été développé pour la clairance intrinsèque (CLint) in vivo (calculée comme le ratio du Vmax (μmol/h/kg poids de rat) sur le Km (μM)), de substrats du CYP2E1 (n = 26) en fonction du PC n octanol:eau, du PC sang:eau et du potentiel d’ionisation). Les prédictions du QPPR, représentées par les limites inférieures et supérieures de l’intervalle de confiance à 95% à la moyenne, furent ensuite intégrées dans un modèle PBPK humain. Subséquemment, l’algorithme de PC et le QPPR pour la CLint furent intégrés avec des modèles QSPR pour les PC hémoglobine:eau et huile:air pour simuler la pharmacocinétique et la dosimétrie cellulaire d’inhalation de composés organiques volatiles (COV) (benzène, 1,2-dichloroéthane, dichlorométhane, m-xylène, toluène, styrène, 1,1,1 trichloroéthane et 1,2,4 trimethylbenzène) avec un modèle PBPK chez le rat. Finalement, la variabilité de paramètres de composition des tissus et du sang de l’algorithme pour les PC tissu:air chez le rat et sang:air chez l’humain a été caractérisée par des simulations Monte Carlo par chaîne de Markov (MCMC). Les distributions résultantes ont été utilisées pour conduire des simulations Monte Carlo pour prédire des PC tissu:sang et sang:air. Les distributions de PC, avec celles des paramètres physiologiques et du contenu en cytochrome P450 CYP2E1, ont été incorporées dans un modèle PBPK pour caractériser la variabilité de la toxicocinétique sanguine de quatre COV (benzène, chloroforme, styrène et trichloroéthylène) par simulation Monte Carlo. Globalement, les approches quantitatives mises en œuvre pour les PC et la CLint dans cette étude ont permis l’utilisation de descripteurs moléculaires génériques plutôt que de fragments moléculaires spécifiques pour prédire la pharmacocinétique de substances organiques chez l’humain. La présente étude a, pour la première fois, caractérisé la variabilité des paramètres biologiques des algorithmes de PC pour étendre l’aptitude des modèles PBPK à prédire les distributions, pour la population, de doses internes de substances organiques avant de faire des tests chez l’animal ou l’humain.