Reliability of toxicokinetic modelling for PFAS exposure assessment in contaminated water in northern Italy.

Introduction: Long-term contamination of tap water and groundwater by perfluoroalkyl and polyfluoroalkyl substances (PFASs) has been documented in the Veneto region of northern Italy. This study aimed to assess the exposure of individuals residing in the contaminated area and to test several toxicokinetic (TK) models of varying complexities to identify an efficient method for predicting perfluorooctanoic acid (PFOA) and perfluorooctanesulfonic acid (PFOS) concentrations in human serum using observed data.The ultimate goal is to provide public health officials with guidance on selecting the appropriate TK model for specific contexts, a reliable and rapid tool to support human bio-monitoring (HBM) studies. Methods: Two simpler empirical TK models and a more complex multi-compartment physiologically based toxicokinetic (PBTK) model were compared with individual and aggregate data from an HBM study. In addition, the PBPK model was modified by adjusting input parameters and introducing new terms into the equations within the original model code. These modifications aimed to optimize the results compared to the original model, with some versions incorporating adjustments to account for the influence of menstruation in women. All models were evaluated to understand their strengths and weaknesses, providing guidance on the appropriate model to use according to specific scenarios. Results: The results obtained from the tested models were quite similar, with significant improvements observed only in the modified models. Simpler models also provided satisfactory results in scenarios involving low PFOS serum concentrations and recent exposure cessation. In many cases, predictions demonstrated high accuracy, particularly at the aggregate level and for women. Conclusions: These findings suggest that environmental protection agencies and health authorities may benefit from employing the tested models at the aggregate level as an initial step in HBM studies, rather than conducting more invasive and expensive screening campaigns.

On the dynamics of random Boolean networks subject to noise: attractors, ergodic sets and cell types.

The asymptotic dynamics of random Boolean networks subject to random fluctuations is investigated. Under the influence of noise, the system can escape from the attractors of the deterministic model, and a thorough study of these transitions is presented. We show that the dynamics is more properly described by sets of attractors rather than single ones. We generalize here a previous notion of ergodic sets, and we show that the Threshold Ergodic Sets so defined are robust with respect to noise and, at the same time, that they do not suffer from a major drawback of ergodic sets. The system jumps from one attractor to another of the same Threshold Ergodic Set under the influence of noise, never leaving it. By interpreting random Boolean networks as models of genetic regulatory networks, we also propose to associate cell types to Threshold Ergodic Sets rather than to deterministic attractors or to ergodic sets, as it had been previously suggested. We also propose to associate cell differentiation to the process whereby a Threshold Ergodic Set composed by several attractors gives rise to another one composed by a smaller number of attractors. We show that this approach accounts for several interesting experimental facts about cell differentiation, including the possibility to obtain an induced pluripotent stem cell from a fully differentiated one by overexpressing some of its genes.

Multidrug resistance and malignancy in human osteosarcoma.

In osteosarcoma, resistance to chemotherapy and metastatic spread are the most important mechanisms responsible for the failure of current multimodal therapeutic programs. We have shown previously that overexpression of the MDR1 gene product P-glycoprotein is the most important predictor of an adverse clinical course in patients with osteosarcoma. treated with chemotherapy. In this study, we analyzed the relationship between P-glycoprotein expression and local aggressiveness and systemic dissemination of multidrug-resistant (MDR) human osteosarcoma cells. Compared to parental sensitive cells, MDR cells showed a decreased tumorigenicity,and metastatic ability in athymic mice, together with a reduced migratory and invasive ability and a lower homotypic adhesion ability in vitro, suggesting that P-glycoprotein overexpression is associated with a less malignant phenotype. These experimental observations were confirmed by clinical data. In fact, the time of appearance of lung metastases in a series of osteosarcoma patients treated with chemotherapy was significantly shorter in the group of cases with no expression of P-glycoprotein in the primary lesion compared to the group with P-glycoprotein overexpression. Moreover, the incidence of P-glycoprotein overexpression was found to be higher among patients with localized disease at the clinical onset than in patients with evidence of metastasis at the time of diagnosis. These data indicate that, in osteosarcoma, the MDR phenotype is not associated with a more aggressive behavior both in vitro and in clinical settings, suggesting that the previously shown association of the MDR phenotype with a worse outcome in osteosarcoma is not related to a higher metastatic ability of cells with P-glycoprotein overexpression but is more likely due to their lack of responsiveness to cytotoxic drugs.

In vivo and in vitro binding of epichlorohydrin to nucleic acids.

Epichlorohydrin (EC) binds to macromolecules of biological relevance in vivo: DNA is less labelled than RNA and proteins, rat organs interact more than mouse organs, stomach is the most labelled organ with liver, kidney and lung involved in decreasing order. Based on the Covalent Binding Index (CBI), EC is a weak-moderate oncogen, just as other chlorinated hydrocarbons such as 1,2-dichloroethane and carbon tetrachloride. An interaction of EC with nucleic acids (DNA and polyribonucleotides) occurs also in vitro. It is mediated either by chemical reactivity per se of the molecule (near-UV (NUV) irradiation does not photoactivate EC) and by enzymatic (microsomal and/or cytosolic) fractions, whose relative effectiveness is variable in relation to the organ tested. The best substrates for interaction are poly(G) and poly(A) when using microsomal and cytosolic fractions, respectively, whereas the labelling of double-stranded DNA is always lower. On the whole, the picture of enzyme (microsome + cytosol)-mediated in vitro interaction is similar to the pattern of in vivo binding, with the exception of rat stomach enzymes which are inactive in vitro.

In vivo and in vitro binding of benzene to nucleic acids and proteins of various rat and mouse organs.

Benzene binds to macromolecules of various organs in the rat and mouse in vivo. Labelling of RNA and proteins is higher (1 order of magnitude) than DNA labelling, which is low in many organs (liver, spleen, bone marrow and kidney), and negligible in lung; no difference between labelling of rat and mouse organs was found. The covalent binding index (CBI) value was about 10, i.e. typical of genotoxic carcinogens classified as weak initiators. In vitro binding of benzene to nucleic acids and proteins is mediated by hepatic microsomes, but not by microsomes from kidney, spleen and lung, or by cytosol from whatever organ. Nucleic acid binding can be induced by pretreatment with phenobarbitone (PB) and suppressed in the presence of SKF 525-A, of cytosol and/or GSH or of heat-inactivated microsomes. Labelling of exogenous DNA is low and is similar in the presence of rat or mouse microsomes in agreement with the low interaction with DNA measured in vivo.

Initiating activity of 1,1,2,2-tetrachloroethane in two-stage BALB/c 3T3 cell transformation.

By using in vitro two-stage BALB/c 3T3 cell transformation assay, we have tested the effect of promoting treatment with tetradecanoylphorbol acetate (TPA) on transformation induced by 1,1,2,2-tetrachloroethane (1,1,2,2-TTCE). Cells were treated with subeffective or transforming concentrations of 1,1,2,2-TTCE in the presence of an S9-mix activating system, followed by TPA promoting treatment. The transforming activity of 1,1,2,2-TTCE is evident only by reseeding confluent cells and allowing additional rounds of cell replications in the amplification test. Treatment with TPA leads to a marked transformation yield in all plates scored even at the lowest assayed dosage of 1,1,2,2-TTCE, without performing amplification of transformation.

Cytotoxic activity and transformation of BALB/c 3T3 cells in vitro by the insecticide acephate.

Cytotoxic and cell transforming activity of the organophosphate insecticide acephate have been studied in an in vitro experimental model which foresees the exposure of BALB/c 3T3 cells to the chemical. The assay was performed in the presence or absence of metabolic activation system derived from phenobarbital and beta-naphthoflavone induced rats (S9-mix). Cytotoxicity of acephate was unaffected by the presence of the metabolizing fraction. Cell-transforming potential, evidenced through the induction of transformation foci, was observed at all tested doses (i.e. 100, 200 and 400 micrograms/ml) with or without exogenous bioactivation. This activity was related with cell proliferation since it was particularly evident in a level-II cell-transformation assay when the cells were allowed to perform active proliferative activity. These findings, obtained in a medium-term (6-8 weeks) test, may contribute to a better understanding of the action of acephate in the multistep carcinogenesis, proving more information on the oncogenic risk to humans.

Results of animal studies suggest a nonlinear dose-response relationship for benzene effects.

Considering the very large industrial usage of benzene, studies in risk assessment aimed at the evaluation of carcinogenic risk at low levels of exposure are important. Animal data can offer indications about what could happen in humans and provide more diverse information than epidemiological data with respect to dose-response consideration. We have considered experiments investigating metabolism, short-term genotoxicity tests, DNA adduct formation, and carcinogenicity long-term tests. According to the different experiments, a saturation of benzene metabolism and benzene effects in terms of genotoxicity seems evident above 30 to 100 ppm. Below 30 to 60 ppm the initiating effect of benzene seems to be linear for a large interval of dosages, at least judging from DNA adduct formation. Potential lack of a promoting effect of benzene (below 10 ppm) could generate a sublinear response at nontoxic levels of exposure. This possibility was suggested by epidemiological data in humans and is not confirmed or excluded by our observations with animals.

Benzene adducts with rat nucleic acids and proteins: dose-response relationship after treatment in vivo.

The dose-response relationship of the benzene covalent interaction with biological macromolecules from rat organs was studied. The administered dose range was 3.6 x 10(7) starting from the highest dosage employed, 486 mg/kg, which is oncogenic for rodents, and included low and very low dosages. The present study was initially performed with tritium-labeled benzene, administered by IP injection. In order to exclude the possibility that part of the detected radioactivity was due to tritium incorporated into DNA from metabolic processes, 14C-benzene was then also used following a similar experimental design. By HPLC analysis, a single adduct from benzene-treated DNA was detected; adduct identification will be attempted in the near future. Linear dose-response relationship was observed within most of the range of explored doses. Linearity was particularly evident within low and very low dosages. Saturation of benzene metabolism did occur at the highest dosages for most of the assayed macromolecules and organs, especially in rat liver. This finding could be considered as indicative of the dose-response relationship of tumor induction and could be used in risk assessment.

Induction of a malignant phenotype in BALB/c 3t3 cells by 1,1,2,2-tetrachloroethane.

BALB/c 3T3 cells transformed by 1,1,2,2-tetrachloroethane, the most toxic chloroethane, acquired a fully malignant phenotype. They were capable of growing in soft agar, were tumorigenic when injected in athymic mice and produced pulmonary nodules after i.v. injection. Untreated BALB/c 3T3 cells were weakly tumorigenic (3/9 animals developed tumors after a longer time) and induced rare pulmonary nodules in a low percentage of animals. Transformed cells were also invasive in the chemoinvasion assay. Moreover, they grew in a gel of reconstituted basement membrane (matrigel), penetrating the gel and assuming a branching morphology that has been associated to the malignant phenotype. By contrast, spontaneous transformants isolated from solvent controls were poorly invasive in these assays. These results show that 1,1,2,2-tetrachloroethane could play a role in the late steps of multistage carcinogenesis.

In vivo and in vitro binding of 1,2-dibromoethane and 1,2-dichloroethane to macromolecules in rat and mouse organs.

The comparative interaction of equimolar amounts of 1,2-dichloroethane and 1,2-dibromoethane with rat and mouse nucleic acids was studied in both in vivo (liver, lung, kidney and stomach) and in vitro (liver microsomal and/or cytosolic fractions) systems. In vivo, liver and kidney DNA showed the highest labeling, whereas the binding to lung DNA was barely detectable. Dibromoethane was more highly reactive than dichloroethane in both species. With dichloroethane, mouse DNA labeling was higher than rat DNA labeling whatever the organ considered: the opposite was seen for the bioactivation of dibromoethane. RNA and protein labelings were higher than DNA labeling, with no particular pattern in terms of organ or species involvement. In vitro, in addition to a low chemical reactivity towards nucleic acids shown by haloethanes per se, both compounds were bioactivated by either liver microsomes and cytosolic fractions to reactive forms capable of binding to DNA and polynucleotides. UV irradiation did not photoactivate dibromoethane and dichloroethane. The in vitro interaction with DNA mediated by enzymatic fractions was PB-inducible (one order of magnitude, using rat microsomes). In vitro bioactivation of haloethanes was mainly performed by microsomes in the case of dichloroethane and by cytosolic fractions in the case of dibromoethane. When microsomes plus cytosol were used, rat enzymes were more efficient than mouse enzymes in inducing a dibromoethane-DNA interaction: the opposite situation occurred for dichloroethane-DNA interaction, and this is in agreement with the in vivo pattern. In the presence of both metabolic pathways, addition or synergism occurred. Dibromoethane was always more reactive than dichloroethane. An indication of the presence of a microsomal GSH transferase was achieved for the activation of dibromoethane. No preferential binding in vitro to a specific polynucleotide was found. Polynucleotide labeling was higher than (or equal to) DNA binding. The labeling of microsomal RNA and proteins and of cytosolic proteins was many times lower than that of DNA or polynucleotides. The in vivo and in vitro data reported above give an unequivocal indication of the relative reactivity of the haloethanes examined with liver macromolecules from the two species and agree, on the whole, with the relative genotoxicity (DNA repair induction ability, mutagenicity and carcinogenicity) of the chemicals.

In vitro cytotoxic and cell transforming activities exerted by the pesticides cyanazine, dithianon, diflubenzuron, procymidone, and vinclozolin on BALB/c 3T3 cells.

Cytotoxic and cell transforming activities of the pesticides cyanazine, diflubenzuron, dithianon, procymidone, and vinclozolin were investigated in vitro by utilizing the BALB/c 3T3 cell transformation test performed in the presence or in the absence of S-9 mix as an exogenous bioactivation system for the chemicals. All the assayed pesticides were cytotoxic in the absence of S-9 mix, whereas only dithianon exerted cytotoxic effects in the presence of metabolic activation. All the chemicals tested did induce BALB/c 3T3 cell transformation, to a various extent, in the absence of S-9 mix. Cell transforming ability of cyanazine and diflubenzuron was not detectable in the presence of S-9.

Evaluation of genotoxic effects of the herbicide dicamba using in vivo and in vitro test systems.

The genotoxic effects of the herbicide dicamba have been studied by measuring 1) the unwinding rate of liver DNA from intraperitoneally (i.p.) treated rats (fluorimetric assay); 2) DNA repair as unscheduled DNA synthesis (UDS) induced in cultured human peripheral blood lymphocytes (HPBL); and 3) sister chromatid exchanges (SCE) in HPBL. Results show that dicamba is capable of inducing DNA damage since it significantly increases the unwinding rate of rat liver DNA in vivo and also induces UDS in HPBL in vitro in the presence of exogenous metabolic activation (S-9 mix). Furthermore, dicamba causes a very slight increase in SCE frequency in HPBL in vitro.

In vitro effects of fenretinide on cell-matrix interactions.

BACKGROUND: Understanding the molecular basis of the metastatic spread of cancer and the underlying mechanisms is crucial for the development and appropriate clinical use of novel therapeutic agents directed at prevention of metastasis. Retinoids have been reported to inhibit cell proliferation, modulate cell differentiation, enhance apoptosis and to prevent the conversion of in situ cancer to locally invasive malignancy by suppressing the invasive process as well as by inhibiting angiogenesis. Fenretinide (4-HPR), a synthetic derivative of retinoic acid, is less toxic than natural retinoids and is active in the prevention and treatment of a variety of tumours in animal models. Its efficacy in cancer chemoprevention and therapy has been investigated in clinical trials. MATERIALS AND METHODS: In order to evaluate the effects of 4-HPR on the late stages of tumour progression, chemically transformed BALB/c 3T3 cells, showing a fully malignant phenotype, were exposed to 4-HPR (0.25-10 microM; 72 hours pre-treatment) and then analysed for in vitro invasive ability. The possible mechanisms of action responsible for the anti-invasive activity of 4-HPR were investigated, analysing cellular adhesion, motility, and proteolytic capability. RESULTS: Data showed that 4-HPR significantly inhibited the invasive phenotype of chemically transformed cells; the reduction in Matrigel invasion was dose-dependent and seemed not to be related to cytotoxic effects or reduction in cell proliferation rates induced by 4-HPR assayed doses. The 4-HPR-induced decrease in chemotactic motility of transformed cells correlated well with the invasion inhibition. 4-HPR, at active concentrations, differently affected cell adhesion to the extracellular matrix, depending on the coating substrate used (laminin, collagen IV, fibronectin and vitronectin). 4-HPR treatment significantly enhanced cell adhesion to laminin, while reducing cell-vitronectin attachment. It did not modify the attachment of the cells to fibronectin and collagen IV. Zymographic analysis failed to demonstrate 4-HPR involvement in the modulation of the activity and expression of gelatine degrading enzymes. CONCLUSION: These data suggest that 4-HPR inhibits tumour cell invasion through a basement-like matrix, by suppressing chemotactic motility and by altering cell-matrix interactions.

Effects of the protease inhibitor antipain on cell malignant transformation.

BACKGROUND: Several natural products have been found to exhibit a chemopreventive activity both in in vivo and in vitro experimental systems. Among them, protease inhibitors seem to play a key role in the regulation of growth and phenotypic expression of transformed cells as well as in the regulation of the late events of carcinogenesis. We evaluated the effect of antipain (AP), a natural protease inhibitor, on chemically induced BALB/c 3T3 cell transformation, on invasion and chemotactic motility of transformed cells and on their gelatinase expression. METHODS: BALB/c 3T3 cells were plated and exposed to 2.5 micrograms/ml 3-MCA or 50 micrograms/ml, 1,2-DBE. The effect of a non-cytotoxic dosage of AP (10 microM) was studied by: a) pretreating cells with AP for 48 hours before the carcinogen exposure; b) adding AP simultaneously to the carcinogen treatment; c) chronic addition of AP at each medium change throughout the experimental duration. The effectiveness of the treatment was analysed as the ability to reduce or inhibit the occurrence of transformed foci. Modulation of the invasive phenotype by anti-transforming dosages of AP was evaluated by in vitro Matrigel invasion assay. Gelatin zymography was performed in order to assess AP regulation of proteolytic enzymes, such as metalloproteases, involved in invasion and metastasis. RESULTS: AP treatment can reduce the transformation rate both in 3-MCA- and 1,2-DBE-initiated cells. Its effectiveness depends on the administration schedule, and chronic addition seems to be the most effective treatment. The concentration of AP, which is effective in the antitransformation assay, is not able to significantly affect the migration and invasion of chemically transformed cells or their gelatinase activity. CONCLUSIONS: AP can suppress chemically induced BALB/c 3T3 cell transformation through mechanisms which do not involve modulation of the invasive phenotype.

The covalent interaction of 1,4-dibromobenzene with rat and mouse nucleic acids: in vivo and in vitro studies.

1,4-Dibromobenzene (1,4-DBB) was covalently bound to DNA from liver, kidney, lung and stomach of mice after intraperitoneal administration. The covalent binding index (CBI) value (23 in mouse liver) was typical of weak initiators. On the contrary, no interaction with DNA from rat organs was observed (CBI detection limit: 1.3-2.6). The in vitro interaction of 1,4-DBB with calf thymus DNA was mediated mainly by microsomes, especially those from liver of both species and from mouse lung. Mouse subcellular fractions were more active then rat subcellular fractions. Unlike liver cytosol, subcellular cytosolic fractions from lung, kidney and stomach were capable of bioactivating 1,4-DBB, although to a lesser extent than liver microsomes. Both cytochrome P-450 and GSH-transferases are involved in 1,4-DBB bioactivation.

Genetic safety evaluation of pesticides in different short-term tests.

Cyanazine, cyhexatin, dicamba and DNOC are pesticides commonly and broadly used in agriculture pest control. However, there is little information on their toxicity and mutagenicity in human cells and in whole animals. Therefore, UDS assay and SCE assay in human peripheral lymphocytes, and chromosome aberration analysis in bone marrow of rats have been used to assess the DNA-damaging activity of the above pesticides. Cyanazine proved non-genotoxic in all the test systems. Cyhexatin showed only weakly positive results for SCE induction in human lymphocytes, providing no concern for genotoxicological hazard. While dicamba did not show clastogenic effects in rodents, DNOC gave significant dose-related increases of structural chromosome aberrations in rat bone marrow cells. Female animals showed increased sensitivity to the toxic effects by DNOC at the highest dose. The results provide further information on the intrinsic genotoxic activity of the tested pesticides, which may contribute to the toxicological assessment of the risk associated with human exposure.

The different genotoxicity of p-dichlorobenzene in mouse and rat: measurement of the in vivo and in vitro covalent interaction with nucleic acids.

Twenty-two hours after i.p. injection to male Wistar rats and BALB/c mice para-dichlorobenzene (p-DCB) is bound covalently to DNA from liver, kidney, lung and stomach of mice but not of rats. DNA adducts in mouse liver are repaired in seventy-two hours. The covalent binding index value, calculated on the labelling of mouse liver DNA, classifies p-DCB as a weak initiator with an oncogenic activity lower than that of chlorobenzene. The labelling of RNA and proteins from the different organs of both species is, however, low. In vitro interaction with calf thymus DNA mediated by mouse and rat microsomes from liver and lung did occur. Binding extent was strongly reduced by addition of 2-diethylaminoethyl-2,2-diphenylvalerate hydrochloride (SKF 525-A) to the microsomal standard incubation mixture, whereas it was enhanced by adding GSH. Cytosolic fractions from kidney and lung were able to induce binding of p-DCB to DNA to a lower extent with respect to microsome-mediated binding. These results indicate that microsomal mixed function oxidase system and microsomal GSH-transferases can be involved in overall activating metabolism whereas cytosolic GSH-transferases play a minor role. This study, which is a part of a structure-activity relationship approach on benzene and its haloderivatives, provides the first evidence of genotoxicity of p-DCB in mammalian cell. It allows to partly explain variations of susceptibility of different species to hepatocarcinogenesis and of hepatotoxicity of different isomers.

In vivo and in vitro interaction of 1,2-dichlorobenzene with nucleic acids and proteins of mice and rats.

Twenty-two hours after i.p. injection into male Wistar rats and BALB/c mice, 1,2-dichlorobenzene (1,2-DCB) was covalently bound to DNA, RNA, and proteins of liver, kidney, lung and stomach. The covalent binding index to liver DNA was typical of carcinogens classified as weak initiators. The enzyme-mediated in vitro interaction of 1,2-DCB with calf thymus DNA of synthetic polyribonucleotides was carried out by a microsomal mixed-function oxidase system and microsomal GSH-transferases, which seemed to be effective only in liver and lung of rat and mouse. Cytosolic GSH-transferases played a minor role in 1,2-DCB bioactivation. The latter finding provides the first evidence of 1,2-DCB genotoxicity in mammalian cells. The type of halide, the number of halosubstituents and their spatial disposition on the benzene ring are the major determinants of halobenzenes activability to intermediate(s) capable of interacting covalently with DNA and other macromolecules in biologic systems.

Chloroform bioactivation leading to nucleic acids binding.

Chloroform was bound covalently to DNA, RNA and proteins of rat and mouse organs in vivo after i.p. injection. Covalent Binding Index values of rat and mouse liver DNA classify chloroform as a weak initiator. Labelings of RNA and proteins from various organs of both species were higher than that of DNA. In an in vitro cell-free system, chloroform was bioactivated by cytochrome P450-dependent microsomal fractions, by cytosolic GSH-transferases from rat and mouse liver, and particularly by the latter enzymes from mouse lung. This observation suggests that GSH plays a role in the binding of chloroform metabolites to DNA. The presence of both microsomal and cytosolic enzymatic systems in the standard incubation mixture generally led to an additive or synergistic bioactivating effect for rat and mouse, respectively.