JAPCA最新文献

This report presents screening-level estimates of the general level of cancer risks arising from air emission from uncontrolled waste sites. Twenty-five National Priorities List sites were chosen randomly and airborne cancer risks estimated for each site in terms of risk to the maximally exposed individual (MEI risk), average individual risk (AEI risk), and population incidence. The estimates were developed using the EPA Human Exposure Model using assumptions on the rate and toxicity of site emissions. MEI risks ranged from 4 X 10(-9) to 1 X 10(-6) with an average of about 5 X 10(-7). AEI risks for individuals residing within four miles of the sites average about 10(-8), declining significantly for individuals residing at longer distances. Population incidence was low at all sites ranging from 2 X 10(-4) to 1 X 10(-2) cancer cases expected within 60 miles of the sites. Due to the uncertainties in this type of analysis and the underlying study assumptions, these results must be viewed with caution. Nonetheless, some preliminary conclusions can be drawn from the analysis, principally that airborne cancer risks from uncontrolled waste sites are likely to be small in most cases, with the greatest concern being maximally exposed individuals rather than the number of cancer cases expected in the exposed population.

To test for an increased reaction to ozone (O3) in older individuals following an initial exposure, and to test for adaptation and its duration, we exposed 10 men and 6 women (60-89 years old) in an environmental chamber to filtered air and 3 consecutive days of O3 exposure (0.45 ppm), followed by a fourth O3 exposure day after a two day hiatus. Subjects alternated 20-min exercise (minute ventilation = 27 L) and rest periods for 2 hours during each exposure. Subjects rated from one to five, 16 possible respiratory/exercise symptoms prior to and following the exposure. Pulmonary function tests were performed before, and during each rest period and following the exposure. Metabolic measurements were obtained during each exercise period. No significant changes in any symptom question occurred, in spite of a threefold increase in the total number of reported symptoms during O3 exposure. Small but significant pre-to-post decrements on the first and second O3 days in forced vital capacity (FVC-111 and 104 mL), forced expiratory volume in 1 (FEV1-171 and 164 mL) and 3 seconds (FEV3-185 and 172 mL) occurred without concomitant changes in any flow parameter of the forced expiratory maneuver. No differences in the group mean response in FVC, FEV1 or FEV3 on the third or fourth day of O3 exposure and the filtered air exposure were found. The observed changes were due to significant physiological changes in eight of the subjects. Unlike young subjects, no evidence of an increased pulmonary function response to a second consecutive O3 exposure was observed.(ABSTRACT TRUNCATED AT 250 WORDS)

Only five studies have been found in the literature which provide any indication of the effectiveness of incineration for rendering infectious hospital waste innocuous. Although there is an indication from these studies for release of bacteria in stack gas, none of the studies identified the bacteria or determined the source of bacteria. The purpose of the present study was to investigate the potential for a hospital incinerator to release human pathogenic bacteria into the ambient environment. In this study, waste spiked with Bacillus subtillis was burned in a hospital incinerator. Although bacteria were found in the incinerator stack gas, (concentrations ranged from not detectable to 1157 colonies/m3 of air) no Bacillus subtilis was recovered from the stack gas. The results suggest that the source of the stack gas bacteria was not from unburned waste or from outdoor air. Analysis of samples of air from the incinerator room (not simultaneous with the stack gas samples) indicates that the source of the stack gas bacteria was most likely the combustion air.

Nine years of summertime ozone data from the Atlanta metropolitan area are analyzed and compared to local emissions of volatile organic carbon and nitrogen oxides. Trends from 1979 to 1987 were studied for the number of days per year ozone exceeded the NAAQS standard, the second-highest ozone level observed per year, and the first quartile summertime average ozone observed, as well as the mean difference between the ozone level observed downwind and upwind of the city. Because this last parameter is sensitive to chemical factors but relatively insensitive to the number of days each year with meteorological conditions conducive to ozone formation, its trend may be best suited for determining how effective emission controls have been in reducing O3 in the Atlanta area. In spite of the fact that sizeable reductions have been claimed for volatile organic carbon emissions over the past several years, the data give no indication that ozone levels have decreased and in fact imply that summertime ozone production may have increased. The results imply that either emissions have not decreased as much as has been claimed or that ozone is not sensitive to anthropogenic volatile organic carbon emissions. In either event, a reevaluation of our nation's strategy for O3 abatement in Atlanta and comparable cities is needed.

A diffusive sampler for formaldehyde originally designed for use in personal monitoring of worker exposure has been evaluated for static measurement of low formaldehyde levels in indoor air. The sampler consists of a 37-mm glass fiber filter impregnated with 2,4-dinitrophenylhydrazine and phosphoric acid and mounted in a polystyrene filter cassette. Formaldehyde is sampled by controlled diffusion and subsequent hydrazone formation on the filter. The hydrazone is eluted from the filter with acetonitrile and analyzed by liquid chromatography and a UV detector. The diffusive sampler was evaluated for static (area) sampling in several industries, offices, and homes with formaldehyde levels of 6-200 ppb. Results from diffusive samplers were compared with results from pumped samplers. Even at low wind velocities (less than 0.01 m.s-1) there was good agreement between pumped and diffusive samples. The sensitivity will be 1 ppb in a 24-h sample, making the sampler especially useful for indoor air monitoring of low formaldehyde levels.

First-time measurements of the potentially toxic inorganic species of arsenic (arsenite and arsenate) have been obtained in fine (less than 2.5 microns AD) and coarse (greater than 2.5 microns AD) atmospheric particles in the Los Angeles area. A recently developed method that includes procedures for sample collection, preparation, and analysis was used in this study. Size-fractionated aerosol samples were collected with a high-volume dichotomous virtual impactor that employed polytetrafluoroethylene filters. Results were obtained for the recovery of arsenic standards added to unexposed and collected filters. Data from this study, indicated that the recently developed speciation method can be used to determine concentrations of As(III) and As(V) in atmospheric particulate matter samples. Size-fractionated aerosol samples were collected in the city of Industry during January and February 1987. In most samples, As(III) and As(V) were above the detection limit (approximately 1 ng m-3 of either species) in both aerosol size fractions. A greater portion (about 75 percent) of the two species were observed in the fine particles. The As(III)/As(V) ratio for both particle sizes was close to 1 (i.e., an equal mixture of both species). Comparison of total suspended particulate arsenic measured by the speciation method to that measured by a routine California Air Resources Board-approved procedure showed good agreement (r = 0.94), indicating both methods were approximately equivalent for the collection and analysis of aerosol arsenic.