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Environmental Medicine: Integrating a Missing Element into Medical Education (1995)
Institute of Medicine (IOM)

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. "Case Study 40: Community Oubreaks of Asthma Associated with Inhalation of Soybean Dust." Environmental Medicine: Integrating a Missing Element into Medical Education. Washington, DC: The National Academies Press, 1995.

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Environmental Medicine: Integrating a Missing Element into Medical Education

During 1987 a coincidence between the unloading of soybeans in the harbor and outbreaks of asthma was observed. In this study we investigated the association between the unloading of products in the harbor, particularly soybeans, and the occurrence of asthma epidemics during the years 1985 and 1986.

METHODS
Identification of Asthma-Epidemic Days

All daily emergency room admissions of Barcelona residents with asthma were recorded during 1985 and 1986. Data were collected from the clinical records of the four largest urban hospitals, which account for approximately 90 percent of the emergencies in the city. An emergency room admission for asthma was defined as a visit during which any asthma-related diagnosis was recorded.14 “Asthma” refers to a disease in which wide variations in resistance to flow in the airways of the lungs occur over short periods.17

The present study included only patients over 14 years of age, because no abnormal increases in the number of cases of acute severe asthma in childhood had ever been observed in the pediatric emergency services in Barcelona.14,15

An “unusual asthma day” was defined as a day on which the number of emergency room visits was so high that the probability that such a number or a higher one was the result of chance was 0.025 or less. This probability was calculated by assuming a Poisson distribution, with the 15-day moving average representing the number of cases expected.18

An “asthma-epidemic day” was defined as an unusual asthma day on which the cases were clustered on an hourly basis. An “hourly cluster” was defined as the occurrence in one four-hour period of so many emergency visits for asthma that the probability that such a high number of visits was the result of chance was 0.05 or less. The four-hour periods were selected on the basis of the distribution of cases during asthma outbreaks. This probability was calculated by the Knox and Lancashire approximation19 to the scan method.20

Data on Products Unloaded at the Harbor

All products identified as having been loaded or unloaded during at least one asthma outbreak were studied. We recorded the days on which each product was loaded or unloaded during 1985 and 1986. In the case of soybeans, additional variables were examined, including the use of two harbor silos (A and B) for soybean storage,

Table 1. Emergency Room Admissions during Outbreaks of Asthma in Barcelona, 1985–1986.

DATE

TOTAL DAILY ADMISSIONS

ADMISSIONS WITHIN A 4-HOUR PERIOD

 

ACTUAL

EXPECTED*

P VALUE

ACTUAL

P VALUE

1985

7/10

17

5.6

<0.001

9

<0.001

8/21

12

3.9

<0.001

8

<0.01

9/10

14

5.3

<0.01

8

0.017

9/12

24

5.8

<0.001

13

<0.001

9/13

17

5.3

<0.001

7

0.016

9/23

17

4.8

<0.001

7

<0.01

1986

1/21

96

11.8

<0.001

49

<0.001

5/6

34

6.9

<0.001

10

<0.01

5/7

15

6.3

<0.01

12

<0.001

9/17

33

6.8

<0.001

10

<0.001

11/11

54

10.5

<0.001

23

<0.001

11/24

32

7.7

<0.001

22

<0.001

11/25

18

6.9

<0.001

9

0.015

*Values are the number of admissions expected on the basis of a 15-day moving average.

Table 2. Association between Asthma Epidemic Days (“Asthma Days”) and Various Products That Were Unloaded in the Harbor, over the 730-Day Period Studied.

PRODUCT

UNLOADING

NO UNLOADING

RISK RATIO

95 PERCENT CONFIDENCE INTERVAL

 

TOTAL DAYS

ASTHMA DAYS

TOTAL DAYS

ASTHMA DAYS

 

Soybeans

262

13

468

0

UH*

7.17-UH*

Wheat

30

3

700

10

7.0

2.33–20.99

Cement

503

12

227

1

5.42

0.89–32.00

Potassium chloride

511

11

219

2

2.36

0.55–10.04

Petroleum

56

2

674

11

2.19

0.51–9.39

Phosphates

217

6

513

7

2.03

0.70–5.84

Gas

229

6

500

7

1.87

0.65–5.42

Coal

200

4

530

9

1.18

0.37–3.78

Fuel oil

153

3

577

10

1.13

0.32–4.06

Cotton

406

7

324

6

0.93

0.32–2.74

Coffee

305

5

425

8

0.87

0.29–2.64

Minerals

276

4

454

9

0.73

0.23–2.34

Gasoline

182

2

548

11

0.55

0.13–2.39

Chemicals§

548

8

182

5

0.53

0.18–1.58

Corn

136

1

594

12

0.36

0.05–2.53

Butane

141

1

589

12

0.35

0.05–2.40

*UH denotes unquantifiably high.

Value for one day is missing.

Including pyrite, perlite, bauxite, and granite.

§Including acetone, ethylene, kerosene, latex, perchloroethylene, sulfuric acid, styrene, and vegetable oils.

the form of the soybeans (in bulk, or as derivatives in the form of meal or pellets), and the country of the port of origin.

Aerobiologic and Meteorologic Data

During three nonconsecutive outbreaks—on November 11, 1986, February 8, 1987, and September 7, 1987—particles were collected in small samplers with cellulose ester filters21 placed in the district bordering the harbor, where most cases had occurred. Morphologic analysis was performed by optical microscopy on mineral oil-mounted slides. Lugol’s solution was used for starch staining, and Coomassie blue solution for the detection of protein.22,23 Soybean samples, collected from the hold of the ship that had unloaded soybeans during the two most recent documented outbreaks (September 4 and 7, 1987), were examined by optical microscopy and transmission and scanning electron microscopy.22,23 Meteorologic information was collected on epidemic days from four stations in different parts of the city and a fifth at the airport, 5 miles to the southwest.

Statistical Analysis

For each product unloaded, a risk ratio was calculated between the probability of an asthma epidemic on the days when the product was being unloaded and the probability of an epidemic on the days when it was not being unloaded. The unit of observation and analysis was the 24-hour day.

Confidence intervals for the risk ratios were estimated by the Miettinen method.24 When there was a zero in one cell of the two-by-two table, the lower limit of the confidence interval was calculated with use of the exact confidence-limit test25; in such a case, the null hypothesis was also tested with Fisher’s exact test.26 Evaluations of the independent effect of each product on the occurrence of asthma epidemics, with control for the other products, were carried out with use of the Mantel-Haenszel method.27

RESULTS

Thirteen of 23 “unusual asthma days” identified during the study period had hourly cluster patterns

Page
702
Front Matter (R1-R12)
Executive Summary (1-4)
1 Introduction (5-13)
2 Curriculum Content (14-21)
3 Implementation Strategies (22-43)
4 Changing Medical Education (44-51)
5 Concluding Remarks (52-53)
References (54-58)
Appendixes (59-60)
A: Taking an Exposure History (61-96)
B: Medical School Courses and Clerkships: Access Points for Integrating Environmental Medicine (97-120)
C: Case Studies in Environmental Medicine (121-138)
Case Study 1: Arsenic Toxicity (139-163)
Case Study 2: Seasonal Arsenic Exposure from Burning Chromium-Copper-Arsenate-Treated Wood (164-167)
Case Study 3: Asbestos Toxicity (168-188)
Case Study 4: Benzene Toxicity (189-207)
Case Study 5: Beryllium Toxicity (208-223)
Case Study 6: Cadmium Toxicity (224-243)
Case Study 7: Fetal Death Due to Nonlethal Maternal Carbon Monoxide Poisoning (244-248)
Case Study 8: Carbon Tetrachloride Toxicity (249-266)
Case Study 9: Chlordane Toxicity (267-288)
Case Study 10: Chronic Reactive Airway Disease Following Acute Chlorine Gas Exposure in an Asymptomatic Atopic Patient (289-290)
Case Study 11: Chromium Toxicity (291-311)
Case Study 12: Cyanide Toxicity (312-331)
Case Study 13: Dioxin Toxicity (332-348)
Case Study 14: Ethylene/Propylene Glycol Toxicity (349-371)
Case Study 15: Formalin Asthma in Hospital Staff (372-373)
Case Study 16: Gasoline Toxicity (374-394)
Case Study 17: Hantavirus Pulmonary Syndrome: A Clinical Description of 17 Patients with a Newly Recognized Disease (395-401)
Case Study 18: Lead Poisoning from Mobilization of Bone Stores During Thyrotoxicosis (402-409)
Case Study 19: Lead Toxicity (410-435)
Case Study 20: Legionaires' Disease: Description of an Epidemic of Pneumonia (436-444)
Case Study 21: Mercury in House Paint as a Cause of Acrodynia: Effect of Therapy with N-Acetyl-D, L-Penixillamine (445-449)
Case Study 22: Mercury Toxicity (450-472)
Case Study 23: Methanol Toxicity (473-492)
Case Study 24: Methylene Chloride Toxicity (493-511)
Case Study 25: Paint Remover Hazard (512-515)
Case Study 26: Fatal Outcome of Methemoglobinemia in an Infant (516-517)
Case Study 27: Nitrate/Nitrite Toxicity (518-537)
Case Study 28: An Outbreak of Nitrogen Dioxide-Induced Respiratory Illness Among Ice Hockey Players (538-541)
Case Study 29: Pentachlorophenol Toxicity (542-557)
Case Study 30: Aldicarb Poisoning: A Case Report with Prolonged Cholinesterase Inhibition and Improvement After Pralidoxime Therapy (558-561)
Case Study 31: Cholinesterase-Inhibiting Pesticide Toxicity (562-584)
Case Study 32: Infertility in Male Pesticide Workers (585-587)
Case Study 33: Pesticide Food Poisoning from Contaminated Watermelons in California, 1985 (588-595)
Case Study 34: Poisoning of an Urban Family Due to Misapplication of Household Organophosphate and Carbamate Pesticides (596-604)
Case Study 35: Polynuclear Aromatic Hydrocarbon (PAH) Toxicity (605-621)
Case Study 36: Polychlorinated Biphenyl (PCB) Toxicity (622-638)
Case Study 37: Ionizing Radiation (639-673)
Case Study 38: Radon Toxicity (674-694)
Case Study 39: Residential Radon Exposure and Lung Cancer in Sweden (695-700)
Case Study 40: Community Oubreaks of Asthma Associated with Inhalation of Soybean Dust (701-706)
Case Study 41: Tetrachloroethylene Toxicity (707-726)
Case Study 42: Toluene Toxicity (727-743)
Case Study 43: Occupational Asthma Due to Toluene Diisocyanate Among Velcro-like Tape Manufacturers (744-749)
Case Study 44: 1,1,1-Trichloroethane (750-766)
Case Study 45: Trimethyltin Encephalopathy (767-771)
Case Study 46: Trichloroethylene Toxicity (772-792)
Case Study 47: Vinyl Chloride Toxicity (793-811)
Case Study 48: Work-Related Disorders of the Neck and Upper Extremity (812-813)
Case Study 49: Contact Dermatitis in Surgeons from Methylmethacrylate Bone Cement (814-816)
Case Study 50: Skin Lesions and Environmental Exposures: Rash Decisions (817-861)
Case Study 51: Acoustic Trauma Caused by the Telephone: A Report of Two Cases (862-867)
Case Study 52: Behavioral and Audiologic Manifestations of Noise-Induced Hearing Loss (868-871)
Case Study 53: Reproductive and Developmental Hazards (872-892)
Case Study 54: Childhood Asthma and Indoor Enviromental Risk Factors (893-903)
Case Study 55: Populations at Risk From Particulate Air Pollution - United States, 1992 (904-908)
D: Resources: Agencies, Organizations, Services, REferences, and Tables of Environmental Health Hazards (909-970)
E: Committee and Staff Biographies (971-975)