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House dust mites in university dormitories.

As no published data was available, dust was collected from 102 university student dormitory rooms and 33 were selected on a random basis for analysis. Mean dust per dormitory room was 4.47 g of coarse, 0.96 g of fine, and a 24-hour sedimented volume of fine dust of 6.90 mL. The mean number of mites was 63/g of coarse dust, and 240/g and 36/mL of fine dust. They were identified as D. pteronyssinus (D.p.), 81.9%; D. farinae, 11.2%; and Cheyletus, 4.7%. Fifteen samples from homes were controls. Mean values were 0.60 g of coarse dust, and 0.20 g and 2.3 mL of fine dust. Mites numbered 985/g of coarse, and 3409/g and 244/mL of fine dust. They were D.p., 87.2%; D. farinae, 3.0%; Cheyletus, 3.7%; and Euroglyphus, 1.6%. Differences between dormitories and homes in amount of dust and number of mites were significant at P less than .001. Dust and mites were significantly less in dormitories with linoleum than those with carpets (P less than .05 and .01, respectively). In conclusion, university dormitories have significantly less mites than homes despite a greater amount of dust harvested.

Animals↗

[Biological effect of wood dust].

The biological effect of exposure to wood dust depends on its composition and the content of microorganisms which are an inherent element of the dust. The irritant and allergic effects of wood dust have been recognised for a long time. The allergic effect is caused by the wood dust of subtropical trees, e.g. western red cedar (Thuja plicata), redwood (Sequoia sempervirens), obeche (Triplochiton scleroxylon), cocabolla (Dalbergia retusa) and others. Trees growing in the European climate such as: larch (Larix), walnut (Juglans regia), oak (Quercus), beech (Fagus), pine (Pinus) cause a little less pronounced allergic effect. Occupational exposure to irritative or allergic wood dust may lead to bronchial asthma, rhinitis, alveolitis allergica, DDTS (Organic dust toxic syndrome), bronchitis, allergic dermatitis, conjunctivitis. An increased risk of adenocarcinoma of the sinonasal cavity is an important and serious problem associated with occupational exposure to wood dust. Adenocarcinoma constitutes about half of the total number of cancers induced by wood dust. An increased incidence of the squamous cell cancers can also be observed. The highest risk of cancer applies to workers of the furniture industry, particularly those dealing with machine wood processing, cabinet making and carpentry. The cancer of the upper respiratory tract develops after exposure to many kinds of wood dust. However, the wood dust of oak and beech seems to be most carcinogenic. It is assumed that exposure to wood dust can cause an increased incidence of other cancers, especially lung cancer and Hodgkin's disease. The adverse effects of microorganisms, mainly mould fungi and their metabolic products are manifested by alveolitis allergica and ODTS. These microorganisms can induce aspergillomycosis, bronchial asthma, rhinitis and allergic dermatitis.

Dermatitis, Allergic Contact↗

A randomized trial of the effect of dust control on children's blood lead levels.

OBJECTIVE: Dust control is recommended as one of the cornerstones of controlling childhood lead exposure; however, the effectiveness of dust control has not been demonstrated for children who have low to mild elevations in blood lead (ie, less than 25 micrograms/dL). The objective of this study was to determine whether dust control, as performed by families, had an effect on children's blood lead levels and dust lead levels in children's homes. DESIGN: Randomized, controlled trial. SETTING: Community-based trial in Rochester, NY. PARTICIPANTS: One hundred four children, 12 to 31 months of age at baseline. INTERVENTION: Families and children were randomized to one of two groups. Families of children in the intervention group received cleaning supplies, information about cleaning areas that are often contaminated with lead, and a cleaning demonstration. Families in the control group received only a brochure about lead poisoning prevention. OUTCOME MEASURES: Baseline measurements of lead in blood, house dust, soil, water, and paint were taken from both groups. Seven months after enrollment, a second blood lead assay was obtained, and lead levels in household dust were measured. The main outcome measures were change in blood lead levels and dust lead levels by treatment group. RESULTS: The median blood lead level of children enrolled in the study was 6.7 micrograms/dL (range, 1.7 to 30.6 micrograms/dL). There was no significant difference in the change of children's blood lead levels or dust lead levels by treatment group. The median change in blood lead levels among children in the intervention group was -0.05 micrograms/dL compared with -0.60 micrograms/dL among those in the control group. There also was no significant difference in the change of dust lead by group assignment, although there was a trend toward a significant difference in the percentage of change in dust lead levels on noncarpeted floors, which was greater among houses in the intervention group. CONCLUSIONS: These data suggest that an intervention that consists only of providing cleaning supplies and a brief description of dust control is not effective at reducing blood lead levels among urban children with low to mild elevations in blood lead levels at a 7-month follow-up.

Child Welfare↗

Induction of atopic dermatitis by inhalation of house dust mite.

BACKGROUND: The pathogenetic role of house dust mite in atopic dermatitis remains controversial. Recent studies have shown that intensive epicutaneous contact of house dust mite allergen with premanipulated skin may induce dermatitis. It is, however, uncertain whether such conditions are met during natural contact with house dust mite. In the past, allergen inhalation has been suggested to induce exacerbation of atopic dermatitis. The aim of this study was to investigate whether dermatitis could be induced in patients with atopic dermatitis by inhalation of house dust mite. METHODS: Twenty patients with atopic dermatitis underwent bronchial provocations with house dust mite. Challenge tests were performed with four concentrations of a standardized house dust mite extract in a double-blind, randomized, placebo-controlled fashion. Spirometry was performed, and FEV1 was measured before and after each challenge dose. Changes in severity or localization of itching or erythema were recorded. RESULTS: In nine of 20 patients with atopic dermatitis bronchial challenge with house dust mite induced unequivocal skin symptoms after 1.5 to 17 hours. Pruritic erythematous lesions on noninvolved sites together with exacerbations of existing lesions were seen in three patients. Three patients had an exacerbation only, and three other patients had new lesions only. In eight of nine patients with house dust mite inhalation-induced dermatitis, skin symptoms were preceded by an early bronchial reaction. All patients with house dust mite-induced dermatitis had a history of asthma, and as a group they had a higher mean blood total IgE level compared with the "negative skin responders." One patient had pruritic erythema on the placebo challenge day, without a preceding bronchoconstrictive reaction. The number of patients who had a skin response on the house dust mite challenge day was significantly higher than the number of patients who had a skin response on the placebo day (p = 0.011 [Prescott's test]). CONCLUSIONS: The respiratory route may be relevant in the induction and exacerbation of dermatitis in a subset of patients with atopic dermatitis who have early bronchial reactions after house dust mite inhalation, a history of asthma, and an elevated blood total IgE level. Furthermore, these findings suggest a possible causal relationship between bronchial reactions and skin reactions.

Administration, Inhalation↗

Polybrominated diphenyl ethers in indoor dust in Ottawa, Canada: implications for sources and exposure.

Polybrominated diphenyl ethers (PBDEs) are widely used as additive flame retardants in plastics, soft furnishings, electrical and electronic equipment, and insulation in the indoor environment, and may be released indoors via volatilization or as dusts. The penta-and octa-brominated mixes are now banned in most parts of Europe, and phasing out of their use has recently begun in North America. This study follows a previous investigation into indoor air levels of PBDEs. House dust was analyzed from the family vacuum cleaners of 68 of the same 74 randomly selected homes, in Ottawa, Canada during the winter of 2002-2003. PBDEs, comprising on average 42% BDE-209, were found in all samples. The levels were log-normally distributed with a geometric mean sigmaPBDE of 2000 ng g(-1), and a median of 1800 ng g(-1) dust. The levels in dust did not correlate with questionnaire information on house characteristics. Correlations were found between pentamix congener levels in dust and in air from the same homes, but not for congeners of the more highly brominated mixes. Exposure scenarios are presented for mean and high dust ingestion rates, and compared against exposures from other pathways, for both adults and toddlers (6 months-2 years). Assuming a mean dust ingestion rate and median dust and air concentrations, adults would be exposed to ca. 7.5 ng sigmaPBDE d(-1) via the dust ingestion pathway, which represents approximately 14% of total daily exposure when compared to diet (82%) and inhalation (4%). However, for toddlers the equivalent intakes would be 99 ng d(-1), representing 80% of their daily PBDE exposure. At high dust ingestion rates these values increase to 180 ng d(-1) (80% daily intake) for adults and 360 ng d(-1) (89% daily intake) for toddlers. The data give a clearer picture of sources of PBDE exposure in the home environment and suggest that dust could be a significant exposure pathway for some individuals, particularly children.

Adult↗

The effect of storage on allergen and microbial agent levels in frozen house dust.

BACKGROUND: House dust samples collected for exposure studies are often stored for variable time periods until analysis. However, there is currently no information on the effects of dust storage on the content of biocontaminants. Therefore, associations were analysed between the levels of mite allergens (Der p 1, Der f 1), cat allergen (Fel d 1) and microbial components (endotoxin, beta(1-->3)-glucan) on the one hand and the storage duration of dust samples at -20 degrees C on the other hand. METHODS: Within the framework of a study on the influences of INdoor factors and Genetics on Asthma (INGA), dust samples were collected from living room floors between June 1995 and August 1998 and extracted according to a standardized protocol. The concentrations of Der p 1, Der f 1, Fel d 1 and beta(1-->3)-glucan were determined with specific enzyme immunoassays. Endotoxin content was quantified using a chromogenic kinetic Limulus amoebocyte lysate (LAL) test. All concentrations were expressed per gram of dust RESULTS: Dust samples (n = 1236) were obtained from 655 homes in Hamburg, Hettstedt, Zerbst and Bitterfeld. Storage duration (range 8-298 days) was grouped into four categories ( 120 d). After adjustment for city of residence and season of dust sampling, means ratios comparing categories 2-4 to the first category were not statistically significant for Der p 1, Der f 1, endotoxin and beta(1-->3 glucan). However, Fel d 1 concentrations significantly declined with increased storage times of dust samples. CONCLUSIONS: Storage of house dust at -20 degrees C for up to 10 months has no effect on mite allergen, endotoxin and beta(1-->3)-glucan levels. A potential loss of Fel d 1 during storage of frozen dust samples needs further investigations by repeated measurements of allergen in identical dust samples.

Air Pollution, Indoor↗

House dust mite allergen in US beds: results from the First National Survey of Lead and Allergens in Housing.

BACKGROUND: Although exposure to house dust mite allergen is a major risk factor for allergic sensitization and asthma, nationwide estimates of dust mite allergen levels in US homes have not been reported. OBJECTIVE: The purpose of this study was to estimate the prevalence of dust mite allergen in beds of US homes and to identify predictors of dust mite allergen concentration. METHODS: Data were obtained from the first National Survey of Lead and Allergens in Housing, a cross-sectional survey of 831 permanently occupied noninstitutional housing units that permitted resident children. Dust mite allergen concentration (Der f 1 plus Der p 1) was determined from a dust sample collected from a bed. The percentages of homes with concentrations at or greater than detection, 2.0 microg/g bed dust, and 10.0 microg/g bed dust were estimated. Independent predictors of allergen concentration were assessed with multivariable linear regression. RESULTS: The percentages of US homes with dust mite allergen concentrations at or greater than detection, 2.0 microg/g, and 10.0 microg/g were 84.2% (SE, 1.73), 46.2% (SE, 2.0), and 24.2% (SE, 2.1), respectively. Independent predictors of higher levels were older homes, non-West census regions, single-family homes, no resident children, lower household income, heating sources other than forced air, musty or mildew odor, and higher bedroom humidity. CONCLUSION: Most US homes have detectable levels of dust mite allergen in a bed. Levels previously associated with allergic sensitization and asthma are common in US bedrooms. Predictors can be used to identify conditions under which homes are more likely to have increased dust mite allergen levels.

Allergens↗

On the possibility of dust condensation in the ejecta of supernova 1987a.

We suggest that supernova 1987a may condense dust of substantial visual optical thickness as do many novae. The dust will act as a calorimeter of the photon luminosity of any central engine that is dominant at the time of dust formation. Observations of novae suggest that dust formation may occur when the expanding ejecta reach a temperature of 1000 K. The early luminosity of the supernova may be dominated by radioactivity that is unrelated to the central engine that determines the energy balance for the long-term development of the supernova. We discuss the possibility that a constant luminosity central power source such as a pulsar dominates the luminosity of the supernova ejecta by the time that dust can condense and argue that, if a shell mass of more than a few tenths of one solar mass was ejected, emission from dust may be observable in the thermal infrared spectral region. Maximum dust optical depth should occur by late 1987 or early 1988. If the dust becomes optically thick, the visual light from the supernova may drop precipitously. The characteristics of an optically thick dust shell as a calorimeter of the luminosity of the central engine are discussed and are related to previous observations of dust formation in type II supernovae. It is suggested that dust of several chemical compositions may form at different epochs.

Journal Article↗

Interrelationship between hemolysis and lipid peroxidation of human erythrocytes induced by silicic acid and silicate dusts.

Silicic acid and silicate dusts (slate dust and chrysotile asbestos) cause hemolysis of erythrocytes in vitro. The peroxidation of polyunsaturated fatty acids (PUFA) of erythrocyte membrane lipids is also enhanced by incubating the erythrocytes with silicic acid and silicate dusts in in vitro. Hemolysis of erythrocytes elicited by silicic acid and silicate dusts is inhibited significantly by polyvinyl-pyrrolidone and dipalmitoyl lecithin (DPL). These agents, however, have no effect on silicic acid and silicate dust induced peroxidation of erythrocyte membrane lipids. On the other hand, peroxidation of erythrocyte membrane lipids, induced by silicic acid and silicate dusts, is inhibited almost completely by adding superoxide dismutase and catalase to the incubation system, whilst the hemolysis of erythrocytes induced by silicic acid and silicate dusts is unaffected by these agents. Similarly the lysis of erythrocytes, induced by silicic acid and silicate dusts, proceeds at a much faster rate than silicic acid and silicate dust induced lipid peroxidation. These results indicate that silicic acid and silicate dust induced hemolysis and lipid peroxidation represent two independent processes.

Asbestos↗

Effects of the Asian dust events on daily mortality in Seoul, Korea.

The Korean peninsula has a long history of dust clouds blown by winds from the arid deserts of Mongolia and China in springtime; these are called Asian dust events. Public concern about the possible adverse effects of this dust has increased, because the dust arrives in Korea after having passed over heavily industrialized eastern China. The present study explored the effect of Asian dust events on daily mortality in Seoul, South Korea, during the period 1995-1998. We evaluated the association between daily death counts and the dust events using Poisson regression analysis, adjusted for time trends, weather variables, and the day of the week. Between 1995 and 1998, we identified 28 Asian dust days in Seoul. The estimated percentage increase in the rate of deaths from 3-day moving averages of exposure was 1.7% (95/ confidence interval: -1.6 to 5.3) for all causes, 2.2% (95% confidence interval: -3.5 to 8.3) for deaths of persons aged 65 years and older, and 4.1% (95% confidence interval: -3.8 to 12.6) for cardiovascular and respiratory causes. Our results provide weak evidence that the Asian dust events are associated with risk of death from all causes. However, the association between the dust events and deaths from cardiovascular and respiratory causes was stronger and it suggests that persons with advanced cardiovascular and respiratory disease may be susceptible to the Asian dust events.

Age Factors↗

The development of a novel method for directional dust monitoring.

Dust monitoring using sticky pads was popularised in the 1980s. The discolouration caused by dust adhering to white adhesive material was measured with a smoke stain reflectometer. This loss of reflectance was expressed as the percentage effective area coverage (EAC%) per day. EAC% can be used as a measure of nuisance caused by dust. EAC% may also be measured with a hand-held Sticky Pad Reader (SPR). Sticky pads can be mounted on flat or cylindrical surfaces to measure dust by deposition or in flux. An alternative method was developed in the 1990s that measured total dust coverage using computer-based scanning. DustScan used a transparent adhesive film wrapped around a vertical cylinder with magnetic north marked. The sticky pad was sealed with another transparent sheet before scanning at 50 dots per inch (dpi). Dust levels were assessed by comparing the grey-scale values of pixels in the exposed area with an unexposed reference area. Insects and other extraneous material could be 'masked out' from the computer analysis. Dust coverage was expressed as percentage absolute area coverage (AAC%). DustScan has subsequently been developed commercially. A limited trial indicated that monitoring periods of 7-14 days were preferred to avoid dust saturation of the sticky pad. A method for calculating EAC% has been developed and shown to have a high degree of correspondence with an SPR. A trial for the Minerals Industry Research Organisation (MIRO) made comparisons between DustScan and other dust monitoring methods. Dust nuisance limits based on AAC% and EAC% are proposed.par.

Air Pollutants↗

The gastrointestinal absorption of plutonium and americium in rats and guinea pigs after ingestion of dusts from the former nuclear weapons site at Maralinga: implications for human exposure.

The gastrointestinal absorption of plutonium and americium present in dusts from the Maralinga test sites in South Australia has been measured as an input to dose assessments. The materials studied were from three different areas, designated Taranaki (Q380II), TM100 (10/2) and N. Plume (26). The three dusts were fed to groups of rats, mixed with their normal food. The Taranaki and TM100 dusts were also fed to guinea pigs, as a suspension in water. Expressed as fractional absorption from the gastrointestinal tract (f1), the values obtained for plutonium were 2 x 10(-6) and 8 x 10(-6) for Taranaki dust in rats and guinea pigs, respectively, 3 x 10(-6) and 10(-5) for TM100 dust in rats and guinea pigs, respectively, and 2 x 10(-6) for N. Plume dust in rats. The f1 values obtained for americium were 3 x 10(-6) and 2 x 10(-5) for Taranaki dust in rats and guinea pigs, respectively, 10(-5) and 5 x 10(-5) for Taranaki dust in rats and guinea pigs, respectively, and 10(-5) for N. Plume dust in rats. On the basis of these results, rounded f1 values used in the dose assessments were 10(-5) for plutonium and 10(-4) for americium, applying to all intakes of dust. These values compare with the International Commission on Radiological Protection recommendations of 10(-3) for unspecified chemical forms of both elements, 10(-4) for plutonium nitrate and 10(-5) for plutonium oxides. The effect of changes in f1 values on doses from 239Pu and 241Am is considered.

Air Pollutants, Radioactive↗

Guanine content and Dermatophagoides pteronyssinus allergens in house dust samples.

The study of the relationship between the guanine content and Dermatophagoides pteronyssinus (Dp) allergens in house dust samples is reported. Mattress and carpet dust of bedrooms from 22 different homes constituted the house dust samples. The guanine content was determined by quantitative measurements and the mite allergenicity by two immunochemical assays with a partially purified extract of Dp as internal reference: RAST inhibition and crossed and rocket line immunoelectrophoresis. A large scale range of guanine content was obtained among the 22 house dust samples studied (0.01 to 1.78 mg/0.1 gm of dust). Data of RAST inhibition, analyzed according to parallel line bioassay, demonstrated no significant difference between the slopes of the reference and the house dust sample lines, but a 100-fold variation in the relative Dp potencies was observed. By crossed and rocket line immunoelectrophoresis technique, the presence and the amounts of major Dp allergens (Der p I and Dp 4) were established in most house dust extracts. A significant correlation was found between the guanine content of the house dust samples and their relative Dp potencies (r = 0.86) on the one hand, and with their relative content of Der p I and Dp 4, two major Dp allergens (r = 0.75 and r = 0.74, respectively) on the other hand; in each case, a quantitative relationship was established. These results suggest that the guanine determination could assess mite allergens in house dust and may be a useful tool in large-scale investigations of house dust.

Allergens↗

A comparison of the effect of conventional and filter vacuum cleaners on airborne house dust mite allergen.

The efficiency (dust collection and recirculation) of a conventional upright vacuum cleaner with a prototype vacuum bag (I) with pore size of 0.1 micron was compared with a standard vacuum cleaner bag (II), in the homes of 11 atopic asthmatic subjects with a known allergy to house dust mite. Four filter vacuum cleaners were assessed in pairs-the Vax 2000 with the Vorwerk VK121 ET340 (in 10 homes), and the Nilfisk GS90 'Allergy Vac' with the Bosch maxima 43 (in nine homes). All of the selected homes were vacuumed throughout (carpets and soft furnishings) for a 15 min period with each of the cleaners, and air was sampled simultaneously at 21 min-1 (Casella personal sampler). The weight of dust retrieved was recorded, and a sample of sieved dust (2 g) and the air filters were extracted to determine the concentrations of the major allergen, Der pI, by ELISA (ALK). No significant difference was observed in either total weight of dust, or airborne and dust concentrations of Der pI between using the conventional cleaner with vacuum bags I, or vacuum bags II. The Vax and the Vorwerk filter vacuum cleaners produced no measurable airborne Der pI concentrations during use in any of the 10 homes tested, whilst the Nilfisk produced airborne Der pI in two, and the Bosch in one of the nine homes tested. The Vorwerk retrieved significantly more dust from the floors than the Vax (P < 0.002). There was no significant difference in dust retrieval between the Nilfisk and the Bosch. All of the filter vacuum cleaners investigated produced lower concentrations of airborne Der pI, compared to the conventional cleaner with or without a special dust bag. However, the amount of dust and concentration/amount of Der pI that these cleaners actually retrieved, varied and the Vorwerk appeared most effective overall.

Air Pollution, Indoor↗

Levels and determinants of beta(1-->3)-glucans and fungal extracellular polysaccharides in house dust of (pre-)school children in three European countries.

BACKGROUND: Mold growth is believed to be one causative factor underlying the association between dampness in buildings and increased respiratory morbidity. Measurements of beta(1-->3)-glucans and fungal extracellular polysaccharides (EPS) are used as markers of mold exposure in field studies. Little is known about their levels and determinants in homes. OBJECTIVE: To study levels and determinants of beta(1-->3)-glucan and EPS levels in mattress and living room floor dust in three European countries. METHODS: Mattress and living room floor dust was collected in the homes of 1065 German, Dutch, and Swedish (pre-)school children. All samples were analyzed for beta(1-->3)-glucans and EPS in one central laboratory. Determinants were assessed by questionnaire. RESULTS: Amounts of dust, EPS and beta(1-->3)-glucan levels differed between countries. Amounts of dust, beta(1-->3)-glucan and EPS levels for mattresses were only weakly correlated with those for living room floors. Floor dust beta(1-->3)-glucan loads, EPS loads and EPS concentrations were strongly correlated with the amount of dust sampled, which is largely determined by the type of floor that was sampled (carpeted floors had 5-20 higher amounts of dust). None of the other determinants was consistently and statistically significantly associated with amounts of dust, beta(1-->3)-glucan and EPS concentrations on floors and mattresses. CONCLUSION: Mattress dust and floor dust are two different measures of exposure to the investigated mold components. Living room floor beta(1-->3)-glucan and EPS loads and EPS concentrations are largely determined by the type of floor sampled. Differences between countries can only partly be explained by the determinants studied.

Air Pollution, Indoor↗

Environmental and childhood lead contamination in the proximity of boat-repair yards in southern Thailand--I: pattern and factors related to soil and household dust lead levels.

High blood lead levels have recently been documented in schoolchildren living in communities adjacent to boat-repair yards in southern Thailand. In this study, the spatial pattern of lead contamination of soil and household dust in an area surrounding several boat-repair yards is described, and household factors associated with elevated dust lead are identified. A cross-sectional spatial study was conducted in a coastal residential area within a distance of 2 km from three major boat-repair yards situated on the east coast of peninsular Thailand. Household dust specimens were collected from an undisturbed position in the residences of children, aged 4-14 years, sampled randomly from all children living in the study area. Soil specimens were obtained from the interstices of a square grid, 70 x 70 m2, superimposed on the area. Geographic coordinates of residence and soil sampling positions were recorded and semivariograms and kriging used to contour the spatial distribution of lead in dust and soil. Environmental lead levels were also modeled in terms of direction and minimum distance from a boat-repair yard and, for household dust lead content, in terms of household variables, including occupation of household members in boat-repair work, type of house construction, and general cleanliness. Household dust and soil lead content ranged from 10 to 3025 mg/kg and from 1 to 7700 mg/kg, respectively. The distribution of soil lead peaked at the location of the boat-repair yards, but outside the yards the distribution was generally below 400 mg/kg and irregular. About 24% of household dust lead specimens were equal to or above 400 mg/kg, but showed significant decrease with increasing distance from the boat-repair yards, at rates of between 7% and 14% per 100 m. In houses where a family member was a worker in one of the major boatyards and in houses where occasional repair of small boats was undertaken, household dust lead levels were significantly elevated, by 65% (95% CI: 18-130%) and 31% (95% CI: 5-63%), respectively. Siting of boat-repair yards at a distance from residential areas and measures to reduce the spread of lead-containing dust are recommended to alleviate the problem of elevated household dust lead levels.

Adolescent↗

Comparison of hardwood and softwood dust-induced expression of cytokines and chemokines in mouse macrophage RAW 264.7 cells.

Numerous epidemiological studies have shown that occupational exposure to wood dust can induce several respiratory diseases such as allergic rhinitis, chronic bronchitis, asthma, and sino-nasal adenocarcinoma. However, comparison of the harmful potential of different wood dust species on the basis of epidemiological studies is complicated because in the occupational environment workers are usually exposed to several wood dust species simultaneously. In the present study, we have characterized and compared the effects of two hardwood dusts, beech and teak, and two softwood dusts, pine and spruce, on cytokine and chemokine expression utilizing an in vitro model, murine macrophage cell line RAW 264.7. The expression patterns of selected cytokines and chemokines were assessed by real-time quantitative PCR and by ELISA. All the tested hardwood and softwood dusts induced TNF-alpha expression and inhibited IL-1beta expression. Similarly, all the wood dusts induced the expression of CCL2, CCL3, CCL4, and CXCL2/3 chemokines and inhibited CCL24 expression. Our results indicate that both hardwood and softwood dusts influence the cytokine and chemokine expression of RAW 264.7 cells. Although some differences could be detected in the magnitude of responses to different wood dust species, the two tested wood dust groups, hardwoods and softwoods, have quite similar effects on cytokine and chemokine expression in RAW 264.7 cell line.

Animals↗

Assessment of human risks from exposure to low toxicity occupational dusts.

Recent animal studies have demonstrated three separate and distinct mechanisms by which low toxicity dusts can cause important chronic pulmonary effects; through overloading of clearance mechanisms, through increased toxicity associated with ultrafine particle size or by increasing the toxicity of known carcinogens in mixed exposures. The problem to be addressed is how the pathogenicity to man of various airborne dusts should be evaluated, when epidemiological evidence is often insufficient, and the reliability of extrapolation of quantitative risks from animals to man is not established. In this paper we examine the feasibility of evaluating the likely human risks of low toxicity dusts by: (1) semi-quantitative comparisons of the ability of various dusts, in animal studies, to cause overload of clearance and resulting inflammation and fibrosis; (2) postulating that these relativities apply quantitatively to human risks; and (3) estimating approximate human risks by comparisons with reference dusts for which adequate animal and human data are available. Such a decision-making framework appears feasible, provided: (1) comparable and quantitative methods are used consistently in animal studies for the measurement of impairment of clearance leading to overload and resulting inflammation and fibrosis; (2) the quantitative relationships between impairment of clearance leading to overload, and resulting inflammation and fibrosis, can be defined adequately in animals for various dusts; (3) the particle size distributions, including those in the ultrafine range, for dusts to which animals and/or humans are exposed, are taken into account (or are comparable); (4) at least two reference dusts with well-documented activities spanning the range of toxicity can be identified; and (5) the reliability of the predictions of human pathogenicity of a sample of other dusts is tested, in toxicological studies and by observation in humans. Some possible candidate reference and test dusts are identified.

Animals↗