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Biomedical subjects

B D Beck

Publications and source records attributed to B D Beck.

At least 19 recordsLinked to original sources
PubMed2006

An evaluation of the US Environmental Protection Agency definition of a risk assessment.

A full presentation of relevant information, including both non-adverse and beneficial effects, of chemicals is important to developing sound and balanced risk assessments. Such considerations are not new. For example, the American Thoracic Society has developed criteria for defining adverse and non-adverse pulmonary effects. Failing to allow risk assessors to even consider non-adverse and beneficial effects will discourage the use of information from developing technologies, such as genomics, and from new understandings of dose-response relationships, as reflected in the hormetic model. Failing to provide such information to risk managers potentially provides a biased perspective on risk.

Dose-Response Relationship, Drug↗
PubMed2005

Risk evaluation of occupational exposure to methylene dianiline and toluene diamine in polyurethane foam.

Methylene diphenylisocyanate (MDI) and toluene diisocyanate (TDI) are widely used in industry to produce polyurethane foam products. Small amounts of methylenedianiline (MDA) and toluene diamine (TDA) are released during MDI and TDI polymerization and may be present in newly finished polyurethane foam parts. MDA and TDA concentrations in foam decline exponentially within several hours of demolding. MDA and the 2,4-isomer of TDA are known animal carcinogens and, in addition, have significant non-carcinogenic health effects. Our goal was to determine whether worker exposure to MDA or TDA in freshly produced polyurethane foams was associated with unacceptable health risks. Sampling and analysis of the fresh foam indicated that MDA and TDA concentrations varied considerably among products, but concentrations in all materials evaluated declined rapidly over time. We found that, under a worst-case exposure scenario, cancer risks from TDA exposure were approximately 5 x 10(-6), whereas cancer risks from MDA exposure resulted in a tumorigenic margin of exposure (MOE) of 85 000. Non-cancer chronic hazard indices were well below 1.0. Therefore, the potential cancer and non-cancer health risks from MDA or TDA exposure to newly manufactured foam parts appear to fall well within acceptable health risk criteria.

Aniline Compounds↗
PubMed2004

Interspecies differences in susceptibility to perturbation of thyroid homeostasis: a case study with perchlorate.

Despite many physiological similarities, humans and rats exhibit notably different susceptibilities to thyroid perturbation. Considerable research has recently been conducted on the thyroid-active chemical perchlorate, a chemical of emerging environmental and regulatory interest. While the data indicate humans and rats exhibit similar dose-response relationships in terms of acute inhibition of thyroidal iodide uptake, the two species appear to exhibit notable differences in terms of thyroid hormone response, the toxicologically significant consequence of iodide uptake inhibition. We analyzed dose-response data for changes in serum T(3), T(4), and TSH levels from studies in humans, rats, mice, and rabbits. We found that thyroid homeostasis in the rat appears to be strikingly more sensitive to perchlorate than any of the other species. Rats exhibited an increase in serum TSH at 0.1mg/kg-day whereas other species remained unresponsive even at doses of 10mg/kg-day. Less pronounced but consistent effects were seen with serum T(3) and T(4). These cross-species comparisons provide strong evidence that data obtained from rat studies should be critically evaluated for their relevance to humans. If rat data are used to develop toxicity criteria for perchlorate, we propose that this is an instance where an inter-species uncertainty factor less than one is supportable. DISCLOSURE STATEMENT: One of the authors (BDB) has been hired by Lockheed Martin Corporation as an expert in litigation involving perchlorate. A portion of the initial research presented in this paper was conducted in conjunction with her role in that matter.

Animals↗
PubMed2002

Effect of BRCA mutations on the length of survival in epithelial ovarian tumors.

PURPOSE: To study the role of BRCA mutations in ovarian cancer survival. PATIENTS AND METHODS: Blood samples and specimens of ovarian tumors (whenever blood samples were not available) at the time of the primary surgery were obtained in the course of a nationwide case-control study of women with ovarian cancer in Israel. The three common BRCA mutations in Israel (185delAG, 5382insC, and 6174delT) were analyzed with a multiplex polymerase chain reaction to amplify the exons containing the three mutations using fluor-labeled primers in a single reaction. Because each mutation is a small insertion or deletion, they can be detected as length polymorphisms. Patients were followed for up to 5 years (range, 20 to 64 months). Statistical analysis was performed using the Kaplan-Meier method and the log-rank test. Stepwise Cox regression analysis was used for determination of independent prognostic factors. RESULTS: This report is based on 896 blood or tumor specimens analyzed for the presence of the BRCA mutations. Of these, 234 women (26.1%) were found to be positive. A significant difference in survival pattern was found between BRCA1/BRCA2 carriers and noncarriers among the women with invasive ovarian cancer (median survival, 53.4 months v. 37.8 months; 3-year survival, 65.8% v. 51.9%, respectively). These differences were independent of age at diagnosis or stage of the disease. CONCLUSION: Our data indicate that the survival of patients with ovarian cancer is affected by BRCA germline mutation, at least in the early years after diagnosis.

Case-Control Studies↗
PubMed2002

Systemic uptake of inhaled arsenic in rabbits.

Human occupational exposure to sufficiently high levels of arsenic in air has been associated with lung cancer, but generally not other types of cancer. Thus, a better understanding of the relationship between airborne arsenic exposures and systemic uptake is essential. In this study, rabbits were exposed to one of four levels of arsenic trioxide in air for 8 h/day, 7 days/week, for 8 weeks (0.05, 0.1, 0.22, or 1.1 mg/m3). Plasma levels of inorganic arsenic, monomethylarsonic acid (MMA), and dimethylarsinic acid (DMA) were measured following the last exposure. Although there was a dose-related increase in plasma levels of methylated arsenic metabolites, statistically significant increases in mean inorganic arsenic levels in plasma were observed only in male rabbits exposed to 0.22 mg/m3, and in both males and females exposed to 1.1 mg/m3. Mean inorganic arsenic levels in plasma in males and females exposed to 0.05 and 0.1 mg/m3, and females exposed to 0.22 mg/m3, were not significantly elevated compared to controls. These results suggest that arsenic inhalation has a negligible impact on body burden of inorganic arsenic until air levels are significantly elevated. Based on plasma measurements of inorganic arsenic, the two lowest exposure levels in this study (0.05 and 0.1 mg/m3) are indistinguishable from background.

Administration, Inhalation↗
PubMed2001

The development of a stochastic physiologically-based pharmacokinetic model for lead.

This presentation describes the development of a prototype Monte Carlo module for the physiologically-based pharmacokinetic (PBPK) model for lead, created by Dr Ellen O'Flaherty. The module uses distributions for the following: exposure parameters (soil and dust concentrations, daily soil and ingestion rate, water lead concentration, water ingestion rate, air lead concentration, inhalation rate and dietary lead intake); absoption parameters; and key pharmacokinetic parameters (red blood binding capacity and half saturation concentration). Distributions can be specified as time-invariant or can change with age. Monte Carlo model predicted blood levels were calibrated to empirically measured blood lead levels for children living in Midvale, Utah (a milling/smelting community). The calibrated model was then evaluated using blood lead data from Palmerton, Pennsylvania (a town with a former smelter) and Sandy, Utah, (a town with a former smelter and slag piles). Our initial evaluation using distributions for exposure parameters showed that the model accurately predicted geometric (GM) blood lead levels of Palmerton and Sandy and slightly over predicted the GSD. Consideration of uncertainty in red blood cell parameters substantially inflated the GM. Future model development needs to address the correlation among parameters and the use of parameters for long-term exposure derived from short-term studies.

Dust↗
PubMed2001

Procedures for health risk assessment in Europe.

This report compares cancer classification systems, health risk assessment approaches, and procedures used for establishing occupational exposure limits (OELs), in various European countries and scientific organizations. The objectives were to highlight and compare key aspects of these processes and to identify the basis for differences in cancer classifications and OELs between various scientific organizations and countries. Differences in cancer classification exist in part due to differences in the ultimate purpose of classification and to the relative importance of different types of data (i.e., animal vs human data, mechanistic data, and data from benign vs malignant tumors). In general, the groups surveyed tend to agree on classification of chemicals with good evidence of carcinogenicity in humans, and agree less on classification of chemicals with positive evidence in animals and inadequate or limited evidence in humans. Most entities surveyed distinguish between genotoxic and nongenotoxic chemicals when conducting risk assessments. Although the risk assessment approach used for nongenotoxic chemicals is fairly similar among groups, risk assessment approaches for genotoxic carcinogens vary widely. In addition to risk assessment approaches, other factors which can affect OELs include selection of the critical effect, use of health-based vs technology-based exposure limits, and consideration of technological feasibility and socioeconomic factors.

Animals↗
PubMed2001

Translocation of MRE11 from the nucleus to the cytoplasm as a mechanism of radiosensitization by heat.

Zhu, W-G., Seno, J. D., Beck, B. D. and Dynlacht, J. R. Translocation of MRE11 from the Nucleus to the Cytoplasm as a Mechanism of Radiosensitization by Heat. Radiat. Res. 156, 95-102 (2001).Hyperthermia sensitizes mammalian cells to ionizing radiation, presumably by inhibiting the repair of radiation-induced double-strand breaks (DSBs). However, the mechanism by which heat inhibits DSB repair is unclear. The nuclear protein MRE11 is a component of a multi-protein complex involved in nonhomologous end joining (NHEJ) of radiation-induced DSBs. Using one-dimensional sodium dodecylsulfate polyacrylamide gel electrophoresis and Western blotting, we found that MRE11 is translocated from the nucleus to the cytoplasm when human U-1 melanoma or HeLa cells are heated for 15 min at 45.5 degrees C or when cells are heated after irradiation with 12 Gy of X rays. No such translocation is observed in unheated irradiated cells. The kinetics of migration of MRE11 to the cytoplasm was dependent upon whether the heated cells were irradiated, while the magnitude of redistribution of MRE11 was dependent upon post-treatment incubation time at 37 degrees C. Cytoplasmic MRE11 content reached a maximum 2-4 h after heating; the increase was not due to new protein synthesis. Partial recovery of nuclear MRE11 content was observed when heated cells or heated irradiated cells were incubated for up to 7 h at 37 degrees C after treatment. Western blotting results showing translocation of MRE11 from the nucleus to the cytoplasm after heating and irradiation were confirmed using confocal microscopy and immunofluorescence staining of fixed cells. Our data suggest that radiosensitization by heat may be caused, at least in part, by translocation of the DNA repair protein MRE11 from the nucleus to the cytoplasm.

Active Transport, Cell Nucleus↗
PubMed2001

Heat-induced aggregation of XRCC5 (Ku80) in nontolerant and thermotolerant cells.

XRCC5 (also known as Ku80) is a component of the DNA-dependent protein kinase (DNA-PK), existing as a heterodimer with G22P1 (also known as Ku70). DNA-PK is involved in the nonhomologous end-joining (NHEJ) pathway of DNA double-strand break (DSB) repair, and kinase activity is dependent upon interaction of the Ku subunits with the resultant DNA ends. Nuclear XRCC5 is normally extractable with non-ionic detergent; it is found in the soluble cytoplasmic fraction after nuclear isolation with Triton X-100. In this study, we found that heating at 45.5 degrees C causes a decreased extractability of XRCC5 from the nuclei of human U-1 melanoma or HeLa cells. Such decreases in extractability are indicative of protein aggregation within nuclei. Recovery of extractability of XRCC5 to that of unheated control cells was observed after incubation at 37 degrees C after heat shock. The decrease in extractability and the kinetics of recovery were dependent on dose, although the decrease in extractability reached a plateau after heating for 15 min or more. Thermotolerant U-1 cells also showed decreased extractability of XRCC5, but to a lesser degree compared to nontolerant cells. When a comparable initial reduction of extractability of XRCC5 was induced in both thermotolerant and nontolerant cells, the kinetics of recovery was nearly identical. The kinetics of recovery of the extractability of XRCC5 was different from that of total nuclear protein in nontolerant cells; recovery of extractability of XRCC5 occurred faster initially and returned to the level in unheated cells faster than total nuclear protein. Similar results were obtained for thermotolerant cells, with differences between the initial recovery of the extractability of XRCC5 and total protein being particularly evident after longer heating times. Heat has been shown to inactivate XRCC5. We speculate that inactivation of XRCC5 after heat shock results from protein aggregation, and that changes in XRCC5 may, in part, lead to inhibition of DSB repair through inactivation of the NHEJ pathway.

Adaptation, Physiological↗
PubMed2000

Cognitive tests: interpretation for neurotoxicity? (Workshop summary).

The appropriate use and interpretation of cognitive tests presents important challenges to the toxicologist and to the risk assessor. For example, intelligence cannot be measured directly; rather intelligence is quantified indirectly by scoring responses (i.e., behaviors) to specific situations (problems). This workshop, "Cognitive Tests: Interpretation for Neurotoxicity?" provided an overview on the types of cognitive tests available and described approaches by which the validity of such tests can be assessed. Unlike many tools available to the toxicologist, cognitive tests have a particular advantage. Being noninvasive and species-neutral, the same test can be performed in different mammalian species. This enhances one's ability to assess the validity of test results. Criteria for test validity include comparable responses across species as well as similar disruption by the same neurotoxicant across species. Test batteries, such as the Operant Test Battery, have indicated remarkable similarity between monkeys and children with respect to performance of certain tasks involving, for example, short-term memory. Still, there is a need for caution in interpretation of such tests. In particular, cognitive tests, especially when performed in humans, are subject to confounding by a range of factors, including age, gender, and, in particular, education. Moreover, the ability of such tests to reflect intelligence must be considered. Certain aspects of intelligence, such as the ability to plan or carry out specific tasks, are not well reflected by many of the standard tests of cognition. Nonetheless, although still under development, cognitive tests do hold promise for reliably predicting neurotoxicity in humans.

Animals↗
PubMed1999

The enigma of arsenic carcinogenesis: role of metabolism.

Inorganic arsenic is considered a high-priority hazard, particularly because of its potential to be a human carcinogen. In exposed human populations, arsenic is associated with tumors of the lung, skin, bladder, and liver. While it is known to be a human carcinogen, carcinogenesis in laboratory animals by this metalloid has never been convincingly demonstrated. Therefore, no animal models exist for studying molecular mechanisms of arsenic carcinogenesis. The apparent human sensitivity, combined with our incomplete understanding about mechanisms of carcinogenic action, create important public health concerns and challenges in risk assessment, which could be met by understanding the role of metabolism in arsenic toxicity and carcinogenesis. This symposium summary covers three critical major areas involving arsenic metabolism: its biodiversity, the role of arsenic metabolism in molecular mechanisms of carcinogenesis, and the impact of arsenic metabolism on human risk assessment. In mammals, arsenic is metabolized to mono- and dimethylated species by methyltransferase enzymes in reactions that require S-adenosyl-methionine (SAM) as the methyl donating cofactor. A remarkable species diversity in arsenic methyltransferase activity may account for the wide variability in sensitivity of humans and animals to arsenic toxicity. Arsenic interferes with DNA methyltransferases, resulting in inactivation of tumor suppressor genes through DNA hypermethylation. Other studies suggest that arsenic-induced malignant transformation is linked to DNA hypomethylation subsequent to depletion of SAM, which results in aberrant gene activation, including oncogenes. Urinary profiles of arsenic metabolites may be a valuable tool for assessing human susceptibility to arsenic carcinogenesis. While controversial, the idea that unique arsenic metabolic properties may explain the apparent non-linear threshold response for arsenic carcinogenesis in humans. In order to address these outstanding issues, further efforts are required to identify an appropriate animal model to elucidate carcinogenic mechanisms of action, and to define dose-response relationships.

Animals↗
PubMed1997

Issues in setting health-based cleanup levels for arsenic in soil.

Health risk assessments often do not take into account the unique aspects of evaluating exposures to arsenic in soil. For example, risks from ingestion of arsenic in soil are often based on toxicity factors derived from studies of arsenic (soluble arsenate or arsenite) in drinking water. However, the toxicity of arsenic in drinking water cannot be directly extrapolated to toxicity of soil arsenic because of differences in chemical form, bioavailability, and excretion kinetics. Because of the differences between soil arsenic and water arsenic, we conclude that risks from arsenic in soil are lower than what would be calculated using default toxicity values for arsenic in drinking water. Site-specific risk assessments for arsenic in soil can be improved by characterizing the form of arsenic in soil, by conducting animal feeding or in vitro bioavailability studies using site soils, and by conducting studies to evaluate the relationship between urinary arsenic and soil arsenic levels. Such data could be used to more accurately measure the contribution that soil arsenic makes to total intake of arsenic. Available data suggest that arsenic usually makes a small contribution to this total.

Adult↗
PubMed1997

Life years lost at hazardous waste sites: remediation worker fatalities vs. cancer deaths to nearby residents.

We present a hypothetical case study using the Years of Potential Life Lost (YPLL) metric to compare cancer risks incurred by residents living near a Superfund site to occupational fatality risks incurred by workers employed in that site's remediation. Since cancer occurs late in life, and because we assume its mortality rate is 60%, each case results in 8.8 YPLL. Each occupational fatality, which typically occurs earlier in life, results in 38.1 YPLL. In our case study, the residential population of 5000 incurred 1.3 YPLL, compared to 5.7 YPLL incurred by the 500 workers. Several uncertain assumptions may influence our calculations; moreover, occupational risks may be viewed as more "voluntary" than risks incurred by residents. However, because the magnitude of the YPLL incurred by workers and residents may be comparable, risk managers should consider occupational risks when evaluating remedial alternatives.

Accidents, Occupational↗
PubMed1997

Inorganic arsenic: a need and an opportunity to improve risk assessment.

This paper presents views on the current status of (inorganic) arsenic risk assessment in the United States and recommends research needed to set standards for drinking water. The opinions are those of the Arsenic Task Force of the Society for Environmental Geochemistry and Health, which has met periodically since 1991 to study issues related to arsenic risk assessment and has held workshops and international conferences on arsenic. The topic of this paper is made timely by current scientific interest in exposure to and adverse health effects of arsenic in the United States and passage of the Safe Drinking Water Act Amendment of 1996, which has provisions for a research program on arsenic and a schedule mandating the EPA to revise the maximum contaminant level of arsenic in drinking water by the year 2001. Our central premise and recommendations are straightforward: the risk of adverse health effects associated with arsenic in drinking water is unknown for low arsenic concentrations found in the United States, such as at the current interim maximum contaminant level of 50 microg/l and below. Arsenic-related research should be directed at answering that question. New epidemiological studies are needed to provide data for reliable dose-response assessments of arsenic and for skin cancer, bladder cancer, or other endpoints to be used by the EPA for regulation. Further toxicological research, along with the observational data from epidemiology, is needed to determine if the dose-response relationship at low levels is more consistent with the current assumption of low-dose linearity or the existence of a practical threshold. Other recommendations include adding foodborne arsenic to the calculation of total arsenic intake, calculation of total arsenic intake, and encouraging cooperative research within the United States and between the United States and affected countries.

Arsenic↗
PubMed1996

Implications of arsenic genotoxicity for dose response of carcinogenic effects.

Epidemiological data relating arsenic ingestion and skin and internal cancers strongly suggest a sublinear or threshold relationship. Physiological saturation of methylation-based arsenic detoxification has been proposed as one explanation for a sublinear response. We have evaluated the molecular bases for sublinearity in light of new data and hypotheses regarding arsenic genotoxicity and chemical carcinogenesis. A review of the dose-response relationships observed in arsenic genotoxicity assays is presented. With the exception of sister chromatid exchanges, sublinear dose-response relationships for arsenic-induced chromosomal aberrations were observed repeatedly in different mammalian and human cell systems. Arsenic also enhanced the clastogenicity and mutagenicity of other DNA damaging agents with a sublinear dose response. Consistent with the dose response of arsenic-induced genetic alterations, arsenic also inhibited DNA ligases I and II, enzymes which play a role in DNA repair, with a sublinear dose response. In some cases, protective effects of relatively low exposures to arsenic have been observed, again consistent with sublinearity. We discuss recent theories on the mechanism of arsenic carcinogenicity and the potential implications for dose-response modeling and risk assessment. Overall, based on available arsenic genotoxicity data, we conclude that it is likely that arsenic indirectly induces genetic damage with a sublinear dose response in humans, thus providing a biological basis for a sublinear dose-response relationship for human cancer. Furthermore, these results suggest that linear dose-response modeling from populations experiencing high arsenic exposures is likely to overpredict cancer risks at relatively low arsenic levels.

Animals↗
PubMed1996

Chemistry, toxicology, and human health risk of cyanide compounds in soils at former manufactured gas plant sites.

Cyanide-containing wastes are commonly found in soils at former manufactured gas plant (MGP) sites, also known as town gas sites. The complex forms of cyanide are responsible for the blue-stained soils and rocks found at these sites. Most concentrations of cyanide at MGP sites are below 2000 ppm, although concentrations greater than 20,000 ppm have been observed. An understanding of the chemistry of the MGP cyanide-containing compounds, their fate, and transport as well as their toxicology is critical to accurately assessing potential human health risks from these compounds. In this paper, the authors demonstrate that the most prevalent types of cyanide compounds found at former MGP sites are the relatively nontoxic iron-complexed forms, such as ferric ferrocyanide, rather than the highly toxic free cyanide forms. Moreover, the chemical conditions at most former MGP sites limit the extent to which free cyanide may be released into air and water from complex cyanides. Using a screening analysis, the authors estimate potential risks from a multiroute exposure to complex and free cyanides in soil, air, and groundwater at former MGP sites and demonstrate that such risks are likely to be insignificant. Unfortunately, the lack of readily available measurement techniques to characterize cyanides in soil can result in erroneous conclusions about potential risks from cyanide compounds in soils at former MGP sites, particularly if health-based soil criteria for free cyanide (e.g., the Massachusetts Department of Environmental Protection criterion for free cyanide is 100 ppm (MA. DEP, 1995)) are applied. The authors recommend development of routine methods for field sampling and laboratory testing techniques to demonstrate that cyanides in soil at former MGP sites are predominated by iron-complexed species and that free cyanide is less than levels of concern.

Animals↗