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H Greim

Publications and source records attributed to H Greim.

At least 19 recordsLinked to original sources
PubMed2001

Classification of carcinogenic chemicals in the work area by the German MAK Commission: current examples for the new categories.

The German Commission for the Investigation of Health Hazards of Chemical Compounds in the Work Area (MAK Commission) introduced an extended classification scheme in 1998. In addition to the traditional three categories still used to date, now called: Category 1 (human carcinogen); Category 2 (animal carcinogen); and Category 3 (suspected carcinogen), two new Categories (4 and 5) were added. Classification of substances into the new Categories 4 and 5 is based on the knowledge of mode of action and the potency of carcinogens. The essential feature of substances classified in the new Categories 4 and 5 is that exposure to these chemicals does not contribute significantly to the risk of cancer to man, provided that an appropriate exposure limit (MAK value) is observed. Chemicals known to act typically by non-genotoxic mechanisms are classified in Category 4. Genotoxic chemicals for which low carcinogenic potency can be assessed on the basis of dose-response relationships and toxicokinetics are classified in Category 5. Since the use of this scheme for 3 years, various chemicals have been classified in one of the new categories. However, in several cases data to sufficiently substantiate a MAK value are missing. Such substances are now classified in a subcategory of Category 3, called Category 3 A, which indicates that further data are required for final classification. Examples are given for classification of dichloromethane into Category 3 A, chloroform and sulfuric acid into Category 4 and ethanol into Category 5.

Animals↗
PubMed2001

Endpoints and surrogates for use in population studies in toxicology.

Risk characterisation of human exposure to chemicals requires information on the intrinsic toxic (hazardous) properties of the chemical, dose response of effects for the critical endpoints and exposure of the population. Information on hazardous properties, including data on mechanism and toxicokinetics, is necessary to define the critical endpoints and the relevant parameters to assess internal exposure and its relation to external exposure. Consequently the design of population studies to evaluate toxic effects or to monitor exposed cohorts must consider the critical endpoints of toxic effects and exposure. External exposure is determined by chemical analysis of the chemicals in food, water or air. The more relevant internal exposure is assessed by analysis of the chemical or its metabolites in body fluids and, if appropriate, by protein- or DNA-adducts. Effects are monitored by determining the relevant organ-specific parameters. In the case of genotoxic agents, effect biomonitoring parameters, like cytogenetic effects in peripheral blood cells or DNA strand breaks, are applied. Genotyping to detect deficiencies in the expression of enzymes, e.g. those involved in metabolic activation or inactivation, may explain interindividual differences in susceptibility. Overall prospective population studies allow exposure monitoring and risk assessment of human exposure only when such parameters are included.

DNA Adducts↗
PubMed2001

Use of covalent binding in risk assessment.

Risk characterization comprises hazard identification describing the intrinsic toxic potential of a chemical, toxicokinetics, as well as the toxic mechanisms, information about dose response and exposure assessment. Compounds that induce reversible effects, which are repaired during and after exposure, are considered thresholded and allow definition of a NOEL. If damage is not repaired, the effect persists and accumulates upon repeated exposure. In such cases a NOEL cannot be determined. Biological reactive intermediates of chemicals have the potential to bind covalently to cellular macromolecules like proteins and DNA. Such interaction is not repaired completely and may persist. Thus, data on covalent binding (CB) are of qualitative and quantitative significance in the risk assessment process. Qualitatively, CB, especially with DNA and in correlation with this to proteins, is indicative for an irreversible and non-thresholded mutagenic and carcinogenic effect. Absence or presence of CB assists to differentiate between primarily genotoxic and thresholded non-genotoxic carcinogens. Quantitatively, CB is used to understand internal exposure and target dose, which is a prerequisite for species-species extrapolation, and to justify extrapolation from high dose to low dose. The reactive intermediates of ethylene, propylene and styrene have been determined in rodents and humans and modeled to predict dose responses of internal exposure. It is described in this communication that such information, together with other parameters like cell proliferation as a result of cytotoxicity, is the basis for quantitative risk assessment of human exposure to these compounds.

Animals↗
PubMed2000

Steady-state transfer and depletion kinetics of mercury from amalgam fillings.

In 29 volunteers with a low amalgam load, the number of amalgam-covered tooth surfaces and the occlusal area of the fillings were determined. Before and at select times after removal of all amalgams, concentrations of total mercury were measured by cold-vapor atomic absorption in plasma and erythrocytes as well as in urine together with the excretion rate. Absorbed daily doses were estimated from intraoral Hg emission by two separate methods. The transfer of Hg from the fillings via the oral cavity and blood to urinary excretion was evaluated according to the most representative combination of parameters. This consisted of occlusal area (1), absorbed dose (2), Hg concentration in plasma (3) and urinary excretion (4). Pairwise correlation coefficients were 0.49 for parameters 1 vs. 2, and 0.75 each for parameters 2 vs. 3 and 3 vs. 4. Within 9 days after removal of the fillings, a transient increase in Hg levels was observed in plasma only; in the group without a rubber dam, concentrations increased significantly above pre-removal values at days 1 and 3, whereas they decreased significantly below pre-removal values at day 30 in the rubber-dam group and at day 100 in both groups. Excretion rates decreased significantly at day 100 in the protected group. Peak plasma-Hg was 0.6 ng/ml on average at day 1 and decreased with halftimes of 3 and 43 days in subjects protected by a rubber dam. The results indicated that concentrations of total mercury in plasma responded rapidly to changes in the amalgam status and reflected the actual absorption most reliably. Notably, plasma-Hg levels were sensitive enough to detect a transient attenuation of the additional exposure after using a rubber dam during the removal of only a few fillings. However, being small in magnitude and lasting 100 days at best, the rubber-dam effect had minor toxicological relevance.

Adult↗
PubMed2000

Internal biokinetic behaviour of molybdenum in humans studied with stable isotopes as tracers.

Although molybdenum is considered to be an essential trace metal for humans, the knowledge about its metabolism is rather limited. The present study was aimed at the assessment of biokinetics following intravenous injection of trace amounts of 95Mo or 96Mo into five healthy volunteers. In a total of 11 investigations, the plasma clearance up to eight hours and the urinary excretion for at least three days after the injection were evaluated. The tracer concentrations were determined by proton nuclear activation analysis in blood plasma and by thermal ionization mass spectrometry in urine samples respectively. In all subjects, the plasma clearance is much faster than expected from the literature. The data obtained for the plasma clearance of the tracer can reasonably be fitted by a two exponential equation. The half times of the fast component range between 4 and 70 minutes and for the slow component between 3 and 30 hours. The urinary excretion of the injected tracer seems also to be faster than expected and the fractions lost are higher for larger doses administered. For the smallest dose given, 34% of the injected tracer were excreted within one day whereas for the four times larger dose about 60% were lost. These findings on urinary excretion are in agreement with recently published results.

Adult↗
PubMed1999

The K-region trans-8,9-diol does not significantly contribute as an intermediate in the metabolic activation of dibenzo[a,l]pyrene to DNA-binding metabolites by human cytochrome P450 1A1 or 1B1.

Metabolic activation of the K-region trans-8,9-diol of the highly carcinogenic hexacyclic aromatic hydrocarbon dibenzo[a,l]pyrene (DB[a,l]P) by human cytochrome P-450 (P450) 1A1 and 1B1 was investigated in Chinese hamster V79 cell lines expressing human P450 1A1 or 1B1. P450 1A1 and 1B1 are the major P450s involved in metabolic activation of polycyclic aromatic hydrocarbons in human cells. The major DNA adducts formed by metabolism of DB[a,l]P in cultures expressing P450 1A1 or 1B1 resulted mainly from the fjord region (-)-anti-DB[a,l]P-11,12-diol 13,14-epoxide [(-)-anti-DB[a,l]PDE] and, to a lesser extent, (+)-syn-DB[a,l]PDE. In V79 cells expressing human P450 1A1, high amounts of as yet unidentified highly polar DNA adducts are formed in addition to the DNA adducts derived from DB[a,l]PDEs. Human P450 1A1 has been found to metabolize DB[a,l]P on its K-region to the trans-8,9-diol, and it has been proposed that the DNA binding of the parent compound in P450 1A1-expressing tissues may be partially mediated by activation of the K-region trans-8,9-diol to form bis-diol epoxides. V79 cells expressing human P450 1A1 or 1B1 formed only low amounts of DNA adducts after treatment with high doses of the K-region trans-8,9-diol. None of the adducts formed were identical to the main adducts formed in the same cell lines by metabolic activation of DB[a,l]P or (-)-DB[a,l]P-trans-11,12-diol. These results demonstrate that the K-region trans-8,9-diol does not significantly contribute to the genotoxicity of the very potent carcinogen DB[a,l]P in human cells or tissues expressing P450 1A1 or 1B1.

Animals↗
PubMed1999

Metabolic activation of dibenzo[a,l]pyrene by human cytochrome P450 1A1 and P450 1B1 expressed in V79 Chinese hamster cells.

Metabolic activation of the strongly carcinogenic polycyclic aromatic hydrocarbon (PAH) dibenzo[a,l]pyrene (DB[a,l]P) and its trans-8,9-dihydrodiol (trans-8,9-diol) catalyzed by human cytochromes P450 (P450) 1A1 and 1B1 was investigated. DNA binding of DB[a,l]P in mammalian cell lines has previously been shown to be preferentially mediated by fjord region DB[a,l]P-11,12-dihydrodiol 13,14-epoxides (DB[a,l]PDE). In order to elucidate different capabilities of both P450 enzymes for metabolic activation of DB[a, l]P V79 Chinese hamster cells, stably expressing human P450s 1A1 or 1B1 have been exposed to the parent PAH or its racemic trans-8, 9-diol. For this purpose, synthesis and spectroscopic characterization of the trans-DB[a,l]P-8,9-diol and its individual enantiomers have been achieved. Both human P450-expressing cell lines were capable of transforming DB[a,l]P to its fjord region DB[a, l]PDE, but the extent of metabolism to DB[a,l]PDE catalyzed by human P450 1B1 was higher compared to human P450 1A1 at all times measured. On the other hand, cytotoxicity studies performed with the same incubation systems emerged stronger effects by DB[a,l]P and its enantiomeric trans-11,12-diols in human P450 1A1-expressing cells. Both human P450 enzymes stereospecifically catalyzed the formation of the (-)-DB[a,l]P-11,12-diol with R,R-configuration, whereas only the human P450 1A1-expressing cells form small amounts of the K-region trans-8,9-diol with high excess of the (+)-(8R, 9R)-enantiomer. Application of trans-DB[a,l]P-8,9-diol in metabolism studies revealed that this compound is converted by human P450s 1A1 and 1B1 to several diol phenols and bis-diols. However, and even at concentrations as high as 10 microM, in both cell lines the trans-DB[a,l]P-8,9-diol showed no cytotoxicity at all, suggesting that an activation of DB[a,l]P via further oxidation of the K-region trans-8,9-diol plays a minor role.

Animals↗
PubMed1999

Effect of rubber dam on mercury exposure during amalgam removal.

It was the aim of this investigation to treat 20 volunteers with maximally 5 amalgam fillings by the same comprehensive protocol in which all removals with (n = 8) and without (n = 12) rubber dam had been performed within a few months. Nine amalgam-related parameters indicated a close matching of both groups before removal. In the group without rubber dam, mercury (Hg) levels in plasma increased significantly above preremoval values at days 1 and 3 after removal; they decreased significantly below preremoval values at day 30 in the rubber-dam group and at day 100 in both groups. Excretion rates did not increase significantly in either group, but decreased significantly at day 100 in the protected group. Peak plasma-Hg was 0.6 ng/mL on average at day one and decreased with halftimes of 3 and 43 d in subjects protected by rubber dam. The results indicated that concentrations of total mercury in plasma responded rapidly to changes in the amalgam status and reflected the actual absorption most reliably. Notably, plasma-Hg levels were sensitive enough to detect a transient attenuation of the additional exposure by using rubber dam during the removal of only a few fillings. However, being small in magnitude and lasting 100 d at best, the rubber-dam effect had minor toxicological relevance.

Absorption↗
PubMed1999

The level of DNA modification by (+)-syn-(11S,12R,13S,14R)- and (-)-anti-(11R,12S,13S,14R)-dihydrodiol epoxides of dibenzo[a,l]pyrene determined the effect on the proteins p53 and p21WAF1 in the human mammary carcinoma cell line MCF-7.

The polycyclic aromatic hydrocarbon (PAH) dibenzo[a,l]pyrene (DB[a,l]P), the most carcinogenic PAH tested in rodent bioassays, exerts its pathobiological activity via metabolic formation of electrophilically reactive DNA-binding fjord region (+)-syn-(11S,12R,13S,14R)- or (-)-anti-(11R,12S,13S,14R)-DB[a,l]P-dihydrodiol epoxides (DB[a,l]-PDEs). DB[a,l]P is metabolized to these DB[a,l]PDEs which bind to DNA in human mammary carcinoma MCF-7 cells. The molecular response of MCF-7 cells to DNA damage caused by DB[a,l]PDEs was investigated by analyzing effects on the expression of the tumor suppressor protein p53 and one of its target gene products, the cyclin-dependent kinase inhibitor p21WAF1. Treatment of MCF-7 cells with (+)-syn- and (-)-anti-DB[a,l]PDE at a concentration range of 0.001-0.1 microM resulted in DB[a,l]PDE-DNA adduct levels between 2 and 30, and 3 and 80 pmol/mg DNA, respectively, 8 h after exposure. (-)-anti-DB[a,l]PDE exhibited a higher binding efficiency that correlated with a significantly stronger p53 response at low concentrations of the dihydrodiol epoxides. The level of p53 increased by 6-8 h after treatment. The p21WAF1 protein amount exceeded control levels by 12 h and remained elevated for 96 h. At a dose of 0.01 microM (+)-syn-DB[a,l]PDE, an increase in p21WAF1 was observed in the absence of a detectable change in p53 levels. The results indicate that the increase in p53 induced by DB[a,l]PDEs in MCF-7 cells requires an adduct level of approximately 15 pmot/mg DNA and suggest that the level of adducts rather than the specific structure of the DB[a,l]PDE-DNA adduct formed triggers the p53 response. The PAH-DNA adduct level formed may determine whether p53 and p21VAF1 pathways respond, resulting in cell-cycle arrest, or fail to respond and increase the risk of mutation induction by these DNA lesions.

Benzopyrenes↗
PubMed1998

Systemic transfer of mercury from amalgam fillings before and after cessation of emission.

In 29 volunteers with a low amalgam load, the number of amalgam-covered tooth surfaces and the occlusal area of the fillings were determined. Concentrations of total mercury were measured in plasma and erythrocytes as well as in urine together with the excretion rate. Absorbed daily doses were estimated from intraoral Hg emission by two separate methods. The transfer of Hg from the fillings via the oral cavity and blood to urinary excretion was evaluated according to the most representative combination of parameters. This consisted of urinary excretion (1), Hg concentration in plasma (2), absorbed dose (3), and occlusal area (4). Pairwise correlation coefficients were 0.75 for parameters 1 vs 2 and 2 vs 3 and 0.49 for parameters 3 vs 4. Within 9 days after removal of the fillings, a transient increase was observed in plasma Hg levels only. This was reduced in those volunteers to whom a rubber dam had been applied during removal. Peak plasma Hg was 0.6 ng/ml on average and decreased with halftimes between 5 and 13 days. A significant decrease in Hg excretion was noted not before 100 days after removal. Being relatively insensitive to dietary mercury, the determination of total mercury in plasma and of its urinary excretion rate appears, under practical aspects, most suitable for the investigation of Hg uptake from amalgam.

Adult↗
PubMed1998

Changes in the classification of carcinogenic chemicals in the work area. Section III of the German List of MAK and BAT Values.

Carcinogenic chemicals in the work area are currently classified into three categories in section III of the German List of MAK and BAT Values (list of values on maximum workplace concentrations and biological tolerance for occupational exposures). This classification is based on qualitative criteria and reflects essentially the weight of evidence available for judging the carcinogenic potential of the chemicals. It is proposed that these categories - IIIA1, IIIA2, IIIB - be retained as Categories 1, 2, and 3, to correspond with European Union regulations. On the basis of our advancing knowledge of reaction mechanisms and the potency of carcinogens, these three categories are supplemented with two additional categories. The essential feature of substances classified in the new categories is that exposure to these chemicals does not contribute significantly to risk of cancer to man, provided that an appropriate exposure limit (MAK value) is observed. Chemicals known to act typically by nongenotoxic mechanisms and for which information is available that allows evaluation of the effects of low-dose exposures, are classified in Category 4. Genotoxic chemicals for which low carcinogenic potency can be expected on the basis of dose-response relationships and toxicokinetics, and for which risk at low doses can be assessed are classified in Category 5. The basis for a better differentiation of carcinogens is discussed, the new categories are defined, and possible criteria for classification are described. Examples for Category 4 (1,4-dioxane) and Category 5 (styrene) are presented.

Animals↗
PubMed1998

Changes in the classification of carcinogenic chemicals in the work area. (Section III of the German List of MAK and BAT values).

Carcinogenic chemicals in the work area were previously classified into three categories in section III of the German List of MAK and BAT values (the list of values on maximum workplace concentrations and biological tolerance for occupational exposures). This classification was based on qualitative criteria and reflected essentially the weight of evidence available for judging the carcinogenic potential of the chemicals. In the new classification scheme the former sections IIIA1, IIIA2, and IIIB are retained as categories 1, 2, and 3, to correspond with European Union regulations. On the basis of our advancing knowledge of reaction mechanisms and the potency of carcinogens, these three categories are supplemented with two additional categories. The essential feature of substances classified in the new categories is that exposure to these chemicals does not contribute significantly to the risk of cancer to man, provided that an appropriate exposure limit (MAK value) is observed. Chemicals known to act typically by non-genotoxic mechanisms, and for which information is available that allows evaluation of the effects of low-dose exposures, are classified in category 4. Genotoxic chemicals for which low carcinogenic potency can be expected on the basis of dose/response relationships and toxicokinetics and for which risk at low doses can be assessed are classified in category 5. The basis for a better differentiation of carcinogens is discussed, the new categories are defined, and possible criteria for classification are described. Examples for category 4 (1,4-dioxane) and category 5 (styrene) are presented.

Animals↗
PubMed1998

Toxicity of aliphatic amines: structure-activity relationship.

SARs may enable the evaluation of the toxic potential of chemicals by drawing conclusions from available data on structurally-related chemicals, thus reducing the need for further testing. The Advisory Committee on Existing Chemicals of Environmental Relevance (BUA) [1,2] of the German Chemical Society (Gesellschaft Deutscher Chemiker [GDCh]) has compiled data on the toxicity and ecological impact for several groups of chemicals [3, 4]. In the present review, some common toxicological properties for aliphatic amines were revealed after evaluation and comparison of the toxicity data.

Administration, Oral↗
PubMed1998

Stable expression of human cytochrome P450 1B1 in V79 Chinese hamster cells and metabolically catalyzed DNA adduct formation of dibenzo[a,l]pyrene.

Chinese hamster V79 cell lines were constructed for stable expression of human cytochrome P450 1B1 (P450 1B1) in order to study its role in the metabolic activation of chemicals and toxicological consequences. The new V79 cell lines were applied to studies on DNA adduct formation of the polycyclic aromatic hydrocarbon (PAH) dibenzo[a,l]pyrene (DB[a,l]P). This compound has been found to be an environmental pollutant, and in rodent bioassays it is the most carcinogenic PAH yet discovered. Activation of DB[a,l]P in various metabolizing systems occurs via fjord region DB[a,l]P-11, 12-dihydrodiol 13,14-epoxides (DB[a,l]PDE): we found that DB[a,l]P is stereoselectively metabolized in human mammary carcinoma MCF-7 cells to the (-)-anti- and (+)-syn-DB[a,l]PDE which both bind extensively to cellular DNA. To follow up this study and to relate specific DNA adducts to activation by individual P450 isoforms, the newly established V79 cells stably expressing human P450 1B1 were compared with those expressing human P450 1A1. DNA adduct formation in both V79 cell lines differed distinctively after incubation with DB[a,l]P or its enantiomeric 11,12-dihydrodiols. Human P450 1A1 catalyzed the formation of DB[a,l]PDE-DNA adducts as well as several highly polar DNA adducts as yet unidentified. The proportion of these highly polar adducts to DB[a,l]PDE adducts was dependent upon both the concentration of DB[a,l]P and the time of exposure. In contrast, V79 cells stably expressing human P450 1B1 generated exclusively DB[a,l]PDE-DNA adducts. Differences in the total level of DNA binding were also observed. Exposure to 0.1 microM DB[a,l]P for 6 h caused a significantly higher level of DNA adducts in V79 cells stably expressing human P450 1B1 (370 pmol/mg of DNA) compared to those with human P450 1A1 (35 pmol/mg of DNA). A 4-fold higher extent of DNA binding was catalyzed by human P450 1B1 (506 pmol/mg of DNA) compared to human P450 1A1 (130 pmol/mg of DNA) 6 h after treatment with 0.05 microM (-)-(11R,12R)-dihydrodiol. In cells stably expressing human P450 1B1 the DNA adducts were derived exclusively from the (-)-anti-DB[a,l]PDE. These results indicate that human P450 1B1 and P450 1A1 differ in their regio- and stereochemical selectivity of activation of DB[a,l]P with P450 1B1 forming a higher proportion of the highly carcinogenic (-)-anti-(11R, 12S,13S,14R)-DB[a,l]PDE metabolite.

Animals↗