Biomedical subjects

Joyce S Tsuji

Publications and source records attributed to Joyce S Tsuji.

5 recordsLinked to original sources

PubMed2005

Research strategies for safety evaluation of nanomaterials, part IV: risk assessment of nanoparticles.

Nanoparticles are small-scale substances (<100 nm) with unique properties and, thus, complex exposure and health risk implications. This symposium review summarizes recent findings in exposure and toxicity of nanoparticles and their application for assessing human health risks. Characterization of airborne particles indicates that exposures will depend on particle behavior (e.g., disperse or aggregate) and that accurate, portable, and cost-effective measurement techniques are essential for understanding exposure. Under many conditions, dermal penetration of nanoparticles may be limited for consumer products such as sunscreens, although additional studies are needed on potential photooxidation products, experimental methods, and the effect of skin condition on penetration. Carbon nanotubes apparently have greater pulmonary toxicity (inflammation, granuloma) in mice than fine-scale carbon graphite, and their metal content may affect toxicity. Studies on TiO2 and quartz illustrate the complex relationship between toxicity and particle characteristics, including surface coatings, which make generalizations (e.g., smaller particles are always more toxic) incorrect for some substances. These recent toxicity and exposure data, combined with therapeutic and other related literature, are beginning to shape risk assessments that will be used to regulate the use of nanomaterials in consumer products.

Environmental Exposure↗

PubMed2005

Evaluation of exposure to arsenic in residential soil.

In response to concerns regarding arsenic in soil from a pesticide manufacturing plant, we conducted a biomonitoring study on children younger than 7 years of age, the age category of children most exposed to soil. Urine samples from 77 children (47% participation rate) were analyzed for total arsenic and arsenic species related to ingestion of inorganic arsenic. Older individuals also provided urine (n = 362) and toenail (n = 67) samples. Speciated urinary arsenic levels were similar between children (geometric mean, geometric SD, and range: 4.0, 2.2, and 0.89-17.7 microg/L, respectively) and older participants (3.8, 1.9, 0.91-19.9 microg/L) and consistent with unexposed populations. Toenail samples were < 1 mg/kg. Correlations between speciated urinary arsenic and arsenic in soil (r = 0.137, p = 0.39; n = 41) or house dust (r = 0.049, p = 0.73; n = 52) were not significant for children. Similarly, questionnaire responses indicating soil exposure were not associated with increased urinary arsenic levels. Relatively low soil arsenic exposure likely precluded quantification of arsenic exposure above background.

Adolescent↗

PubMed2004

Health effect levels for risk assessment of childhood exposure to arsenic.

Health risks to children from chemicals in soil and consumer products have become a regulatory focus in the U.S. This study reviews short-term health effect levels for arsenic exposure in young children (i.e., 0-6 years old). Acute health effects are described mostly in adults in case reports of arsenic poisoning from water or food and in studies of medicinal arsenic treatment. Several epidemiological studies report health effects from subchronic arsenic exposure in children primarily from drinking water in developing countries. Acute health effects typically include gastrointestinal, neurological, and skin effects, and in a few cases facial edema and cardiac arrhythmia. Dermatoses are most consistently reported in both adults and children with subchronic exposure. With low exposure, the prevalence and severity of disease generally increases with age (i.e., length of exposure) and arsenic dose. The available data collectively indicate a lowest-observed-adverse-effect level around 0.05mg/kg-day for both acute and subchronic exposure. At low doses, children do not appear to be more sensitive than adults on a dose-per-body-weight basis, although data for acute exposures are limited and uncertainties exist for quantifying potential neurological or vascular effects at low-level subchronic exposures. Based on these data, possible reference levels for acute and subchronic exposure in young children are 0.015 and 0.005mg/kg-day, respectively.

Adolescent↗

PubMed2003

Evaluation of mercury in urine as an indicator of exposure to low levels of mercury vapor.

We conducted a pooled analysis to investigate the relationship between exposure to elemental mercury in air and resulting urinary mercury levels, specifically at lower air levels relevant for environmental exposures and public health goals (i.e., < 50 microg/m3 down to 1.0 microg/m3). Ten studies reporting paired air and urine mercury data (149 samples total) met criteria for data quality and sufficiency. The log-transformed data set showed a strong correlation between mercury in air and in urine (r = 0.774), although the relationship was best fit by a series of parallel lines with different intercepts for each study R2 = 0.807). Predicted ratios of air to urine mercury levels at 50 microg/m3 air concentration ranged from 1:1 to 1:3, based on the regression line for the studies. Toward the lower end of the data set (i.e., 10 microg/m3), predicted urinary mercury levels encompassed two distinct ranges: values on the order of 20 microg/L and 30-60 microg/L. Extrapolation to 1 microg/m3 resulted in predicted urinary levels of 4-5 and 6-13 microg/L. Higher predicted levels were associated with use of static area air samplers by some studies rather than more accurate personal air samplers. Urinary mercury predictions based primarily on personal air samplers at 1 and 10 microg/m3 are consistent with reported mean (4 microg/L) and upper-bound (20 microg/L) background levels, respectively. Thus, although mercury levels in air and urine are correlated below 50 microg/m3, the impact of airborne mercury levels below 10 microg/m3 is likely to be indistinguishable from background urinary mercury levels.

Biomarkers↗

PubMed2002

Separating potential source exposure from background exposure in subsistence populations in developing countries.

Risk assessment methods of developed countries have prescribed exposure assumptions for calculating health risks that are generally inappropriate for developing countries because of population, cultural, and social differences. For example, populations in developing countries are often subsistence users of natural resources with a more outdoor-oriented lifestyle. Assessments should thus measure specific dietary intake rates and contact rates with environmental media. Chemical analyses of food, environmental media, and any biomarkers of exposure should include a carefully matched reference population to distinguish between exposures due to naturally occurring metals in more mineralized areas and potential anthropogenic sources. Without a reference group, one might predict excess risk associated with the external source, even though exposure is due to background levels. For example, subsistence populations often have a simple diet with high ingestion rates of a few food types (e.g. 200 g/day wet weight of fish; 500 g/day of rice). These foods can be naturally elevated in arsenic (fish and rice) and mercury (fish). Conservative risk assessments that extrapolate toxicity from high to low doses can predict elevated risks for these naturally occurring elements (e.g. greater than 1 in 10,000 cancer risk for arsenic). Whether the calculated risks are actually indicative of harm to subsistence populations should be considered in light of the beneficial properties of the diet and the lack of alternative food choices.

Animals↗