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2.
J Occup Environ Hyg ; 6(1): 19-31, 2009 Jan.
Article in English | MEDLINE | ID: mdl-18982535

ABSTRACT

This study investigated the relationships between particle number, surface area, and respirable mass concentration measured simultaneously in a foundry and an automotive engine machining and assembly center. Aerosol concentrations were measured throughout each plant with a condensation particle counter for number concentration, a diffusion charger for active surface area concentration, and an optical particle counter for respirable mass concentration. At selected locations, particle size distributions were characterized with the optical particle counter and an electrical low pressure impactor. Statistical analyses showed that active surface area concentration was correlated with ultrafine particle number concentration and weakly correlated with respirable mass concentration. Correlation between number and active surface area concentration was stronger during winter (R2 = 0.6 for both plants) than in the summer (R2 = 0.38 and 0.36 for the foundry and engine plant respectively). The stronger correlation in winter was attributed to use of direct-fire gas fired heaters that produced substantial numbers of ultrafine particles with a modal diameter between 0.007 and 0.023 mu m. These correlations support findings obtained through theoretical analysis. Such analysis predicts that active surface area increasingly underestimates geometric surface area with increasing particle size, particularly for particles larger than 100 nm. Thus, a stronger correlation between particle number concentration and active surface area concentration is expected in the presence of high concentrations of ultrafine particles. In general, active surface area concentration may be a concentration metric that is distinct from particle number concentration and respirable mass concentration. For future health effects or toxicological studies involving nano-materials or ultrafine aerosols, this finding needs to be considered, as exposure metrics may influence data interpretation.


Subject(s)
Air Pollutants, Occupational/analysis , Automobiles , Industry , Occupational Exposure/analysis , Air Pollutants, Occupational/chemistry , Environmental Monitoring , Metallurgy , Particle Size , Regression Analysis , Seasons , Surface Properties
3.
Ann Occup Hyg ; 52(1): 9-21, 2008 Jan.
Article in English | MEDLINE | ID: mdl-18056626

ABSTRACT

Ultrafine particle number and respirable particle mass concentrations were measured throughout an automotive grey iron foundry during winter, spring and summer using a particle concentration mapping procedure. Substantial temporal and spatial variability was observed in all seasons and attributed, in part, to the batch nature of operations, process emission variability and frequent work interruptions. The need for fine mapping grids was demonstrated, where elevations in particle concentrations were highly localized. Ultrafine particle concentrations were generally greatest during winter when incoming make-up air was heated with direct fire, natural gas burners. Make-up air drawn from roof level had elevated respirable mass and ultrafine number concentrations above ambient outdoor levels, suggesting inadvertent recirculation of foundry process emissions. Elevated respirable mass concentrations were highly localized on occasions (e.g. abrasive blasting and grinding), depended on the area within the facility where measurements were obtained, but were largely unaffected by season. Particle sources were further characterized by measuring their respective number and mass concentrations by particle size. Sources that contributed to ultrafine particles included process-specific sources (e.g. melting and pouring operations), and non-process sources (e.g. direct fire natural gas heating units, a liquid propane-fuelled sweeper and cigarette smoking) were additionally identified.


Subject(s)
Air Pollutants, Occupational/analysis , Iron , Metallurgy , Environmental Monitoring/methods , Humans , Inhalation Exposure/analysis , Occupational Exposure/analysis , Particle Size , Seasons
4.
J Occup Environ Hyg ; 4(5): 341-51, 2007 May.
Article in English | MEDLINE | ID: mdl-17454502

ABSTRACT

Very fine particle number and mass concentrations were mapped in an engine machining and assembly facility in the winter and summer. A condensation particle counter (CPC) was used to measure particle number concentrations in the 0.01 microm to 1 microm range, and an optical particle counter (OPC) was used to measure particle number concentrations in 15 channels between 0.3 microm and 20 microm. The OPC measurements were used to estimate the respirable mass concentration. Very fine particle number concentrations were estimated by subtracting the OPC particle number concentrations from 0.3 microm to 1 microm from the CPC number concentrations. At specific locations during the summer visit, an electrical low pressure impactor was used to measure particle size distribution from 0.07 microm to 10 microm in 12 channels. The geometric mean ratio of respirable mass concentration estimated from the OPC to the gravimetrically measured mass concentration was 0.66 with a geometric standard deviation of 1.5. Very fine particle number concentrations in winter were substantially greater where direct-fire natural gas heaters were operated (7.5 x 10(5) particles/cm(3)) than where steam was used for heat (3 x 10(5) particles/cm(3)). During summer when heaters were off, the very fine particle number concentrations were below 10(5) particles/cm(3), regardless of location. Elevated very fine particle number concentrations were associated with machining operations with poor enclosures. Whereas respirable mass concentrations did not vary noticeably with season, they were greater in areas with poorly fitting enclosures (0.12 mg/m(3)) than in areas where state-of-the-art enclosures were used (0.03 mg/m(3)). These differences were attributed to metalworking fluid mist that escaped from poorly fitting enclosures. Particles generated from direct-fire natural gas heater operation were very small, with a number size distribution modal diameter of less than 0.023 microm. Aerosols generated by machining operations had number size distributions modes in the 0.023 microm to 0.1 microm range. However, multiple modes in the mass size distributions estimated from OPC measurements occurred in the 2-20 microm range. Although elevated, very fine particle concentrations and respirable mass concentrations were both associated with poorly enclosed machining operations; the operation of the direct-fire natural gas heaters resulted in the greatest very fine particle concentrations without elevating the respirable mass concentration. These results suggest that respirable mass concentration may not be an adequate indicator for very fine particle exposure.


Subject(s)
Aerosols/analysis , Air Pollutants, Occupational/analysis , Automobiles , Environmental Monitoring/methods , Occupational Exposure , Aerosols/chemistry , Heating , Humans , Inhalation Exposure , Particle Size , Seasons
5.
Crit Rev Toxicol ; 36(9): 727-76, 2006 Oct.
Article in English | MEDLINE | ID: mdl-17050083

ABSTRACT

After decades of research involving numerous epidemiologic studies and extensive investigations in laboratory animals, a causal relationship between diesel exhaust (DE) exposure and lung cancer has not been conclusively demonstrated. Epidemiologic studies of the transportation industry (trucking, busing, and railroad) show a small elevation in lung cancer incidence (relative risks [RRs] generally below 1.5), but a dose response for DE is lacking. The studies are also limited by a lack of quantitative concurrent exposure data and inadequate or lack of controls for potential confounders, particularly tobacco smoking. Furthermore, prior to dieselization, similar elevations in lung cancer incidence have been reported for truck drivers, and in-cab diesel particulate matter (DPM) exposures of truck drivers were comparable to ambient highway exposures. Taken together, these findings suggest that an unidentified occupational agent or lifestyle factor might be responsible for the low elevations in lung cancer reported in the transportation studies. In contrast, underground miners, many of whom experience the highest occupational DPM exposures, generally do not show elevations in lung cancer. Laboratory studies must be interpreted with caution with respect to predicting the carcinogenic potential of DE in humans. Tumors observed in rats following lifetime chronic inhalation of very high levels of DPM may be attributed to species-specific overload mechanisms that lack relevance to humans. Increased tumor incidence was not observed in other species (hamsters or mice) exposed to DPM at very high levels or in rats exposed at lower levels (99% reduction in DPM and other quantitative and qualitative changes in the chemical and physical characteristics of diesel exhaust. Thus, the current database, which is focused almost entirely on the potential health effects of traditional diesel exhaust (TDE), has only limited utility in assessing the potential health risks of new-technology diesel exhaust (NTDE). To overcome some of the limitations of the historical epidemiologic database on TDE and to gain further insights into the potential health effects of NTDE, new studies are underway and more studies are planned.


Subject(s)
Air Pollutants/toxicity , Carcinogens, Environmental/toxicity , Occupational Exposure , Vehicle Emissions/toxicity , Air Pollutants/pharmacokinetics , Animals , Carcinogenicity Tests , Carcinogens, Environmental/pharmacokinetics , Humans , Lung Neoplasms/epidemiology , Lung Neoplasms/etiology , Meta-Analysis as Topic , Rats , Risk Assessment
6.
Ann Occup Hyg ; 50(3): 249-57, 2006 Apr.
Article in English | MEDLINE | ID: mdl-16361396

ABSTRACT

Aerosol mapping was used to assess particle number and mass concentration in an engine machining and assembly facility in the winter and spring. Number and mass concentration maps were constructed from data collected with two mobile sampling carts, each equipped with a condensation particle counter (10 nm < diameter < 1 microm) and an optical particle counter (300 nm < diameter < 20 microm). Number concentrations inside the facility ranged from 15 to 150 times greater than that outside the facility and were highly dependent on season. The greatest number concentration (>1,000,000 particles cm(-3)) occurred in winter in an area where mass concentration was low (<0.10 mg m(-3)). The increased number of particles was attributed to the exhaust of direct-fire, natural-gas burners used to heat the supply air. The greatest mass concentrations were found around metalworking operations that were poorly enclosed. The larger particles that dominated particle mass in this area were accompanied by ultrafine particles, probably generated through evaporation and subsequent condensation of metalworking fluid components. Repeat mapping events demonstrated that these ultrafine particles persist in workplace air over long time periods.


Subject(s)
Air Pollutants, Occupational/analysis , Metallurgy , Aerosols , Environmental Monitoring/methods , Heating/instrumentation , Humans , Nanostructures/analysis , Occupational Exposure , Particle Size , Seasons
8.
Inhal Toxicol ; 16(14): 889-900, 2004 Dec 15.
Article in English | MEDLINE | ID: mdl-15764476

ABSTRACT

While the International Agency for Research on Cancer (IARC) classified diesel exhaust (DE) as a"probable"carcinogen in 1989 based primarily on"sufficient"animal data, other investigators have since concluded that the lung tumors found in the rat studies were a result of particle overloading. Subsequent health risk assessments of DE have not used the rat cancer data. The U.S. Environmental Protection Agency (EPA), in developing its 2002 Health Assessment Document (HAD) for DE, primarily considered the epidemiology studies of railroad workers and truck drivers to develop health risk assessments of DE. However, both sets of epidemiology studies have serious weaknesses that make them unsuitable for cancer risk assessment. Major shortcomings were the lack of contemporaneous measurements of exposures to DE, difficulties with exposure history reconstruction, and adequately accounting for other exposures such as gasoline exhaust and cigarette smoke. To compound these problems, there was not, and there is still not, a specific exposure marker for DE. Interestingly, in the underground mining industry, where diesel exposures are much higher than observed in railroad workers and truck drivers, there was no increase in lung cancer. These problems and concerns led the U.S. EPA to conclude that while DE was a"likely"carcinogen, a unit risk value or range of risk cannot be calculated from existing data and that the risk could be zero. In addition, the DE emissions have changed and continue to change with the implementation of new emission control technologies. The HAD recognized this fact and noted that further studies are needed to assess new diesel engine emissions. Recent chemical characterization studies on low-emitting diesel engines with catalyzed particulate filters have shown emissions rates for several chemicals of concern that are even lower than comparable compressed natural gas (CNG)-fueled engines. With lower emissions, better fire safety, and improved cost-effectiveness of new low-emitting diesels compared to CNG, current efforts to restrict use of low-emitting diesels seems misguided.


Subject(s)
Air Pollutants/adverse effects , Vehicle Emissions/adverse effects , Air Pollutants/analysis , Animals , Humans , Mice , Risk Assessment , Transportation , Vehicle Emissions/analysis
9.
J Law Med Ethics ; 30(3 Suppl): 166-72, 2002.
Article in English | MEDLINE | ID: mdl-12508521

ABSTRACT

Workplace violence is a continuing problem in the United States, accounting for approximately 1,000 deaths each year and for more than 1.5 million incidents of nonfatal injuries. State and federal agencies have published guidelines for preventing workplace assaults, but there is a need for a strong research agenda to address the effectiveness of intervention strategies. After an overview, this article provides a discussion of workplace violence from three perspectives. One section discusses the process used in a manufacturing setting to install a workplace violence prevention program. A second section provides insight into the processes used to fully implement a workplace violence prevention program in a health care setting. A final section provides insight to the processes brought to bear in one state to mandate prevention of workplace violence in the health care setting. There is a critical need to evaluate alternative strategies to address workplace violence, to make the findings available to legislative and executive branches of government, and to implement effective strategies to counter violence in the workplace.


Subject(s)
Occupational Health/legislation & jurisprudence , Violence/legislation & jurisprudence , Violence/prevention & control , Workplace/legislation & jurisprudence , Humans , Public Health/legislation & jurisprudence , Risk Factors , Security Measures , Social Control Policies/legislation & jurisprudence , United States/epidemiology , Violence/statistics & numerical data
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