Biomarkers for assessing occupational exposures to 1,3-butadiene

The overall objective of this study was to evaluate a continuum of biomarkers in blood and urine for their sensitivities as indicators of low level occupational exposures to 1,3 butadiene (BD). The study design was largely cross-sectional, with biological samples collected within a short timeframe. Personal 8-h BD exposure measures were made on several occasions over a 60-day period for each potentially exposed worker in order provide maximum accuracy for this independent variable and to accommodate the different expression intervals of the several biomarkers. Co-exposures to styrene, toluene and benzene were also measured. The study included 24 BD monomer production workers (mean BD exposure=0.642 mg/m(3)), 34 polymerization workers (mean BD exposure=1.794 mg/m(3)) and 25 controls (mean BD exposure=0.023 mg/m(3)). The several biomarkers were measured by a consortium of investigators at different locations in the US and Europe. These biomarkers included: (1) metabolic genotypes (CYP2E1, EH, GST M1, GST T1, ADH2, ADH3), determined in Prague and Burlington, VT; (2) urinary M1 and M2 metabolites (1,2-dihydroxy-4-[N-acetylcysteinyl]-butane and 1-hydroxy-2-[N-acetylcysteinyl]-3-butene, respectively), determined in Albuquerque, NM and Leiden; (3) hemoglobin adducts (N-[2-dihydroxy-3-butenyl]valine=HBVal and N-[2,3,4-trihydroxybutyl]valine=THBVal), determined in Amsterdam and Chapel Hill, NC, respectively; (4) HPRT mutations determined by autoradiographic assay in Galveston, TX, with slides re-read in Burlington, VT; (6) hypoxanthine-guanine phosphoribosyltransferase (HPRT) mutations determined by cloning assay in Leiden with mutational spectra characterized in Burlington, VT; (7) sister chromatid exchanges and chromosome aberrations determined by standard methods and FISH analysis in Prague. Urinary M1 and M2 metabolites and HBVal and THBVal hemoglobin adducts were all significantly correlated with BD exposure levels, with adducts being the most highly associated. No significant relationships were observed between BD exposures and HPRT mutations or any of the cytogenetic endpoints, regardless of method of assay.

DNA adducts of 1,3-butadiene in humans: relationships to exposure, GST genotypes, single-strand breaks, and cytogenetic end points

The modulation of 1,3-butadiene (BD)-induced DNA adducts by occupational exposure, glutathione S-transferase (GST) genotypes, single-strand breaks, and cytogenetic end points was studied in 15 workers and 11 controls. The exposed group consisted of 8 smokers and 7 nonsmokers, whereas the control group consisted of 7 nonsmokers and 4 smokers. Among all subjects, the adduct levels in workers lacking GSTM1 were significantly higher than in those who were GSTM1 positive (P = 0.026), and individuals with combined GSTM1(-) and GSTT1(+) genotype had elevated level of adducts compared to that of persons with GSTM1(+) and GSTT1(+) (P = 0.049). The increase in BD-DNA adduct levels in all subjects was significantly related to BD exposure and GSTM1 genotype (linear multiple regression analysis, P = 0.001; P = 0.035). The results suggest that DNA adducts serve as a sensitive and specific biomarker, integrating exposure and host metabolic capacity, although the data are limited to a small number of subjects.

Mutagenicity, carcinogenicity, and teratogenicity of acrylonitrile

Acrylonitrile (AN) is an important intermediary for the synthesis of a variety of organic products, such as artificial fibres, household articles and resins. Although acute effects are the primary concern for an exposure to AN, potential genotoxic, carcinogenic and teratogenic risks of AN have to be taken seriously in view of the large number of workers employed in such industries and the world-wide population using products containing and possibly liberating AN. An understanding of the effect of acrylonitrile must be based on a characterization of its metabolism as well as of the resulting products and their genotoxic properties. Tests for mutagenicity in bacteria have in general been positive, those in plants and on unscheduled DNA synthesis doubtful, and those on chromosome aberrations in vivo negative. Wherever positive results had been obtained, metabolic activation of AN appeared to be a prerequisite. The extent to which such mutagenic effects are significant in man depends, however, also on the conditions of exposure. It appears from the limited data that the ultimate mutagenic factor(s), such as 2-cyanoethylene oxide, may have little opportunity to act under conditions where people are exposed because it is formed only in small amounts and is rapidly degraded. The carcinogenic action of AN has been evaluated by various agencies and ranged from 'reasonably be anticipated to be a human carcinogen' to 'cannot be excluded', the most recent evaluation being 'possibly carcinogenic to humans'. Animal data that confirm the carcinogenic potential of AN have certain limitations with respect to the choice of species, type of tumors and length of follow up. Epidemiological studies which sometimes, but not always, yielded positive results, encounter the usual difficulties of confounding factors in chemical industries. Exposure of workers to AN should continue to be carefully monitored, but AN would not have to be considered a cancer risk to the population provided limitations on releases from consumer products and guidelines on AN in water and air are enforced. AN is teratogenic in laboratory animals (rat, hamster) at high doses when foetal/embryonic (and maternal) toxicity already is manifest. Pregnant workers should not be exposed to AN. In view of the small concentrations generally encountered outside plants, women not professionally exposed would appear not to be at risk of teratogenic effects due to AN. Future research should concentrate on the elucidation of the different degradation pathways in man and on epidemiological studies in workers including pregnant women, assessing also, if possible, individual exposure by bio-monitoring.

The influence of alpha-tocopherol and pyritinol on oxidative DNA damage and lipid peroxidation in human lymphocytes

Unscheduled DNA synthesis (UDS) and lipid peroxidation (LPO) were measured in human peripheral lymphocytes from healthy volunteers. These processes were induced by the catalytic system Fe2+-sodium ascorbate. The degree of induced LPO was measured spectrophotometrically by the thiobarbituric acid assay. UDS was detected by scintillometric measurement of the incorporation of 3H-thymidine into DNA. The protective action by fat-soluble vitamin E (D,L-alpha-tocopherol) and the artificial antioxidant pyritinol on UDS and LPO was also investigated. The system Fe2+ (2 mumole/l)-sodium ascorbate (30 mumole/l) increased the LPO level in healthy volunteers approximately 2.5 times and the incorporation of 3H-thymidine by 60-70%. alpha-Tocopherol (0.2 mmole/l) very efficiently suppressed LPO processes (p less than 0.01) and the oxidative damage of DNA measured as UDS was also significantly diminished (p less than 0.05). Pyritinol had no effect on LPO and UDS under our experimental conditions.

System for the evaluation of the risk from chemical mutagens for man: basic principles and practical recommendations

A testing system is recommended that permits (1) reduction in cost and time requirements, (2) analysis of gene and chromosome mutations in germ and somatic cells, (3) evaluation of mutagenic effects of a chemical substance and its metabolites, (4) guarantee of the minimal variability between separate experiments and (5) evaluation of the dose--effect relationship. The testing scheme has two parts, a screening system and a complete test system. The screening system consists of two tests: (a) test on microorganisms with a metabolic activation in vitro (or test on Drosophila) and (b) cytogenetic analysis of mammalian bone marrow. The complete test system includes 4 tests: (a) test on microorganisms with a metabolic activation in vitro and in vivo (or test on Drosophila), (b) dominant-lethal test on mammals, (c) cytogenetic analysis of mammalian bone marrow and (d) cytogenetic analysis of the culture of human lymphocytes. The decision whether the selected chemical substance is to be tested according to the screening or complete test system is based on: its occurrence in the population, its economic (or medical) significance, and on information concerning its mutagenic, carcinogenic or teratogenic effects. The group of chemicals to be tested according to the screening system involves: industrial chemicals, organophosphate insecticides, drugs used by a limited group of patients. The group of chemicals to be tested according to the complete test system consists of pesticides, food additives, drugs in general use as well as chemicals of the former group, if at least one of the screening system tests detected some genetic effect. Genetic risk estimation should be governed by the following considerations. A positive effect identified in any test of the testing system must have a direct bearing on man. Quantitative evaluation of mutagenic risk from a chemical substance can be determined by the increased level of spontaneous mutations in the most sensitive test on the basis of an average dose of, and exposure to, the given chemical substance in the human population. Chemicals showing a mutagenic activity in any of recommended tests are subject to the quantitative evaluation, they are usually widespread and because of their social or economic value they cannot be replaced or excluded. Genetic aspects require that any substance with a mutagenic activity be considered dangerous and its use should be prohibited or it should be replaced by another non-mutagenic chemical, or at least the contact with it should be limited to persons of non-reproductive age. From the hygienic aspect it is recommended, as a temporary measure, to evaluate a chemical mutagen and to prohibit or limit its use if its average population dose produces a 0.1% or greater increase in the spontaneous level of mutations.