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Biomedical subjects

E J Calabrese

Publications and source records attributed to E J Calabrese.

At least 19 recordsLinked to original sources

The Council for Health and Environmental Safety of Soils.

The Council for Health and Environmental Safety of Soils (CHESS) was organized in 1987 to develop a consensus soil risk assessment methodology to be used as a framework for establishing standards for soil contamination to protect the environment and public health. The wide range of contaminating substances of possible health concern in soil is affecting land use and development, causing excessive economic expenditures, and the regulatory approaches for control are disperse. The International Society of Regulatory Toxicology and Pharmacology agreed to sponsor the Council and through a Governing Board composed of experienced scientists from the federal government, state departments of public health and environmental protection, academia, and the private sector including industry and environmental organizations. The Board was created to support the goals of CHESS, its mode of operation, and to establish funding policies and directions. A technical council agreed to develop a peer-reviewed consensus methodology to assess public health risks from contaminated soil by technical committees composed of recognized experts in the area of soil contamination and other relevant disciplines. This methodology would then be made available to federal and state agencies, the private sector, and the scientific community at large. After extensive study, a final decision was made to develop a decision-tree framework to be used at the state and local levels for application to all types of soil contamination. Following extensive studies it was agreed the ubiquitous nature of petroleum contamination in soil has direct and immediate public health implications and CHESS therefore directed its first efforts to this area.(ABSTRACT TRUNCATED AT 250 WORDS)

Environmental Pollution

Does the animal-to-human uncertainty factor incorporate interspecies differences in surface area?

Risk assessment practices for noncarcinogens typically employ an uncertainty factor (UF) for animal-to-human extrapolation when defining acceptable levels for humans based on animal studies. EPA has interpreted the use of this factor as addressing interspecies differences due to dose normalization via surface area (exposure-dose relationships) and to innate differences in species susceptibility (dose-response relationships). Thus EPA has concluded that dose normalization via surface area is not necessary when using animal studies to define acceptable levels for noncarcinogens for humans. In this report we challenge this position on both theoretical and practical grounds. It is recommended that the UF for animal-to-human extrapolation for noncarcinogens in the risk assessment process and the technique for dose normalization be considered distinctly.

Animals

Distinguishing outdoor soil ingestion from indoor dust ingestion in a soil pica child.

This paper represents the first quantitative attempt to distinguish the amount of outdoor soil ingestion from indoor dust ingestion in a soil pica child. Based on a methodology using a comparison of differential element ratios it is estimated that the predominant proportion of the fecal tracers were from outdoor soil and not indoor dust origin. The methodology employed can be utilized on a broader scale to assess the relative amounts of soil and dust consumed by individuals.

Child

Effects of joint exposures to selected peroxisome proliferators on hepatic acyl-CoA oxidase activity in male B6C3F1 mice.

The interaction potential of peroxisome proliferators of similar and dissimilar structure was examined in B6C3F1 mice. Mice were fed diets containing varying concentrations of ciprofibrate (Cipro), clofibrate (Clof) or di(2-ethylhexyl)phthalate (DEHP), or combinations of Cipro and Clof or Cipro and DEHP for 4 d. Induction of peroxisomal beta-oxidation, measured by increased acyl-CoA oxidase activity, was used as the endpoint for analysis. An additive response occurred following joint exposure to the structurally related compounds Cipro and Clof, whereas a possible synergistic response occurred at low dose combinations of the structurally dissimilar Cipro and DEHP. These findings represent the first report assessing the in-vivo interaction potential of structurally similar and dissimilar peroxisome proliferators and provides insight into the dose-response nature of joint exposures to certain non-genotoxic carcinogens.

Acyl-CoA Oxidase

The interactive effect of chlorine, copper and nitrite on methaemoglobin formation in red blood cells of Dorset sheep.

Simultaneous exposure to chemicals which can oxidize the haemoglobin of the red blood cell to methaemoglobin is common. Although the effects of some of these agents have been documented individually, little research considers the interactive effects. In-vitro experiments on the treated blood of female Dorset sheep assessed the interactive capacity of chlorite, copper and nitrite to affect methaemoglobin formation. All combinations of doses which produced 2.5, 5, 10% methaemoglobin were tested in all possible combinations (a total of 80), as were the controls. This included data on each chemical alone, each two-way combination and the three-way combination. The response is largely additive (the sum of the individual effects) except for one of the two-way interactions, chlorite/nitrite (P less than .01), which showed antagonism. Chlorite may oxidize nitrite which could explain the less-than-additive response. Overall, the result of combining these agents on methaemoglobin was additive.

Animals

Lead-induced cell proliferation and organ-specific tumorigenicity.

While lead acetate is a renal carcinogen in rodent studies, the mechanism by which it induces cancer has not been established. This report proposes that the enhanced susceptibility of renal tubular epithelial cells to lead-induced mitogenicity at the levels comparable to those administered in the cancer bioassay may contribute to the carcinogenic response seen in this target organ. Of relevance is that the nonresponsiveness of the liver to lead-induced carcinogenicity was associated with significantly less capacity (i.e., 675-fold) of lead to induce the mitogenic response in the rodent liver.

Animals

Mink as a predictive model in toxicology.

This paper reviewed the biomedical and toxicological database concerning the use of mink as a predictive model of human responses. It is concluded that substantial information exists on the mink genetics, physiology, metabolism, nutritional requirements, and susceptibility to infectious disease; and provides a foundation upon which interspecies extrapolation may be considered. In addition, information on the response of mink to several dozen toxic substances revealed that mink respond in a qualitatively and quantitatively similar manner to other more commonly employed species as well as humans. Our conclusion does not infer that mink should be used routinely in toxicological testing for estimation of human responses. However, it indicates that toxicological data from this species may be a useful complement in risk assessment processes based upon data obtained from traditionally employed models such as rats and dogs.

Animals

A guide to interpreting soil ingestion studies. I. Development of a model to estimate the soil ingestion detection level of soil ingestion studies.

This paper provides a model with which to predict soil ingestion recovery values in soil ingestion studies either retrospectively or prospectively. The predictive equations generated from the model can be used to estimate minimum soil ingestion detection levels from soil ingestion studies which use mass-balance methods. The model is derived from data assessing soil recovery efficiencies in adults using eight different predictive tracer elements. The results constitute a methodology for determining minimum detection levels of soil ingestion and hence have important regulatory significance.

Humans

A guide to interpreting soil ingestion studies. II. Qualitative and quantitative evidence of soil ingestion.

Four major studies have attempted to qualitatively and quantitatively assess the extent of soil ingestion in children using the soil tracer methodology. The validity of the estimates of soil ingestion in each study was reevaluated in light of the inherent strengths and limitations of study design and/or execution, as well as via a novel methodology for estimating the soil recovery variance for each tracer, which then led to the estimation of soil ingestion detection limits for each tracer for studies performing mass-balance analyses. Based on these analyses it is concluded that the Binder et al. (1986, Arch. Environ. Health 41, 341-345) and Van Wijnen et al. (1990, Environ. Res. 51, 147-162) studies provide no convincing evidence to support qualitative and quantitative estimates of soil ingestion due to inherent limitations in their respective study designs. The Davis et al. (1990, Arch. Environ. Health 45, 112-122) and Calabrese et al. (1989, Regul. Toxicol. Pharmacol. 10, 123) studies displayed convincing qualitative evidence of soil ingestion. However, the results indicate that the median soil ingestion estimates of Davis et al. were less reliable than those of Calabrese et al. The range of detection limits vary according to the tracer and the assumption of acceptable precision in recovery estimation. The minimum detection level of soil ingestion in children in the Calabrese et al. study, with a variance in recovery of 100% +/- 20%, was 21 mg/day based on Zr.(ABSTRACT TRUNCATED AT 250 WORDS)

Adult

Evidence of soil-pica behaviour and quantification of soil ingested.

A previously published report on soil ingestion in children, revealed evidence that one of the subjects, a 3.5-year-old female, displayed soil-pica behaviour. Soil ingestion estimates for this child ranged from approximately 5 to 7 g d-1 for seven of eight soil tracers employed. The present paper revealed that the soil-pica behaviour occurred only in the second of the two weeks of observation, during which daily soil ingestion rates ranged from 10 to 13 g d-1. Tracer recovery studies displayed acceptable precision (i.e. 100% less than +/- 30%) for six of the eight tracers during the soil-pica episode (week 2). Evaluation of the weekly soil ingestion values of the remaining 63 subjects indicated no convincing evidence of soil-pica behaviour in this group of children aged 1-4.

Child Behavior

Induction of peroxisome proliferation in rainbow trout exposed to ciprofibrate.

Rainbow trout (Salmo gairdneri), average body weight of 450 g, were treated with 15, 25, or 35 mg/kg of ciprofibrate via intraperitoneal injection every other day for 2 to 3 weeks. The effects on hepatic peroxisomal acyl-CoA oxidase, polypeptide PPA-80, catalase, and liver weight were measured. The treatment of trout with ciprofibrate showed significant dose-related increases in peroxisomal acyl-CoA activity, polypeptide PPA-80, and catalase after 3 weeks of exposure. Peroxisomal oxidase activity showed a significant (p = 0.0008) increase (78%) at 35 mg/kg and a marginal (p = 0.1) increase (27%) at 25 mg/kg after 3 weeks of exposure. Densitometric analysis of polypeptide PPA-80 and catalase showed increases up to 48 and 236% at 35 mg/kg, respectively. Morphometric analysis on livers of trout administered 35 mg/kg for 3 weeks showed a 2.3-fold increase of peroxisomal volume density, as compared to control. This study demonstrates the induction of peroxisome proliferation in rainbow trout administered ciprofibrate, a known peroxisome proliferator in rodents.

Acyl-CoA Oxidase

Preliminary adult soil ingestion estimates: results of a pilot study.

Six adults were evaluated for the extent to which they ingest soil. This study was originally part of a large childhood soil ingestion study and was used to validate part of the analytical methodology used in that larger study. The adult study followed the soil tracer methodology of the children's study. The principal findings of the adult study revealed that the four most reliable tracer elements based on recovery studies in a mass balance assessment [aluminum (Al), silicon (Si), yttrium (Y), and zirconium (Zr)] yielded the following mean daily adult soil ingestion estimations: Al (77 mg), Si (5 mg), Y (53 mg), and Zr (22 mg). The median daily soil ingestion estimations based on these same tracer elements were: Al (57 mg), Si (1 mg), Y (65 mg), and Zr (-4 mg). These findings represent the first published quantitative estimates of soil ingestion by adults.

Adult

Inhibition of beta-glucuronidase in human urine by ascorbic acid.

The effects of oral supplementation of ascorbic acid (1500 mg d-1) on urinary beta-glucuronidase (beta-G) activity was assessed in a double-blind crossover study design over a 3-week period. The subjects on ascorbic acid treatment displayed a statistically significant (P less than 0.05) decrease in beta-G with an approximate decrease of 25%.

Adult

Superoxide dismutase: its role in xenobiotic detoxification.

Since the discovery of superoxide dismutase in 1969, the role of this enzyme in modulating cellular toxicity of superoxide has been well established. Experimentally, cellular damage from compounds or exposures which produce superoxide extracellularly can be prevented or modified by pretreating a cell or organ system with SOD. Likewise, induction of intracellular SOD by exposing the cell system to various types of nonlethal stress will impart resistance or tolerance to further exposures to oxidant and nonoxidant stresses which would normally be toxic. The differences in intracellular SOD activity based on species, age, and organ variability can have a major impact on the interpretation of toxicology data, particularly extrapolation to human toxicology. An awareness of the importance of SOD to the toxicity of xenobiotics which produce superoxide, either directly or indirectly, will enable those conducting toxicology studies to better understand and interpret their results.

Animals

Catalase: its role in xenobiotic detoxification.

Catalase activity is found primarily in peroxisomes although in some species and in some organ systems, cytosolic catalase also may be involved in intracellular oxidant stress protection. Toxicology studies with repeat exposures to xenobiotics producing hydrogen peroxide either directly or indirectly generally indicate that the organisms develop resistance to the toxin (adaptation). This adaptation would result from induction of catalase activity in most target organs. The induction of hepatic peroxisomes accompanied by less than compensatory increase in catalase activity is now recognized as suggesting a potential for hepatotoxic and hepatocarcinogenic effects. Although these effects seem to also require mobilization of fatty acids, it is not clear if such mobilization is an absolute requirement. As would be expected, there are great differences among species in catalase activity thus making animal-human extrapolations difficult. Finally, with the exception of premature and neonatal animals, age-related variations in catalase activity do not seem to be large enough to have toxicological relevance. However, in old animals, their apparent inability to replace lost catalase activity after repeated stress may have major significance in explaining observed young-old differences in toxicity resulting from oxidant stress.

Aging

How much soil do young children ingest: an epidemiologic study.

Sixty-four children aged 1-4 years were evaluated for the extent to which they ingest soil. The study followed the soil tracer methodology of S. Binder, D. Sokal, and D. Maughan (1986, Arch. Environ. Health, 41, 341-345). However, the present study included a number of modifications from the Binder et al. study. The principal new features were (1) increasing the tracer elements from three to eight; (2) using a mass-balance approach so that the contribution of food and medicine ingestion would be considered; (3) extending the period of observation from 3 days to 8 days; and (4) validating the methodology by having adult volunteers ingest known amounts of soil in a mass-balance validation study. The principal findings reveal the following. (1) The adult study confirmed the validity of the tracer methodology to estimate soil ingestion. (2) Of the eight tracers employed in the adult study, only Al, Si, and Y provided sufficient recovery data that was directly acceptably stable and reliable. (3) If food ingestion determinations were taken into consideration, the median estimates of soil ingestion from the eight tracers ranged from a low of 9 mg/day (Y) to a high of 96 mg/day (V); the median values of Al, Si, and Y, the three most reliable tracers, ranged from 9 mg/day to 40 mg/day. (4) One child had soil ingestion values ranging from 5 to 8 g/day, depending on the tracer. (5) If food ingestion had not been considered, the estimates of soil ingestion would have increased about two- to sixfold, depending on the tracer with Ti and Y being most affected by food intake. (6) Since soil and dust samples did not significantly differ in their levels of tracer elements, no reliable differentiation between the contribution of ingestion of dust and soil could be made. (7) These findings are generally consistent with the previously reported findings of Binder et al. (1986) and P. Clausing, B. Brunekreff, and J.H. van Wijnen (1987, Int. Arch. Occup. Med., 59, 73) if these latter studies are corrected for ingestion of tracers in food and medicine. The findings also account for the apparent discrepancy between the estimates from Al and Si and estimates based on Ti in previous studies. Thus the elevated estimates of soil ingestion by Ti were substantially reduced when food ingestion is considered.

Adult