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Bioaerosol Lung Damage in a Worker with Repeated Exposure to Fungi in a Water-Damaged Building.

There has been increased concern over health effects related to potential exposure of building occupants to bioaerosols. We report the case of a worker with a respiratory illness related to bioaerosol exposure in a water-damaged building with extensive fungal contamination. We performed environmental tests to evaluate potential exposure to fungi, and we used mycotoxin-specific IgG antibody in serologic studies in the attempt to evaluate exposure to mycotoxins. Extensive fungal contamination was documented in many areas of the building. Penicillium, Aspergillus, and Stachybotrys species were the most predominant fungi found in air sampling. Our serologic test was not useful in differentiating workers who were probably occupationally exposed to mycotoxins from those who were not; however, it did yield evidence that individuals may make specific IgG antibodies to macrocyclic tricothecene mycotoxins. Further research is needed concerning health effects related to bioaerosol exposures, particularly regarding markers of exposure to specific fungi that may produce mycotoxins. In the absence of clinical tools specific for evaluation of mycotoxin-related illness, a systematic clinical approach for evaluating persons with suspected building-related respiratory illness is warranted. Key words: bioaerosol, building-related illness, fungi, hypersensitivity pneumonitis, mycotoxin, Stachybotrys, water damage. Environ Health Perspect 109:641-644 (2001). [Online 15 June 2001]

http://ehpnet1.niehs.nih.gov/docs/2001/ 109p641-644trout/abstract.html

Physicians are increasingly being asked to evaluate persons who report symptoms thought to be associated with indoor (nonindustrial) environments where various types of environmental problems have been identified. Although occupants of moisture-damaged buildings may experience increased respiratory symptoms (1), the clinical importance of moisture damage remains unclear in situations where occupants report nonspecific building-related illnesses (2). There has been particular concern over potential health effects from exposure to fungi that produce mycotoxins (3). This concern has received much public attention (4) and has led to recommendations for the remediation of buildings based in part on the reported association of various health effects with exposure to mycotoxins (5).

In October 1998, the National Institute for Occupational Safety and Health (NIOSH) received a request from a local health department to assist in the evaluation of potential occupational exposure to fungi among workers at a hotel. A preliminary visual inspection of the hotel revealed that many areas of the building had widespread fungal growth, which appeared to be the result of frequent and severe water damage. Our subsequent activities included an environmental survey to assess potential fungal exposure and a pilot serologic survey to assess exposure of workers to mycotoxins. During the same period, clinical evaluation of a worker who developed chronic restrictive lung disease related to work duties in the hotel was performed by physicians not directly related to the NIOSH evaluation.

Case Presentation

Clinical evaluation. A 48-year-old white male, without a prior history of pulmonary disease or tobacco use, presented to his primary care physician in July 1998 with a 2-month history of dry cough and a 1-week history of fever and dyspnea. A chest exam revealed scattered rhonchi and crackles on the right side; an initial chest X ray was unremarkable. Over a period of several months, the patient was treated with several courses of azithromycin for a pneumonitis of uncertain etiology. Pulmonary function testing (Table 1) revealed a reduced forced vital capacity, (FVC), forced expiratory volume in the first second of exhalation ([FEV.sub.1]), and total lung capacity (TLC). The diffusing capacity corrected for alveolar volume (DLCO/VA) was normal.
Table 1. Pulmonary function testing of case patient
(height 74 in; weight 226 lb).

Date Dec 1998 Feb 1999 Aug 1999

FVC (L) 3.60 (66%) 3.48 (64) 3.31 (59)
[FEV.sub.1] (L) 2.91 (66%) 2.86 (65) 2.76 (63)
[FEV.sub.1]/FVC 0.81 (100%) 0.81 (99) 0.83 (106)
DLCO/VA (L/min/mmHg) 5.98 (139) 5.66 (131) ND
TLC (L) 5.0 (66) 4.8 (63) ND

Date Dec 1999 Feb 2000

FVC (L) 3.19 (57) 3.17 (57)
[FEV.sub.1] (L) 2.55 (58) 2.59 (59)
[FEV.sub.1]/FVC 0.80 (102) 0.82 (104)
DLCO/VA (L/min/mmHg) ND ND
TLC (L) ND ND

ND, not done. Values in parentheses are observed values
expressed as a percentage of predicted values.


Occupational history revealed that the patient had been a hotel manager at one hotel for the previous 14 years. Two months before initial presentation, he and a co-worker began assessing the extent of water damage and fungal growth in hotel rooms after hotel guests complained of water leakage and odors (Figure 1). These assessments included stripping wallpaper and making holes in walls; no respiratory protection was worn. Shortly thereafter, the patient reported the onset of a nonproductive cough. The patient performed these types of duties until the hotel was dosed in October 1998, 5 months after the initial assessment for water damage. However, as the primary supervisor for remediation of the damaged areas, the patient continued to enter all parts of the hotel. The patient had no prior history of exposure to farms or other environments where he would have been exposed to excessive amounts of fungi.

[ILLUSTRATION OMITTED]

Seven months after his initial presentation, the patient was referred for further evaluation. Dyspnea and cough were noted to be temporally related to his presence in the hotel. His white blood cell count and erythrocyte sedimentation rate were normal. His total IgE level was 346 IU/mL (normal range 0-99 IU/mL). Precipitating antibodies were positive only to Thermoactinomyces vulgaris. Specific IgG and IgE antibody responses to Stachybotrys sp. were not elevated. A repeat chest X ray was unremarkable, as was high-resolution computed tomography (HRCT) of the chest. A methacholine challenge test was performed and was equivocal [the cumulative dose of methacholine (in milligrams) that causes a 20% fall in [FEV.sub.1] = 25 mg/mL methacholine]. A repeat HRCT of the chest performed several weeks later with inspiratory and expiratory views was suggestive of an interstitial mosaic pattern consistent with bronchiolitis. Spirometry remained notable for a moderate restrictive defect (Table 1). Based on the patient's history and laboratory findings, he was advised to completely avoid all exposure to his workplace (11 months after the initial investigations for water damage).

The patient was subsequently referred for bronchoscopy. Transbronchial biopsy was unremarkable. Bronchoalveolar lavage (BAL) initially was not performed. The patient was given a provisional diagnosis of restrictive lung disease consistent with a chronic form of hypersensitivity pneumonitis, and treatment was begun with high-dose prednisone (120 mg/day). Repeat bronchoscopy (4.5 months after the initial bronchoscopy) revealed 12% lymphocytes in the BAL fluid (normal [is less than] 20%) and a CD4/CD8 ratio of 0.8 (laboratory reference [is greater than] 1). On the basis of continuing symptoms, evidence of advancing restrictive lung disease (despite removal from the workplace), and concern over the side effects of prednisone, treatment with methotrexate was initiated at 10 mg/week and was subsequently increased to 7.5 mg twice weekly as the prednisone was gradually decreased. A repeat HRCT of the chest was normal. The patient's symptoms gradually improved, while his lung function remained stable (Table 1).

Environmental evaluation. Beginning in November 1998, we conducted environmental surveys (including bulk and air sampling) in a total of 19 rooms of the 10-story hotel. Rooms that had experienced water damage but that had not yet been remediated were chosen for sampling; the objective was to sample from a representative group of affected rooms. We collected 14 bulk samples of materials that appeared to be contaminated with fungi for analysis with culture techniques (all fungal samples were analyzed by P & K Microbiology Services, Inc., Cherry Hill, NJ) (6). Using previously described methods (6,7), we collected 18 samples to be analyzed for mycotoxins (specifically trichothecenes, atranones, griseo-fulvins, and phenylspirodrimanes), which can be produced by Stachybotrys chartarum (synonyms atra or alternans) and other fungi.

We collected air samples over a 2-day period using culturable and nonculturable methods. Concentrations of culturable airborne fungi were determined for 14 interior building locations and 1 outdoor location using the Andersen single-stage viable cascade impactor (Andersen Instruments, Smyrna, GA) at a calibrated flow rate of 28.3 L/min. We used the Air-O-Cell (Zefon Analytical Accessories, St. Petersburg, FL) at a calibrated flow rate of 15 L/min (6) to determine airborne concentrations of total spores (nonculturable method) at 13 locations throughout the building at the same locations as the culturable samples and at an outdoor location.

Fungal concentrations from the bulk material samples ranged from 8.8 x [10.sup.4] to 5.2 x [10.sup.7] colony forming units (CFU) per gram of material. The predominant fungi identified included Acremonium sp., Alternaria sp., Aspergillus niger, Aspergillus sydowii, Mucor sp., Penicillium sp., Phoma sp., Stachybotrys chartarum, Ulocladium chartarum, and yeasts. Among the identified fungi, Aspergillus sp., Penicillium sp., and Stachybotrys chartarum are known to be capable of producing mycotoxins. Mycotoxins produced by Stachybotrys chartarum (or Memnoniella echinata) were identified in 8 of 18 samples. The complex trichothecenes, satratoxin and roridin, produced by Stachybotrys chartarum, were found in minute quantities. Atranones, spirocyclic compounds (phenylspirodrimanes) produced by Stachybotrys chartarum and M. echinata, and epidechlorogriseofulvin, produced by M. echinata, were also identified.

Results of the culturable air samples are presented in Table 2. Two of the samples were overloaded with fungal growth so colonies could not be counted; results in Table 2 reflect the 12 samples that could be counted. In water-damaged areas, Penicillium sp. and Aspergillus sp. were the predominant genera detected. Stachybotrys was identified from 5 of 12 sampling locations. Results of the nonculturable techniques were consistent with those obtained by culturable sampling, with Stachybotrys identified from 13 of 14 sample locations.
Table 2. Results of air sampling for culturable fungi (n = 12).

 Median indoor Outdoor Predominant(c) Predo-
Agar concentration concen- genera/species minant(c)
media(a) (CFU/ tration indoors genera
 [m.sup.3] (b) (CFU/[m. outdoors
 sup.3])

Cornmeal 1,200 (294-2,690) 380 Penicillium Clados-
 agar sp. (100)(d) porium sp.
 Aspergillus
 sp. (83)
 Cladosporium
 sp. (100)
 Stachybotrys
 chartarum (42)
Dichloran 1,350 (319-2,745) 419 Penicillium Clados-
 glycerol sp. (100) porium sp.
 Aspergillus
 sp. (100)
 Cladosporium
 sp. (100)

(a) Cornmeal agar is a selective nutrient medium to promote the
growth of Stachybotrys species; dichloran glycerol is a selective
nutrient medium to promote the growth of low-moisture tolerating
fungi (i.e., xerophiles). (b) Values in parentheses indicate range.
(c) Genera most frequently found across all samples. (d) Values in
parentheses indicate the percentage of samples in which each fungus
was found.


Laboratory evaluation. Because there are currently no useful biological monitoring techniques to assess exposure to mycotoxins, we conducted a pilot serologic evaluation using a test under development to identify specific IgG and IgM antibodies to roridin (a tricothecene mycotoxin known to be produced by several different fungi including Stachybotrys species). Tricothecene mycotoxins are potent irritants and may act as hap-tens, which bind constitutive proteins exerting an immune response similar to what has been described for other xenobiotics. De novo biosynthesis of antibodies from mycotoxin exposure has been shown for related mycotoxins such as aflatoxins found in food (8). In addition, cows exposed to mycotoxins in their feed have been shown to produce anti-mycotoxin antibodies (9). Roridin-A IgG antibodies, generated in animals, have been shown to be specific for macrocyclic tricothecenes (roridin is a type of macrocyclic tricothecene) (10).

In a study approved by the NIOSH Human Subjects Review Board, personnel lists of former hotel employees (total of 90 full- or part-time employees) were reviewed with hotel management to determine exposed (persons who had routinely worked in the fungi-contaminated areas) and unexposed (persons who had worked in areas found not to be grossly contaminated with fungi) workers. Employee recruitment was difficult because the hotel was closed at the time of our evaluation and employees were no longer employed at the hotel. Eight employees agreed to participate in the survey, including six exposed and two unexposed employees. The two hotel employees who participated in the discovery and initial mitigation of the water problem (including the hotel manager), and who were the persons most highly exposed to the fungal contamination, were included among the six exposed employees. After informed consent was obtained, a serum sample was collected from each participant. A brief questionnaire to assess job duties, medical history, and current symptoms was also administered to participants. We did not perform clinical examinations of study participants.

We performed enzyme-linked immuno-sorbent assays (ELISA) for roridin-hemisuccinate-human serum albumin (RH-HSA)-specific IgG antibodies on each serum sample. Fifty microliters of a 50 [micro]g/mL solution of RH-HSA was placed in each well and incubated overnight at 4 [degrees] C. Each well was then washed three times with phosphate-buffered saline (0.02 M phosphate buffer, pH 7.4) containing 0.91 M sodium chloride and Tween; a similar wash was repeated between all subsequent steps. Aliquots (200 [micro]L) of each diluted serum sample (1:10 in 5% bovine serum albumin-deionized water) were added to the wells and allowed to incubate at room temperature for 2 hr. After washing, 100 [micro]L of goat anti-human IgG or IgM (whole molecule) alkaline phosphatase conjugate (Sigma Chemical Co., St. Louis, MO) was added to each well and incubated for 2 hr at room temperature. The plates were again washed and 100 [micro]L of 0.6 mM disodium p-nitrophenyl phosphate (Sigma Chemical Co.) substrate solution, diluted in alkaline glycine buffer (0.05 M glycine and 0.5 mM magnesium chloride, pH 10.4), was added. After 10-15 min, the reactions were read on an automated ELISA plate reader. Each serum was tested in triplicate. We used seven stored sera obtained from unrelated NIOSH studies (from persons living in the same geographic area as the hotel but with no known contact to this hotel or excessively moldy environments) as assay controls. A response was defined as positive if a subject's serum optical density (OD) was greater than the assay control sera's mean OD + 3 SD.

The participants in the survey included three males and five females. The median length of employment at the hotel was 4 years (range: 1-14 years). Persons considered exposed worked in housekeeping, maintenance, or supervisory jobs, whereas the two unexposed persons worked in the bar/restaurant area. Among the eight sera samples, two had elevated IgG antibody titers to RH-HSA. The two individuals with elevated levels included one who was considered exposed and one who was considered unexposed. The hotel manager (case patient) did not have an elevated antibody level. No exposed or unexposed individuals gave evidence of specific IgM antibodies to RH-HSA.

Although exposed workers reported a spectrum of symptoms, some of which were reported to improve away from work, none of the workers were identified during our interview as having a clinical illness similar to that of the case patient. We did not perform systematic clinical evaluations of survey participants.

Discussion

Fungi are ubiquitous in the environment, and most individuals are exposed to them on a daily basis. Many fungi are capable of producing mycotoxins, which suggests that most people have some level of regular exposure to mycotoxins. An important aspect of evaluating whether health effects may be related to mycotoxin exposure is documentation of exposure (11). This is difficult because there are currently no reliable exposure indicators for mycotoxins. The standard used to associate health effects to mycotoxin exposure is the measurement of mycotoxins in bulk samples obtained from materials such as walls, ceiling tiles, and air ducts (12,13). Although the identification and quantification of several mycotoxins has been recently accomplished using mono-clonal antibodies and enzyme immunoassays, these methods have had limited use in field evaluations (10,14-16). The pilot serologic survey of this investigation was not able to distinguish between exposed and unexposed workers in a building heavily contaminated with mycotoxin-producing fungi. Although this laboratory testing did yield evidence that individuals may make specific IgG antibodies to roridin, the source of the exposure that led to this response cannot be determined from our data. Further studies are needed to determine the validity and specificity of this antibody testing in humans.

This case report emphasizes the importance of a careful occupational and environmental history because earlier recognition and avoidance of exposure to the suspected causal antigens may have reduced the degree of the patient's pulmonary disease. Furthermore, this case illustrates the complexity of establishing a definitive relationship between a specific illness and exposure to bioaerosols in general, or to any specific component of a bioaerosol (such as a mycotoxin).

In this case, the worker who developed chronic lung disease was likely exposed to an unusually high concentration of airborne fungi while investigating water incursion into the building. Although a specific diagnosis or cause of his pulmonary disease could not be confirmed, environmental sampling revealed heavy growth and airborne dissemination of many fungi, including several known to cause hypersensitivity pneumonitis (HP) (17,18). This worker fulfilled several of the major criteria required for the diagnosis of HP (19), including chronic respiratory symptoms compatible with HP, prolonged exposure to a putative antigen, and recurrence of symptoms upon reentry into the contaminated workplace. Although there was no absolute lymphocytosis on BAL, the CD4/CD8 ratio was decreased, which is consistent with HP.

The difficulty in making a definitive diagnosis of HP is due in part to the incomplete understanding of the pathogenesis of this disorder (20). A diagnosis of HP is further complicated because HP can present in acute, subacute, or chronic forms (21,22). Prolonged, low-dose exposure to inciting agents has been thought to predispose to a more chronic presentation (21). The clinical manifestations of the chronic form of HP, which often include cough and dyspnea without the systemic manifestations more commonly seen in the acute form (20,21), are compatible with the case patient's presentation.

Figure 2 provides an algorithmic approach that can be helpful in the clinical evaluation of a person who, based on a history and physical examination, is suspected of having an illness associated with bioaerosol exposure. After infectious processes are appropriately evaluated and found to be unlikely, then further evaluation is warranted. Hypersensitivity illnesses that must be considered in such an evaluation can be categorized broadly as having asthmatic or pneumonitis features, although there may be considerable overlap between the two. Although inhalation fevers (e.g., humidifier fever) do not manifest primarily as respiratory illness, they should also be considered in the differential diagnosis. Detailed reviews related to the diagnosis of these illnesses are available to supplement the broad algorithm presented here (23).

[ILLUSTRATION OMITTED]

In the last several years, reports have implicated exposure to Stachybotrys chartarum as being associated with acute pulmonary hemorrhage/hemosiderosis among infants or children (24). However, in a recent extensive review, the Centers for Disease Control and Prevention (13) concluded that evidence from currently available studies is not sufficient to support an association between acute pulmonary hemorrhage/hemosiderosis and exposure to Stachybotrys chartarum, and that further investigation of acute pulmonary hemorrhage/hemosiderosis in infants is needed. Our findings reinforce the difficulty investigators have had in attempting to determine actual exposure to mycotoxins.

Conclusion

Building-related illnesses include a variety of recognized disease entities that are characterized by objective clinical findings related to specific exposures in the indoor environment (2). These illnesses are preventable if greater efforts at improving building design, construction, indoor environmental controls, and maintenance to prevent or reduce exposure to potential etiologic agents are implemented. The clinical and environmental evaluations we have presented emphasize the need for further research involving biomarkers and health effects related to bioaerosol exposure. Such research should focus on identifying acceptable levels of indoor airborne microorganisms and mycotoxins and developing better methods for assessing their effects on human health. In the absence of tools specific for evaluation of possible mycotoxin-related illness, the clinical evaluation of suspected building-related respiratory illness should follow standard guidelines.

REFERENCES AND NOTES

(1.) Dales RE, Burnett R, Zwanenburg H. Adverse health effects among adults exposed to home dampness and molds. Am Rev Respir Dis 143:505-509 (1991).

(2.) Menzies D, Bourbeau J. Building-related illnesses. N Engl J Med 337(21):1524-1531 (1997).

(3.) ACGIH. Bioaerosols: assessment and control. Cincinnati, OH: American Conference of Governmental Industrial Hygienists; 1999.

(4.) Mann A. Mold: A Health Alert. USA Weekend Online Special Reports (serial online), 5 December 1999. Available: www.usaweekend.com/99_issues/ 991205/991205mold.html [cited February 2000].

(5.) New York City Department of Health. Guidelines on Assessment and Remediation of Fungi in Indoor Environments. Available: www.ci.nyc.ny.us/html/doh/ html/epi/moldrpt1.html [cited 17 April 2001].

(6.) Martinez K, Wallingford K. Unpublished data.

(7.) Jarvis BB. Macrocyclic tricothecenes. In: Mycotoxins and Phytoalexins (Sharma RP, Salunkhe DK, eds). Boca Raton, FL:CRC Press, 1991;361-421.

(8.) Autrup H, Seremet T, Wakhisi J. Evidence for human antibodies that recognize an aflatoxin epitope in groups with high and low exposure to aflatoxins. Arch Environ Health 45(1):31-34 (1990).

(9.) Gelev I, Dimitrov K, Tomova A. Immunological activity of the blood sera from cattle with chronic mycotoxicosis. Vet Med Nauki 23(4):16-24 (1986).

(10.) Martlbauer E, Gareis M, Terplan G. Enzyme immunoassay for the macrocyclic trichothecene roridin A: production, properties, and use of rabbit antibodies. Appl Environ Microbiol 54:225-230 (1988).

(11.) Fung F, Clark R, Williams S. Stachybotrys, a mycotoxin-producing fungi of increasing toxicologic importance. J Toxicol Clin Toxicol 36(1-2):79-86 (1998).

(12.) Johanning E, Biagini R, Hull D, Morey P, Jarvis B, Landsbergis P. Health and immunology study following exposure to toxigenic fungi (Stachybotrys chartarum) in a water-damaged office environment. Int Arch Occup Environ Health 68:207-218 (1996).

(13.) CDC. Update: Pulmonary hemorrhage/hemosiderosis among infants--Cleveland, Ohio, 1993-1996. MMWR 49(9):180-184 (2000).

(14.) Dietrich R, Schneider E, Usleber E, Martlbauer E. Use of monoclonal antibodies for the analysis of mycotoxins. Natural Toxins 3:288-293 (1995).

(15.) Schneider E, Usleber E, Martblauer E, Dietrich R, Terplan G. Multimycotoxin dipstick enzyme immunoassay applied to wheat. Food Addit Contam 12(3):387-393 (1995).

(16.) Hack R, Martblauer E, Terplan G. Production and characterization of monoclonal antibodies to the macrocyclic tricothecene roridin A. Appl Environ Microbiol 54(9):2328-2330 (1988).

(17.) Solley GO, Hyatt RE. Hypersensitivity pneumonitis induced by Penicillium species. J Allergy Clin Immunol 65(1):65-70 (1980).

(18.) Yoshida K, Ueda A, Yamasaki H, Sato K, Uchida K, Ando M. Hypersensitivity pneumonitis resulting from Aspergillus fumigatus in a greenhouse. Arch Environ Health 48(4):260-262 (1993).

(19.) Schuyler M, Cormier Y. The diagnosis of hypersensitivity pneumonitis. Chest 111(3):534-536 (1997).

(20.) Cormier Y. Hypersensitivity pneumonitis. In: Environmental and Occupational Medicine (Rom E, ed). Philadelphia: Lippincott-Raven; 1998;457-465.

(21.) Richerson H. Hypersensitivity pneumonitis. In: Organic Dusts: Exposure, Effects, and Prevention (Rylander R, Jacobs RR, eds). Ann Arbor, MI:Lewis Publishers, 1996;139-160.

(22.) Fink JN, Lindesmith LA, Horvath EP. Hypersensitivity pneumonitis. In: Occupational Medicine (Zenz C, Dickerson OB, Horvath EP, eds). 3rd ed. Philadelphia: Mosby, 1994;205-212.

(23.) Bernstein IL, Chan-Yeung M, Malo JL, Bernstein DI, eds. Asthma in the Workplace. 2nd ed. New York:Marcel Dekker, 1999.

(24.) CDC. Update: Pulmonary hemorrhage/hemosiderosis among infants--Cleveland, Ohio, 1993-1996. MMWR 46:33-35 (1997).

Douglas Trout,(1) Jonathan Bernstein,(2) Kenneth Martinez,(1) Raymond Biagini,(3) and Kenneth Wallingford(1)

(1) Division of Surveillance, Hazard Evaluation and Field Studies, National Institute for Occupational Safety and Health, Centers for Disease Control and Prevention, Cincinnati, Ohio, US; (2) Division of Immunology, Allergy Section, University of Cincinnati College of Medicine, Cincinnati, Ohio, USA; (3) Division of Applied Research and Technology, National Institute for Occupational Safety and Health, Centers for Disease Control and Prevention, Cincinnati, Ohio, USA

Address correspondence to D. Trout, NIOSH, 676 Columbia Parkway, R-10, Cincinnati, OH 45226 USA. Telephone: (513) 841-4558. Fax (513) 458-7105. E-mail: DTrout@cdc.gov

We thank W. Rath for assistance in the clinical evaluation.

Received 18 December 2000; accepted 5 February 2001.
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Publication:Environmental Health Perspectives
Date:Jun 1, 2001
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