1 4822 122 OCHRATOXIN A: 50 YEARS OF RESEARCH. SINCE OCHRATOXIN A (OTA) WAS DISCOVERED, IT HAS BEEN UBIQUITOUS AS A NATURAL CONTAMINANT OF MOLDY FOOD AND FEED. THE MULTIPLE TOXIC EFFECTS OF OTA ARE A REAL THREAT FOR HUMAN BEINGS AND ANIMAL HEALTH. FOR EXAMPLE, OTA CAN CAUSE PORCINE NEPHROPATHY BUT CAN ALSO DAMAGE POULTRIES. HUMANS EXPOSED TO OTA CAN DEVELOP (NOTABLY BY INHALATION IN THE DEVELOPMENT OF ACUTE RENAL FAILURE WITHIN 24 H) A RANGE OF CHRONIC DISORDERS SUCH AS UPPER UROTHELIAL CARCINOMA. OTA PLAYS THE MAIN ROLE IN THE PATHOGENESIS OF SOME RENAL DISEASES INCLUDING BALKAN ENDEMIC NEPHROPATHY, KIDNEY TUMORS OCCURRING IN CERTAIN ENDEMIC REGIONS OF THE BALKAN PENINSULA, AND CHRONIC INTERSTITIAL NEPHROPATHY OCCURRING IN NORTHERN AFRICAN COUNTRIES AND LIKELY IN OTHER PARTS OF THE WORLD. OTA LEADS TO DNA ADDUCT FORMATION, WHICH IS KNOWN FOR ITS GENOTOXICITY AND CARCINOGENICITY. THE PRESENT ARTICLE DISCUSSES HOW RENAL CARCINOGENICITY AND NEPHROTOXICITY CAUSE BOTH OXIDATIVE STRESS AND DIRECT GENOTOXICITY. CAREFUL ANALYSES OF THE DATA SHOW THAT OTA CARCINOGENIC EFFECTS ARE DUE TO COMBINED DIRECT AND INDIRECT MECHANISMS (E.G., GENOTOXICITY, OXIDATIVE STRESS, EPIGENETIC FACTORS). ALTOGETHER THIS PROVIDES STRONG EVIDENCE THAT OTA CARCINOGENICITY CAN ALSO OCCUR IN HUMANS. 2016 2 2961 36 GENETIC AND EPIGENETIC MECHANISMS IN METAL CARCINOGENESIS AND COCARCINOGENESIS: NICKEL, ARSENIC, AND CHROMIUM. CHRONIC EXPOSURE TO NICKEL(II), CHROMIUM(VI), OR INORGANIC ARSENIC (IAS) HAS LONG BEEN KNOWN TO INCREASE CANCER INCIDENCE AMONG AFFECTED INDIVIDUALS. RECENT EPIDEMIOLOGICAL STUDIES HAVE FOUND THAT CARCINOGENIC RISKS ASSOCIATED WITH CHROMATE AND IAS EXPOSURES WERE SUBSTANTIALLY HIGHER THAN PREVIOUSLY THOUGHT, WHICH LED TO MAJOR REVISIONS OF THE FEDERAL STANDARDS REGULATING AMBIENT AND DRINKING WATER LEVELS. GENOTOXIC EFFECTS OF CR(VI) AND IAS ARE STRONGLY INFLUENCED BY THEIR INTRACELLULAR METABOLISM, WHICH CREATES SEVERAL REACTIVE INTERMEDIATES AND BYPRODUCTS. TOXIC METALS ARE CAPABLE OF POTENT AND SURPRISINGLY SELECTIVE ACTIVATION OF STRESS-SIGNALING PATHWAYS, WHICH ARE KNOWN TO CONTRIBUTE TO THE DEVELOPMENT OF HUMAN CANCERS. DEPENDING ON THE METAL, ASCORBATE (VITAMIN C) HAS BEEN FOUND TO ACT EITHER AS A STRONG ENHANCER OR SUPPRESSOR OF TOXIC RESPONSES IN HUMAN CELLS. IN ADDITION TO GENETIC DAMAGE VIA BOTH OXIDATIVE AND NONOXIDATIVE (DNA ADDUCTS) MECHANISMS, METALS CAN ALSO CAUSE SIGNIFICANT CHANGES IN DNA METHYLATION AND HISTONE MODIFICATIONS, LEADING TO EPIGENETIC SILENCING OR REACTIVATION OF GENE EXPRESSION. IN VITRO GENOTOXICITY EXPERIMENTS AND RECENT ANIMAL CARCINOGENICITY STUDIES PROVIDED STRONG SUPPORT FOR THE IDEA THAT METALS CAN ACT AS COCARCINOGENS IN COMBINATION WITH NONMETAL CARCINOGENS. COCARCINOGENIC AND COMUTAGENIC EFFECTS OF METALS ARE LIKELY TO STEM FROM THEIR ABILITY TO INTERFERE WITH DNA REPAIR PROCESSES. OVERALL, METAL CARCINOGENESIS APPEARS TO REQUIRE THE FORMATION OF SPECIFIC METAL COMPLEXES, CHROMOSOMAL DAMAGE, AND ACTIVATION OF SIGNAL TRANSDUCTION PATHWAYS PROMOTING SURVIVAL AND EXPANSION OF GENETICALLY/EPIGENETICALLY ALTERED CELLS. 2008 3 1993 32 EPIGENETIC AND EPITRANSCRIPTOMIC MECHANISMS OF CHROMIUM CARCINOGENESIS. HEXAVALENT CHROMIUM [CR(VI)], A GROUP I CARCINOGEN CLASSIFIED BY THE INTERNATIONAL AGENCY FOR RESEARCH ON CANCER (IARC), REPRESENTS ONE OF THE MOST COMMON OCCUPATIONAL AND ENVIRONMENTAL POLLUTANTS. THE FINDINGS FROM HUMAN EPIDEMIOLOGICAL AND LABORATORY ANIMAL STUDIES SHOW THAT LONG-TERM EXPOSURE TO CR(VI) CAUSES LUNG CANCER AND OTHER CANCER. ALTHOUGH CR(VI) IS A WELL-RECOGNIZED CARCINOGEN, THE MECHANISM OF CR(VI) CARCINOGENESIS HAS NOT BEEN WELL UNDERSTOOD. DUE TO THE FACT THAT CR(VI) UNDERGOES A SERIES OF METABOLIC REDUCTIONS ONCE ENTERING CELLS TO GENERATE REACTIVE CR METABOLITES AND REACTIVE OXYGEN SPECIES (ROS) CAUSING GENOTOXICITY, CR(VI) IS GENERALLY CONSIDERED AS A GENOTOXIC CARCINOGEN. HOWEVER, MORE AND MORE STUDIES HAVE DEMONSTRATED THAT ACUTE OR CHRONIC CR(VI) EXPOSURE ALSO CAUSES EPIGENETIC DYSREGULATIONS INCLUDING CHANGING DNA METHYLATION, HISTONE POSTTRANSLATIONAL MODIFICATIONS AND REGULATORY NON-CODING RNA (MICRORNA AND LONG NON-CODING RNA) EXPRESSIONS. MOREOVER, EMERGING EVIDENCE SHOWS THAT CR(VI) EXPOSURE IS ALSO CAPABLE OF ALTERING CELLULAR EPITRANSCRIPTOME. GIVEN THE INCREASINGLY RECOGNIZED IMPORTANCE OF EPIGENETIC AND EPITRANSCRIPTOMIC DYSREGULATIONS IN CANCER INITIATION AND PROGRESSION, IT IS BELIEVED THAT CR(VI) EXPOSURE-CAUSED EPIGENETIC AND EPITRANSCRIPTOMIC CHANGES COULD PLAY IMPORTANT ROLES IN CR(VI) CARCINOGENESIS. THE GOAL OF THIS CHAPTER IS TO REVIEW THE EPIGENETIC AND EPITRANSCRIPTOMIC EFFECTS OF CR(VI) EXPOSURE AND DISCUSS THEIR ROLES IN CR(VI) CARCINOGENESIS. BETTER UNDERSTANDING THE MECHANISM OF CR(VI) CARCINOGENESIS MAY IDENTIFY NEW MOLECULAR TARGETS FOR MORE EFFICIENT PREVENTION AND TREATMENT OF CANCER RESULTING FROM CR(VI) EXPOSURE. 2023 4 1819 33 EFFECTS OF CHRONIC OCHRATOXIN A EXPOSURE ON P53 HETEROZYGOUS AND P53 HOMOZYGOUS MICE. EXPOSURE TO THE MYCOTOXIN OCHRATOXIN A (OTA) CAUSES NEPHROPATHY IN DOMESTIC ANIMALS AND RODENTS AND RENAL TUMORS IN RODENTS AND POULTRY. HUMANS ARE EXPOSED TO OTA BY CONSUMING FOODS MADE WITH CONTAMINATED CEREAL GRAINS AND OTHER COMMODITIES. MANAGEMENT OF HUMAN HEALTH RISKS DUE TO OTA EXPOSURE DEPENDS, IN PART, ON ESTABLISHING A MODE OF ACTION (MOA) FOR OTA CARCINOGENESIS. TO FURTHER INVESTIGATE OTA'S MOA, P53 HETEROZYGOUS (P53+/-) AND P53 HOMOZYGOUS (P53+/+) MICE WERE EXPOSED TO OTA IN DIET FOR 26 WEEKS. THE FORMER ARE SUSCEPTIBLE TO TUMORIGENESIS UPON CHRONIC EXPOSURE TO GENOTOXIC CARCINOGENS. OTA-INDUCED RENAL DAMAGE BUT NO TUMORS WERE OBSERVED IN EITHER STRAIN, INDICATING THAT P53 HETEROZYGOSITY CONFERRED LITTLE ADDITIONAL SENSITIVITY TO OTA. RENAL CHANGES INCLUDED DOSE-DEPENDENT INCREASES IN CELLULAR PROLIFERATION, APOPTOSIS, KARYOMEGALY, AND TUBULAR DEGENERATION IN PROXIMAL TUBULES, WHICH WERE CONSISTENT WITH OCHRATOXICOSIS. THE LOWEST OBSERVED EFFECT LEVEL FOR RENAL CHANGES IN P53+/- AND P53+/+ MICE WAS 200 MUG OTA/KG BW/DAY. BASED ON THE LACK OF TUMORS AND THE SEVERITY OF RENAL AND BODY WEIGHT CHANGES AT A MAXIMUM TOLERATED DOSE, THE RESULTS WERE INTERPRETED AS SUGGESTIVE OF A PRIMARILY NONGENOTOXIC (EPIGENETIC) MOA FOR OTA CARCINOGENESIS IN THIS MOUSE MODEL. 2015 5 5493 20 REVIEW OF IN VITRO TEST SYSTEMS USING DNA DAMAGE AND REPAIR FOR SCREENING OF CHEMICAL CARCINOGENS. CHEMICAL CARCINOGENS ARE MECHANISTICALLY CLASSIFIED AS GENOTOXIC WHICH INTERACT DIRECTLY WITH DNA, AND EPIGENETIC WHICH CAUSE CHRONIC TISSUE INJURY, HORMONAL IMBALANCE, AND PROMOTIONAL EFFECTS. THIS REVIEW EVALUATES IN VITRO TESTS FOR THEIR CONTRIBUTION TO A BATTERY FOR IDENTIFYING GENOTOXIC CHEMICAL CARCINOGENS. IN ADDITION TO BACTERIAL MUTAGENIC ASSAYS, NONSPECIFIC DNA DAMAGE/REPAIR TESTS ARE RECOMMENDED FOR SCREENING CHEMICALS, IN PARTICULAR THE HEPATOCYTE PRIMARY CULTURE/DNA REPAIR TEST. 1979 6 4824 41 OCHRATOXIN A: THE CONTINUING ENIGMA. THE MYCOTOXIN OCHRATOXIN A (OTA) HAS BEEN LINKED TO THE GENESIS OF SEVERAL DISEASE STATES IN BOTH ANIMALS AND HUMANS. IT HAS BEEN DESCRIBED AS NEPHROTOXIC, CARCINOGENIC, TERATOGENIC, IMMUNOTOXIC, AND HEPATOTOXIC IN LABORATORY AND DOMESTIC ANIMALS, AS WELL AS BEING THOUGHT TO BE THE PROBABLE CAUSAL AGENT IN THE DEVELOPMENT OF NEPHROPATHIES (BALKAN ENDEMIC NEPHROPATHY, BEN AND CHRONIC INTERSTITIAL NEPHROPATHY, CIN) AND UROTHELIAL TUMORS IN HUMANS. AS A RESULT, SEVERAL INTERNATIONAL AGENCIES ARE CURRENTLY ATTEMPTING TO DEFINE SAFE LEGAL LIMITS FOR OTA CONCENTRATION IN FOODSTUFFS (E.G., GRAIN, MEAT, WINE, AND COFFEE), IN PROCESSED FOODS, AND IN ANIMAL FODDER. IN ORDER TO ACHIEVE THIS GOAL, AN ACCURATE RISK ASSESSMENT OF OTA TOXICITY INCLUDING MECHANISTIC AND EPIDEMIOLOGICAL STUDIES MUST BE CARRIED OUT. OCHRATOXIN HAS BEEN SUGGESTED BY VARIOUS RESEARCHERS TO MEDIATE ITS TOXIC EFFECTS VIA INDUCTION OF APOPTOSIS, DISRUPTION OF MITOCHONDRIAL RESPIRATION AND/OR THE CYTOSKELETON, OR, INDEED, VIA THE GENERATION OF DNA ADDUCTS. THUS, IT IS STILL UNCLEAR IF THE PREDOMINANT MECHANISM IS OF A GENOTOXIC OR AN EPIGENETIC NATURE. ONE ASPECT THAT IS CLEAR, HOWEVER, IS THAT THE TOXICITY OF OTA IS SUBJECT TO AND CHARACTERIZED BY LARGE SPECIES- AND SEX-SPECIFIC DIFFERENCES, AS WELL AS AN APPARENTLY STRICT STRUCTURE-ACTIVITY RELATIONSHIP. THESE CONSIDERATIONS COULD BE CRUCIAL IN THE INVESTIGATION OF OTA-MEDIATED TOXICITY. FURTHERMORE, THE USE OF APPROPRIATE IN VIVO AND IN VITRO MODEL SYSTEMS APPEARS TO BE VITAL IN THE GENERATION OF RELEVANT EXPERIMENTAL DATA. THE INTENTION OF THIS REVIEW IS TO COLLATE AND DISCUSS THE CURRENTLY AVAILABLE DATA ON OTA-MEDIATED TOXICITY WITH PARTICULAR FOCUS ON THEIR RELEVANCE FOR THE IN VIVO SITUATION, AND ALSO TO SUGGEST POSSIBLE FUTURE STRATEGIES FOR UNLOCKING THE SECRETS OF OCHRATOXIN A. 2005 7 474 25 ARSENIC BIOTRANSFORMATION AS A CANCER PROMOTING FACTOR BY INDUCING DNA DAMAGE AND DISRUPTION OF REPAIR MECHANISMS. CHRONIC EXPOSURE TO ARSENIC IN DRINKING WATER POSES A MAJOR GLOBAL HEALTH CONCERN. POPULATIONS EXPOSED TO HIGH CONCENTRATIONS OF ARSENIC-CONTAMINATED DRINKING WATER SUFFER SERIOUS HEALTH CONSEQUENCES, INCLUDING ALARMING CANCER INCIDENCE AND DEATH RATES. ARSENIC IS BIOTRANSFORMED THROUGH SEQUENTIAL ADDITION OF METHYL GROUPS, ACQUIRED FROM S-ADENOSYLMETHIONINE (SAM). METABOLISM OF ARSENIC GENERATES A VARIETY OF GENOTOXIC AND CYTOTOXIC SPECIES, DAMAGING DNA DIRECTLY AND INDIRECTLY, THROUGH THE GENERATION OF REACTIVE OXIDATIVE SPECIES AND INDUCTION OF DNA ADDUCTS, STRAND BREAKS AND CROSS LINKS, AND INHIBITION OF THE DNA REPAIR PROCESS ITSELF. SINCE SAM IS THE METHYL GROUP DONOR USED BY DNA METHYLTRANSFERASES TO MAINTAIN NORMAL EPIGENETIC PATTERNS IN ALL HUMAN CELLS, ARSENIC IS ALSO POSTULATED TO AFFECT MAINTENANCE OF NORMAL DNA METHYLATION PATTERNS, CHROMATIN STRUCTURE, AND GENOMIC STABILITY. THE BIOLOGICAL PROCESSES UNDERLYING THE CANCER PROMOTING FACTORS OF ARSENIC METABOLISM, RELATED TO DNA DAMAGE AND REPAIR, WILL BE DISCUSSED HERE. 2011 8 2840 34 FRAMEWORK ANALYSIS FOR THE CARCINOGENIC MODE OF ACTION OF NITROBENZENE. NITROBENZENE (CASRN: 98-95-3) HAS BEEN SHOWN TO INDUCE CANCERS IN MANY TISSUES INCLUDING KIDNEY, LIVER, AND THYROID, FOLLOWING CHRONIC INHALATION IN ANIMALS. HOWEVER, WITH A FEW EXCEPTIONS, GENOTOXICITY ASSAYS USING NITROBENZENE HAVE GIVEN NEGATIVE RESULTS. SOME DNA BINDING/ADDUCT STUDIES HAVE BROUGHT FORTH QUESTIONABLE RESULTS AND, CONSIDERING THE AVAILABLE WEIGHT OF EVIDENCE, IT DOES NOT APPEAR THAT NITROBENZENE CAUSES CANCER VIA A GENOTOXIC MODE OF ACTION. NITROBENZENE PRODUCES A NUMBER OF FREE RADICALS DURING ITS REDUCTIVE METABOLISM, IN THE GUT AS WELL AS AT THE CELLULAR LEVEL, AND GENERATES SUPEROXIDE ANION AS A BY-PRODUCT DURING OXIDATIVE MELABOLISM. THE REACTIVE SPECIES GENERATED DURING NITROBENZENE METABOLISM ARE CONSIDERED CANDIDATES FOR CARCINOGENICITY. FURTHERMORE, SEVERAL LINES OF EVIDENCE SUGGEST THAT NITROBENZENE EXERTS ITS CARCINOGENICITY THROUGH A NON-DNA REACTIVE (EPIGENETIC) FASHION, SUCH AS A STRONG TEMPORAL RELATIONSHIP BETWEEN NON-, PRE-, AND NEOPLASTIC LESIONS LEADING TO CARCINOGENESIS. IN THIS REPORT, WE FIRST DESCRIBE THE ABSORPTION, DISTRIBUTION, METABOLISM, AND EXCRETION OF NITROBENZENE FOLLOWED BY A SUMMARY OF THE AVAILABLE GENOTOXICITY STUDIES AND THE ONLY AVAILABLE CANCER BIOASSAY. WE SUBSEQUENTLY REFER TO THE MODE OF ACTION FRAMEWORK OF THE U.S. ENVIRONMENTAL PROTECTION AGENCY'S 2005 GUIDELINES FOR CARCINOGEN RISK ASSESSMENT AS A BASIS FOR PRESENTING POSSIBLE MODES OF ACTION FOR NITROBENZENE-INDUCED CANCERS OF THE LIVER, THYROID, AND KIDNEY, AS SUPPORTED BY THE AVAILABLE EXPERIMENTAL DATA. THE RATIONALE(S) REGARDING HUMAN RELEVANCE OF EACH MODE OF ACTION IS ALSO PRESENTED. FINALLY, WE HYPOTHESIZE THAT THE CARCINOGENIC MODE OF ACTION FOR NITROBENZENE IS MULTIFACTORIAL IN NATURE AND REFLECTIVE OF FREE RADICALS, INFLAMMATION, AND/OR ALTERED METHYLATION. 2007 9 6296 35 THE PROSPECTS FOR A SIMPLIFIED AND INTERNATIONALLY HARMONIZED APPROACH TO THE DETECTION OF POSSIBLE HUMAN CARCINOGENS AND MUTAGENS. IT IS PROPOSED THAT THE MANY SETS OF REGULATORY GUIDELINES FOR THE ASSESSMENT OF CHEMICAL CARCINOGENICITY AND MUTAGENICITY SHOULD BE SIMPLIFIED AND HARMONIZED IN LIGHT OF CURRENT EXPERIMENTAL DATA. DATA ARE DISCUSSED WHICH ILLUSTRATE THAT AN ABSOLUTE DISTINCTION WOULD BE DRAWN BETWEEN ASSAYS CONDUCTED IN VITRO FROM THOSE IN VIVO, AND THAT THE GENOTOXICITY OF A CHEMICAL CAN BE ADEQUATELY DEFINED USING A COMBINATION OF THE SALMONELLA MUTATION ASSAY AND ONE FOR THE ASSESSMENT OF CHROMOSOME ABERRATIONS IN VITRO. IT IS SPECIFICALLY RECOMMENDED THAT ONCE A CHEMICAL HAS SHOWN A CLEAR POSITIVE RESPONSE IN VITRO, FURTHER SHORT-TERM ASSAYS SHOULD BE CONDUCTED IN VIVO; THIS AVOIDS CONSIDERING THE 'WEIGHT OF EVIDENCE' OF IN VITRO DATA, THE DANGERS OF WHICH ARE ILLUSTRATED. IT HAS NOW BEEN UNEQUIVOCALLY ESTABLISHED THAT NOT ALL IN VITRO GENOTOXINS PROVE CARCINOGENIC TO MAMMALS. IT IS THEREFORE RECOMMENDED THAT ALL NEW IN VITRO GENOTOXINS SHOULD BE ASSESSED IN VIVO USING THE MOUSE BONE MARROW MICRONUCLEUS ASSAY, AND IF A NEGATIVE RESPONSE IS OBSERVED, A LIVER GENOTOXICITY TEST. AT PRESENT AN ASSAY FOR THE INDUCTION OF UNSCHEDULED DNA SYNTHESIS (UDS) IN THE LIVER IS THE MOST WELL DEVELOPED FOR THIS PURPOSE. CURRENT DATA INDICATE THAT AN IN VITRO GENOTOXIN FOUND TO BE INACTIVE IN THESE TWO IN VIVO ASSAYS WILL BE NEITHER CARCINOGENIC NOR MUTAGENIC TO THE GERM CELLS OF MAMMALS. EQUALLY, GENOTOXICITY PRODUCED IN MAMMALS INDICATES A CARCINOGENIC AND MUTAGENIC POTENTIAL WHICH CAN USUALLY ONLY BE COUNTERED BY APPROPRIATE CHRONIC BIOASSAYS. THE USE OF SHORT-TERM IN VIVO ASSAYS IN THIS CRITICAL ROLE REQUIRES ATTENTION TO THE SELECTION OF APPROPRIATE DOSE-LEVELS AND ROUTES OF EXPOSURE - THESE ISSUES ARE DISCUSSED. THE ABOVE TESTING STRATEGY WILL NOT DETECT CERTAIN ANIMAL CARCINOGENS, SOME OF WHICH ARE SPECIFICALLY DISCUSSED. THESE CARCINOGENS HAVE BEEN VARIOUSLY REFERRED TO IN THE LITERATURE AS EPIGENETIC/NON-GENOTOXIC/HORMONAL/TOXIC/AMBIGUOUS OR AMBIVALENT CARCINOGENS. IT IS SUGGESTED THAT THEY PRESENT A MINOR POTENTIAL HAZARD TO MAN WHEN COMPARED WITH THAT OF GENOTOXIC CARCINOGENS AND THAT THEIR SHORT-TERM DETECTION CAN ONLY BE ACHIEVED BY THE DEVELOPMENT OF NEW WHOLE MAMMAL ASSAYS EMPLOYING NON-GENETIC ENDPOINTS. THIS IS IN CONTRAST TO THE PRESENT TENDENCY TO EMPLOY ADDITIONAL GENOTOXICITY ASSAYS FOR THEIR DETECTION IN THE UNJUSTIFIED BELIEF THAT THEY POSSESS AN EXQUISITE SPECIFICITY OF GENOTOXIC ACTION. THIS ARTICLE REPRESENTS A PERSONAL VIEW, BUT THE TESTING STRATEGY PROPOSED IS BASED TO A LARGE EXTENT ON THE ORIGINAL THREE-TIER APPROACH OF BRIDGES.(ABSTRACT TRUNCATED AT 400 WORDS) 1986 10 1970 26 EPIGENETIC ALTERATIONS AND OCCUPATIONAL EXPOSURE TO BENZENE, FIBERS, AND HEAVY METALS ASSOCIATED WITH TUMOR DEVELOPMENT (REVIEW). THE CHRONIC OCCUPATIONAL EXPOSURE TO CONTAMINANTS AND CARCINOGENS LEADS TO THE DEVELOPMENT OF CANCER. OVER THE PAST DECADES, MANY CARCINOGENS HAVE BEEN FOUND IN THE OCCUPATIONAL ENVIRONMENT AND THEIR PRESENCE IS OFTEN ASSOCIATED WITH AN INCREASED INCIDENCE OF CANCER. ACCORDING TO THE INTERNATIONAL AGENCY FOR RESEARCH ON CANCER (IARC), THE MAJORITY OF CARCINOGENS ARE CLASSIFIED AS 'PROBABLE' AND 'POSSIBLE' HUMAN CARCINOGENS, WHILE, DIRECT EVIDENCE OF CARCINOGENICITY IS PROVIDED IN EPIDEMIOLOGICAL AND EXPERIMENTAL STUDIES. ADDITIONALLY, ACCUMULATING EVIDENCE SUGGESTS THAT EPIGENETIC ALTERATIONS MAY BE EARLY INDICATORS OF GENOTOXIC AND NON-GENOTOXIC CARCINOGEN EXPOSURE. IN THE PRESENT REVIEW, THE RELATIONSHIP BETWEEN EXPOSURES TO BENZENE, MINERAL FIBERS, METALS AND EPIGENETIC ALTERATIONS ARE DISCUSSED AS THE MOST IMPORTANT CANCER RISK FACTORS DURING WORK ACTIVITIES. 2017 11 4820 44 OCHRATOXIN A AS A POTENTIAL ETIOLOGIC FACTOR IN ENDEMIC NEPHROPATHY: LESSONS FROM TOXICITY STUDIES IN RATS. VARIOUS REPORTS SUGGEST THAT CHRONIC DIETARY EXPOSURE TO OCHRATOXIN A (OTA), A MYCOTOXIN FREQUENTLY DETECTED IN VARIOUS FOOD ITEMS MAY BE LINKED TO THE PATHOGENESIS OF ENDEMIC NEPHROPATHY, A CHRONIC TUBULOINTERSTITIAL KIDNEY DISEASE WHICH OCCURS IN GEOGRAPHICALLY LIMITED AREAS OF THE BALKAN REGION. OTA IS A POTENT NEPHROTOXIN AND RENAL CARCINOGEN. HOWEVER, THE PATHOLOGICAL LESIONS OBSERVED IN KIDNEYS OF RATS TREATED WITH OTA APPEAR BE RATHER DIFFERENT FROM THE CLINICAL AND PATHOLOGICAL CHARACTERISTICS OF ENDEMIC NEPHROPATHY. MOREOVER, INCREASING EVIDENCE SUGGESTS THAT OTA DOES NOT BIND TO DNA BUT INDUCES TUMORS BY AN EPIGENETIC, THRESHOLDED MECHANISM. THIS IMPLIES THAT THERE IS A DOSE BELOW WHICH NO ADVERSE HEALTH EFFECTS ARE EXPECTED TO OCCUR. BASED ON FOOD CONSUMPTION DATA AND OTA SERUM CONCENTRATIONS, IT APPEARS THAT HUMAN EXPOSURE - EVEN IN AREAS WITH RELATIVELY HIGH DIETARY EXPOSURE TO OTA SUCH AS ENDEMIC VILLAGES - IS SEVERAL ORDERS OF MAGNITUDE BELOW DOSES KNOWN TO CAUSE NEPHROTOXICITY AND TUMOR FORMATION IN LABORATORY ANIMALS. WHILE IT IS UNDOUBTEDLY IMPORTANT TO ENCOURAGE PREVENTION OF FOOD CONTAMINATION BY OTA AND OTHER MYCOTOXINS, THESE OBSERVATIONS SUGGEST THAT OTA IS NOT LIKELY TO BE AN ETIOLOGICAL FACTOR INVOLVED IN BEN AND INDICATE A NEED TO SEARCH FOR NEW CLUES FOR THE ETIOLOGY OF THIS ENDEMIC KIDNEY DISEASE. 2007 12 3623 33 IN VIVO COMET ASSAY ON ISOLATED KIDNEY CELLS TO DISTINGUISH GENOTOXIC CARCINOGENS FROM EPIGENETIC CARCINOGENS OR CYTOTOXIC COMPOUNDS. THE OBJECTIVE OF THIS STUDY WAS TO DETERMINE THE ABILITY OF THE ALKALINE IN VIVO COMET ASSAY (PH>13) TO DISTINGUISH GENOTOXIC CARCINOGENS FROM EPIGENETIC CARCINOGENS WHEN PERFORMED ON FRESHLY ISOLATED KIDNEY CELLS AND TO DETERMINE THE POSSIBLE INTERFERENCE OF CYTOTOXICITY BY ASSESSING DNA DAMAGE INDUCED BY RENAL GENOTOXIC, EPIGENETIC OR TOXIC COMPOUNDS AFTER ENZYMATIC ISOLATION OF KIDNEY CELLS FROM OFA SPRAGUE-DAWLEY MALE RATS. THE ABILITY OF THE COMET ASSAY TO DISTINGUISH (1) GENOTOXICITY VERSUS CYTOTOXICITY AND (2) GENOTOXIC VERSUS NON-GENOTOXIC (EPIGENETIC) CARCINOGENS, WAS THUS INVESTIGATED BY STUDYING FIVE KNOWN GENOTOXIC RENAL CARCINOGENS ACTING THROUGH DIVERSE MECHANISMS OF ACTION, I.E. STREPTOZOTOCIN, ARISTOLOCHIC ACIDS, 2-NITROANISOLE, POTASSIUM BROMATE AND CISPLATIN, TWO RODENT RENAL EPIGENETIC CARCINOGENS: D-LIMONENE AND CICLOSPORINE AND TWO NEPHROTOXIC COMPOUNDS: STREPTOMYCIN AND INDOMETHACIN. ANIMALS WERE TREATED ONCE WITH THE TEST COMPOUND BY THE APPROPRIATE ROUTE OF ADMINISTRATION AND GENOTOXIC EFFECTS WERE MEASURED AT THE TWO SAMPLING TIMES OF 3-6 AND 22-26H AFTER TREATMENT. REGARDING THE TISSUE PROCESSING, THE LIMITED BACKGROUND LEVEL OF DNA MIGRATION OBSERVED IN THE NEGATIVE CONTROL GROUPS THROUGHOUT ALL EXPERIMENTS DEMONSTRATED THAT THE ENZYMATIC ISOLATION METHOD IMPLEMENTED IN THE CURRENT STUDY IS APPROPRIATE. ON THE OTHER HAND, STREPTOZOTOCIN, 20MG/KG, USED AS POSITIVE REFERENCE CONTROL CONCURRENTLY TO EACH ASSAY, CAUSED A CLEAR INCREASE IN THE MEAN OLIVE TAIL MOMENT MEDIAN VALUE, WHICH ALLOWS VALIDATING THE CURRENT METHODOLOGY. UNDER THESE EXPERIMENTAL CONDITIONS, THE IN VIVO RODENT COMET ASSAY DEMONSTRATED GOOD SENSITIVITY AND GOOD SPECIFICITY: ALL THE FIVE RENAL GENOTOXIC CARCINOGENS WERE CLEARLY DETECTED IN AT LEAST ONE EXPRESSION PERIOD EITHER DIRECTLY OR INDIRECTLY, AS IN THE CASE OF CISPLATIN: FOR THIS CROSS-LINKING AGENT, THE SIGNIFICANT DECREASE IN DNA MIGRATION OBSERVED UNDER STANDARD ELECTROPHORESIS CONDITIONS WAS CLEARLY AMPLIFIED WHEN THE DURATION OF ELECTROPHORESIS WAS INCREASED UP TO 40MIN. IN CONTRAST, EPIGENETIC AND NEPHROTOXIC COMPOUNDS FAILED TO INDUCE ANY SIGNIFCANT INCREASE IN DNA MIGRATION. IN CONCLUSION, THE IN VIVO RODENT COMET ASSAY PERFORMED ON ISOLATED KIDNEY CELLS COULD BE USED AS A TOOL TO INVESTIGATE THE GENOTOXIC POTENTIAL OF A TEST COMPOUND IF NEOPLASIC/PRENEOPLASIC CHANGES OCCUR AFTER SUBCHRONIC OR CHRONIC TREATMENTS, IN ORDER TO DETERMINE THE ROLE OF GENOTOXICITY IN TUMOR INDUCTION. MOREOVER, THE EPIGENETIC CARCINOGENS AND CYTOTOXIC COMPOUNDS DISPLAYED CLEARLY NEGATIVE RESPONSES IN THIS STUDY. THESE RESULTS ALLOW EXCLUDING A DNA DIRECT-ACTING MECHANISM OF ACTION AND CAN THUS SUGGEST THAT A THRESHOLD EXISTS. THEREFORE, THE CURRENT IN VIVO RODENT COMET ASSAY COULD CONTRIBUTE TO ELUCIDATE AN EPIGENETIC MECHANISM AND THUS, TO UNDERTAKE A RISK ASSESSMENT ASSOCIATED WITH HUMAN USE, DEPENDING ON THE EXPOSURE LEVEL. 2007 13 4823 31 OCHRATOXIN A: POTENTIAL EPIGENETIC MECHANISMS OF TOXICITY AND CARCINOGENICITY. ASSESSMENT OF THE SIGNIFICANCE TO HUMAN HEALTH OF OCHRATOXIN A (OTA) IN FOOD IS LIMITED BY A LACK OF HUMAN TOXICITY DATA. THEREFORE, OTA RISK EVALUATION RELIES MAINLY ON THE USE OF ANIMAL DATA, WITH RENAL CARCINOGENICITY IN RAT BEING CONSIDERED AS THE PIVOTAL EFFECT. THE ELUCIDATION OF THE MECHANISM OF ACTION WOULD IMPROVE THE USE OF THE CARCINOGENICITY DATA FOR RISK ASSESSMENT. DIRECT GENOTOXICITY VERSUS EPIGENETIC MECHANISMS APPEARS TO BE A KEY QUESTION. IN THIS PRESENTATION, NEW BIOCHEMICAL AND TOXICOGENOMIC RESULTS OBTAINED IN A RECENT EUROPEAN PROJECT (EU-GRANT # QLK1-CT-2001-011614) WILL BE SUMMARIZED IN THE CONTEXT OF PREVIOUSLY REPORTED MECHANISMS OF ACTION INCLUDING INHIBITION OF PROTEIN SYNTHESIS, PRODUCTION OF OXIDATIVE STRESS AND ALTERATION OF CELL SIGNALLING. AMONGST OTHERS, THE NEW DATA INDICATE THAT CHRONIC ADMINISTRATION OF A CARCINOGENIC DOSE OF OTA AFFECTED CELL-SIGNALLING PATHWAYS RESULTING IN A SIGNIFICANTLY REDUCED RENAL ANTIOXIDANT DEFENCE AND INCREASED OXIDATIVE DNA DAMAGE. THESE DATA CONFIRM PREVIOUS HYPOTHESES INVOLVING OXIDATIVE STRESS AS A POSSIBLE KEY EPIGENETIC MECHANISM OF OTA TOXICITY AND CARCINOGENICITY. 2005 14 6553 28 TRANSGENERATIONAL EFFECTS IN DNA METHYLATION, GENOTOXICITY AND REPRODUCTIVE PHENOTYPE BY CHRONIC ARSENIC EXPOSURE. AN EMERGING CONCERN IS THE INFLUENCES OF EARLY LIFE EXPOSURE TO ENVIRONMENTAL TOXICANTS ON OFFSPRING CHARACTERISTICS IN LATER LIFE. SINCE RECENT EVIDENCE SUGGESTS A TRANSGENERATIONAL TRANSFERENCE OF ABERRANT PHENOTYPES FROM EXPOSED-PARENTS TO NON-EXPOSED OFFSPRING RELATED TO ADULT-ONSET DISEASES INCLUDING REPRODUCTIVE PHENOTYPE. THE TRANSGENERATIONAL POTENTIAL OF ARSENIC A WELL KNOW GENOTOXIC AND EPIGENETIC MODIFIER AGENT HAS NOT BEEN ASSESSED IN MAMMALS UNTIL NOW. IN THIS EXPERIMENTAL STUDY, WE EVALUATED THE TRANSGENERATIONAL EFFECTS OF ARSENIC IN A RAT MODEL WITH CHRONIC EXPOSURE TO ARSENIC. RATS CHRONICALLY EXPOSED TO ARSENIC IN DRINKING WATER (1 MG AS(2)O(3)/ML) (F0) WERE MATED TO PRODUCE THE ARSENIC LINEAGE (F1, F2, AND F3). THE ARSENIC TOXIC EFFECTS ON WERE EVALUATED OVER THE FOUR GENERATIONS BY ANALYZING THE DNA METHYLATION PERCENTAGE, GENOTOXICITY IN WBC AND PHYSICAL AND REPRODUCTIVE PARAMETERS, INCLUDING SPERM QUALITY PARAMETERS AND HISTOPATHOLOGICAL EVALUATION OF THE GONADS. CHRONIC EXPOSURE TO ARSENIC CAUSED GENOTOXIC DAMAGE (F0-F3) DIFFERENT METHYLATION PATTERNS, ALTERATIONS IN PHYSICAL AND REPRODUCTIVE PARAMETERS, ABERRANT MORPHOLOGY IN THE OVARIES (F0 AND F1) AND TESTICLES (F1-F3), AND A DECREASE IN THE QUALITY OF SPERM (F0-F3, EXCEPT F2). PARENTAL CHRONIC ARSENIC EXPOSURE CAUSES TRANSGENERATIONAL GENOTOXICITY AND CHANGES IN GLOBAL DNA METHYLATION WHICH MIGHT BE ASSOCIATED WITH REPRODUCTIVE DEFECTS IN RATS. COMBINED WITH RECENT STUDIES REVEAL THAT DISTURBANCES IN THE EARLY LIFE OF AN INDIVIDUAL CAN AFFECT THE HEALTH OF LATER GENERATIONS. 2021 15 567 29 BASIC PROPERTIES AND MOLECULAR MECHANISMS OF EXOGENOUS CHEMICAL CARCINOGENS. EXOGENOUS CHEMICAL CARCINOGENESIS IS AN EXTREMELY COMPLEX MULTIFACTORIAL PROCESS DURING WHICH GENE-ENVIRONMENT INTERACTIONS INVOLVING CHRONIC EXPOSURE TO EXOGENOUS CHEMICAL CARCINOGENS (ECCS) AND POLYMORPHISMS OF CANCER SUSCEPTIBILITY GENES ADD FURTHER COMPLEXITY. WE DESCRIBE THE PROPERTIES AND MOLECULAR MECHANISMS OF ECCS THAT CONTRIBUTE TO INDUCE AND GENERATE CANCER. A BASIC AND SPECIFIC PROPERTY OF MANY LIPOPHILIC ORGANIC ECCS INCLUDING POLYCYCLIC AROMATIC HYDROCARBONS AND POLYHALOGENATED AROMATIC HYDROCARBONS IS THEIR ABILITY TO BIOACCUMULATE IN THE ADIPOSE TISSUE FROM WHERE THEY MAY BE RELEASED IN THE BLOOD CIRCULATION AND TARGET PERIPHERAL TISSUES FOR CARCINOGENESIS. MANY ORGANIC ECCS ARE PROCARCINOGENS AND CONSEQUENTLY NEED TO BE ACTIVATED BY THE CYTOCHROME P450 (CYP) SYSTEM AND/OR OTHER ENZYMES BEFORE THEY CAN ADDUCT DNA AND PROTEINS. BECAUSE THEY CONTRIBUTE NOT ONLY TO THE COCARCINOGENIC AND PROMOTING EFFECTS OF MANY AROMATIC POLLUTANTS BUT ALSO TO THEIR MUTAGENIC EFFECTS, THE ARYL HYDROCARBON RECEPTOR-ACTIVATING AND THE INDUCIBLE CYP SYSTEMS ARE CENTRAL TO EXOGENOUS CHEMICAL CARCINOGENESIS. ANOTHER BASIC PROPERTY OF ECCS IS THEIR ABILITY TO INDUCE STABLE AND BULKY DNA ADDUCTS THAT CANNOT BE SIMPLY REPAIRED BY THE DIFFERENT REPAIR SYSTEMS. IN ADDITION, FOLLOWING ECC EXPOSURE, MUTAGENESIS MAY ALSO BE CAUSED INDIRECTLY BY FREE-RADICAL PRODUCTION AND BY EPIGENETIC ALTERATIONS. AS A RESULT OF COMPLEX MOLECULAR INTERPLAYS, DIRECT AND/OR INDIRECT MUTAGENESIS MAY ESPECIALLY ACCOUNT FOR THE CARCINOGENIC EFFECTS OF MANY EXOGENOUS METALS AND METALLOIDS. BECAUSE OF THESE MOLECULAR PROPERTIES AND ACTION MECHANISMS, WE CONCLUDE THAT ECCS COULD BE MAJOR CONTRIBUTORS TO HUMAN CANCER, WITH OBVIOUSLY GREAT PUBLIC HEALTH CONSEQUENCES. 2010 16 5057 24 PHENOBARBITAL MECHANISTIC DATA AND RISK ASSESSMENT: ENZYME INDUCTION, ENHANCED CELL PROLIFERATION, AND TUMOR PROMOTION. CHRONIC EXPOSURE TO HIGH DOSES OF PHENOBARBITAL (PB) CAUSES HEPATOCELLULAR ADENOMAS IN BOTH MICE AND RATS AND HEPATOCELLULAR CARCINOMAS IN SOME STRAINS OF MICE. LONG-TERM PB THERAPY HAS NOT BEEN FOUND TO CAUSE HUMAN TUMORS. PB IS NOT DNA REACTIVE, AND MOST GENOTOXICITY TESTS HAVE YIELDED NEGATIVE RESULTS. PB HAS BEEN EXTENSIVELY STUDIED AS AN EPIGENETIC, RODENT LIVER TUMOR PROMOTER. AT EXPOSURES CAUSING RODENT LIVER TUMORS, PB HAS MEASURABLE EFFECTS ON HEPATOCYTES: PB INHIBITS CELL-TO-CELL COMMUNICATION; PB INDUCES ENZYMES, INCLUDING P450 CYTOCHROMES; PB STIMULATES PROLIFERATION AND INHIBITS APOPTOSIS OF HEPATOCYTES IN NEOPLASTIC FOCI. THRESHOLD EXPOSURES FOR SOME OF THESE ENDPOINTS COINCIDE WITH THE THRESHOLD EXPOSURE FOR TUMORIGENESIS. 1996 17 4121 35 MECHANISMS OF CHEMICALLY INDUCED RENAL CARCINOGENESIS IN THE LABORATORY RODENT. LABORATORY STUDIES WITH CLASSICAL RENAL CARCINOGENS IN THE RAT AND MOUSE, AS WELL AS RESEARCH INVESTIGATION WITH SOME OF THE CHEMICALS PROVING POSITIVE FOR THE KIDNEY IN NATIONAL TOXICOLOGY PROGRAM CARCINOGENICITY BIOASSAYS, HAVE DEMONSTRATED THE EXISTENCE OF A RANGE OF DIVERSE MECHANISMS UNDERLYING RODENT KIDNEY CARCINOGENESIS. THE CLASSICAL CARCINOGENS USED AS EXPERIMENTAL MODELS FOR STUDYING RENAL TUMOR PATHOGENESIS, SUCH AS THE NITROSAMINES, ARE GENOTOXIC AND INTERACT DIRECTLY WITH DNA, FORMING DNA ADDUCTS WITH MUTAGENIC POTENTIAL. IN CONTRAST, POTASSIUM BROMATE AND FERRIC NITRILOTRIACETATE (FE-NTA), ALSO EFFECTIVE RENAL CARCINOGENS, APPEAR TO CAUSE INDIRECT DAMAGE TO DNA MEDIATED BY OXIDATIVE STRESS. A NUMBER OF NONGENOTOXIC CHEMICALS ARE ASSOCIATED WITH EPIGENETIC RENAL TUMOR INDUCTION IN RODENTS, AND THE ACTIVITY OF THESE TENDS TO INVOLVE PROLONGED STIMULATION OF CELL PROLIFERATION THROUGHOUT THE DURATION OF EXPOSURE. THIS MODE OF ACTION REFLECTS A SUSTAINED REGENERATIVE RESPONSE, EITHER DUE TO DIRECT CHEMICAL TOXICITY TO THE TUBULE CELLS, AS WITH CHLOROFORM, OR TO INDIRECT CYTOTOXICITY ASSOCIATED WITH LYSOSOMAL OVERLOAD, AS IN ALPHA2U-GLOBULIN ACCUMULATION IN MALE RATS RESULTING FROM THE ADMINISTRATION OF SUCH CHEMICALS AS D-LIMONENE AND TETRACHLOROETHYLENE. THE HISTOPATHOLOGIC NATURE OF HYDROQUINONE RENAL CARCINOGENESIS SUGGESTS THAT AN ADDITIONAL EPIGENETIC PATHWAY TO RENAL TUBULE TUMOR FORMATION IN RATS MAY BE THROUGH CHEMICAL-MEDIATED EXACERBATION OF, AND INTERACTION WITH, THE AGE-RELATED SPONTANEOUS RENAL DISEASE, CHRONIC PROGRESSIVE NEPHROPATHY. THESE VARIOUS MECHANISTIC PATHWAYS HAVE IMPLICATIONS FOR THE NATURE OF THE INDUCED CANCER PROCESS WITH RESPECT TO TUMOR INCIDENCE, LATENCY, MALIGNANCY, AND SEX PREDISPOSITION. 1998 18 4208 26 METAL CARCINOGEN EXPOSURE INDUCES CANCER STEM CELL-LIKE PROPERTY THROUGH EPIGENETIC REPROGRAMING: A NOVEL MECHANISM OF METAL CARCINOGENESIS. ARSENIC, CADMIUM, NICKEL AND HEXAVALENT CHROMIUM ARE AMONG THE MOST COMMON ENVIRONMENTAL POLLUTANTS AND POTENT CARCINOGENS. CHRONIC EXPOSURE TO THESE METALS CAUSES VARIOUS TYPES OF CANCER IN HUMANS, REPRESENTING A SIGNIFICANT ENVIRONMENTAL HEALTH ISSUE. ALTHOUGH UNDER ACTIVE INVESTIGATION, THE MECHANISMS OF METAL CARCINOGENESIS HAVE NOT BEEN CLEARLY DEFINED. ONE COMMON FEATURE OF THESE METAL CARCINOGENS IS THAT THEY ARE ALL ABLE TO CAUSE VARIOUS EPIGENETIC DYSREGULATIONS, WHICH ARE BELIEVED TO PLAY IMPORTANT ROLES IN THEIR CARCINOGENICITY. HOWEVER, HOW METAL CARCINOGEN-CAUSED EPIGENETIC DYSREGULATION CONTRIBUTES TO METAL CARCINOGENESIS REMAINS LARGELY UNKNOWN. THE EVOLUTION OF CANCER STEM CELL (CSC) THEORY HAS OPENED EXCITING NEW AVENUES FOR STUDYING THE MECHANISM OF METAL CARCINOGENESIS. INCREASING EVIDENCE INDICATES THAT CHRONIC METAL CARCINOGEN EXPOSURE PRODUCES CSC-LIKE CELLS THROUGH DYSREGULATED EPIGENETIC MECHANISMS. THIS REVIEW WILL FIRST PROVIDE SOME BRIEF INTRODUCTIONS ABOUT CSC, EPIGENETICS AND EPIGENETIC REGULATION OF CSCS; THEN SUMMARIZE PROGRESSES IN RECENT STUDIES ON METAL CARCINOGEN-INDUCED CSC-LIKE PROPERTY THROUGH EPIGENETIC REPROGRAMING AS A NOVEL MECHANISM OF METAL CARCINOGENESIS. SOME PERSPECTIVES FOR FUTURE STUDIES IN THIS FIELD ARE ALSO PRESENTED. 2019 19 6898 18 [THE ADVANCE OF MODEL OF ACTION IN LOW-DOSE CHRONIC BENZENE EXPOSURE INDUCED HEMATOTOXICITY]. BENZENE IS CLASSIFIED AS GROUP 1 CARCINOGEN BY IARC. IT HAS BEEN FOUND THAT BENZENE INDUCES HEMATOTOXICITY EVEN IN LOW DOSE EXPOSURE. THE IDENTIFICATION OF KEY EVENTS DURING BENZENE INDUCED HEMATOTOXICTY LEADS TO ADJUSTMENT OF OCCUPATIONAL EXPOSURE LIMITS OF BENZENE. IN THIS REVIEW, WE FOCUS ON THE EXPOSURE, METABOLISM, TARGET ORGANS, KEY EPIGENETIC CHANGES, TOXICTY EFFECTS AND END POINTS OF LOW-DOSE CHRONIC BENZENE EXPOSURE INDUCED HEMATOTOXICITY AND FINALLY DISCUSS THE PERSPECTIVES ON THE FUTURE STUDY OF THIS AREA. 2015 20 4819 25 OCCURRENCE OF TOXICITY AND CELL PROLIFERATION AFTER A SINGLE GAVAGE ADMINISTRATION OF CHLOROFORM TO MALE F344 RATS. CHLOROFORM, AN INDUSTRIAL SOLVENT AND ONE OF THE MOST COMMON ENVIRONMENTAL CONTAMINANTS WHICH PRODUCES CARCINOGENIC EFFECTS IN THE LIVER AND KIDNEY OF RODENTS, IS NOT GENOTOXIC IN MOST TRADITIONAL BACTERIAL AND MAMMALIAN TEST SYSTEMS. ITS CARCINOGENIC POTENTIAL APPEARS ATTRIBUTABLE TO THE SUSTAINED CELL TURNOVER (REGENERATIVE HYPERPLASIA) WHICH RESULTS FROM CHRONIC CHLOROFORM TOXICITY. IN THIS PRESENT STUDY, CELL PROLIFERATION (REPLICATIVE DNA SYNTHESIS, RDS) AND HISTOPATHOLOGICAL CHANGES IN HEPATOCYTES AND RENAL TUBULAR EPITHELIAL CELLS WERE ASSESSED IN MALE F344 RATS FOLLOWING A SINGLE GAVAGE CHLOROFORM EXPOSURE (50, 150 OR 500 MG/KG). IN ADDITION, BIOCHEMICAL PARAMETERS (BUN, GOT, LDH AND NAG) WERE EXAMINED USING PLASMA AND URINE SAMPLES. CELL PROLIFERATION AND HISTOPATHOLOGICAL CHANGES (E.G. HYPERTROPHY, NECROSIS, VACUOLATION) WERE ONLY SEEN AT THE DOSE OF 500 MG/KG IN THE LIVER AND KIDNEY. AT THE SAME DOSE, ALL BIOCHEMICAL MARKERS WERE INCREASED AT THE 24 TO 48 HR TIME POINTS. THESE RESULTS OBTAINED ARE THUS IN LINE WITH EARLIER FINDINGS POINTING TO EPIGENETIC CARCINOGENICITY. 1998