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

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. "Case Study 28: An Outbreak of Nitrogen Dioxide-Induced Respiratory Illness Among Ice Hockey Players." 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

resurfaced for 10 minutes every hour; during games, the ice was resurfaced for 5 minutes after each 15-minute period. A Plexiglas shield surrounded the ice to protect spectators from airborne hockey pucks. Two ventilation systems were used in the arena: air vents for passive air exchange and exhaust fans.

The ice resurfacer was powered by an internal combustion engine using propane fuel. If these engines are not properly tuned and the fuel mixture in the carburetor receives too little oxygen, elevated levels of carbon monoxide may be produced; if the mixture has too much oxygen, elevated levels of nitrogen dioxide may be produced.16

Ice arenas in Minnesota are required to measure ambient levels of carbon monoxide and nitrogen dioxide on a weekly basis during the months of operation. Measurements are taken 120 cm above the ice in the center of the arena. Ambient levels of nitrogen dioxide above 0.5 ppm are considered to be elevated and are required to be reported to the Minnesota Department of Health.

METHODS
Epidemiologic and Clinical Investigation

Questionnaires were administered to all hockey team members who attended the two games. In addition, cheerleaders and band members, who were present during the second game, were interviewed. Information was obtained on symptoms (including cough, hemoptysis, shortness of breath, dyspnea, chest pain, headache, and weakness), onset and duration of each symptom, general health status (including history of asthma or other respiratory problems), length of time in the arena, and location in the arena during the games (in the stands or on the ice). For hockey players, information also was obtained on position played and length of time on the ice. All interviews were completed within 10 days after attending a game at the arena. A case was defined as acute onset of cough, hemoptysis, or dyspnea during a hockey game or within 48 hours of attending a hockey game at the arena. Attack rates for teams were compared using standard univariate analysis.17

Spirometry was performed within 10 days of exposure and again at 2 months after exposure for all members from two hockey teams: team C (with a single exposure) and team D (with multiple exposures). Spirometry also was performed on members of a basketball team from one of the schools, which served as an unexposed group for comparison. Pulmonary function testing was performed at the high schools that the players attended using a portable spirometer (Microloop, Medical Graphics Corp, St Paul, Minn). The best result of three attempts was recorded. Intermountain Thoracic Society predicted values (which control for age, height, and weight) were used to determine results by percent of predicted.18

We reviewed medical records for hockey players who reported seeing a physician. Information was obtained on physical examination, chest roentgenogram findings, and treatment prescribed during initial and follow-up clinic visits.

Environmental Investigation

Air quality records at the ice arena were reviewed for the hockey season. No measurements had been obtained during the two games in question. Therefore, to simulate conditions during the games, the ice resurfacer was operated for 30 minutes and levels of nitrogen dioxide and carbon monoxide in the arena were measured. The use of the ventilation systems during the two games also was reviewed.

Survey of State Health Departments

To evaluate air quality monitoring in indoor ice arenas nationally, and to obtain an estimate of the number of ice arenas located in each state, a telephone survey of all 50 state health departments was conducted. The Ice Skating Institute of America, the US Figure Skating Association, and the National Hockey Association also were contacted to obtain estimates of the number of indoor ice arenas located in the United States.

RESULTS
Epidemiologic Investigation

Questionnaires were completed on 92 (94%) of 98 hockey players with a single exposure (teams A, B, and C), 34 (100%) of 34 players with multiple exposures (team D), 16 (76%) of 21 cheerleaders, and 25 (96%) of 26 band members. Overall, 116 cases were identified.

Symptoms reported by at least 30% of the 69 case hockey players who had a single exposure are listed in Table 1. A typical case was characterized by acute onset of cough and dyspnea within 1 hour of playing a game at the arena. At the time of onset, the cough was frequently so severe that players had difficulty driving home after the game. The mean duration of cough was 16 days in players with acute exposure. The dyspnea was described most often as “aching lungs” or “a tightness in the chest” that made it difficult to inhale deeply. Hemoptysis was characterized by blood-tinged sputum. Similar symptoms were noted among players on team

Table 1.—Symptoms Reported by 69 Case Patients With a Single Exposure to Nitrogen Dioxide, Minnesota, 1987

Symptom

No. (%) of Patients

Cough (acute onset)

67 (97)

Shortness of breath (exertion)

45 (65)

Chest pain

44 (64)

Shortness of breath (rest)

31 (45)

Headache

31 (45)

Hemoptysis

24 (35)

Weakness

22 (32)

D. However, because many of the players on team D complained of chronic cough, they were not included as acute cases. The mean duration of cough for players on team D was 41 days. Eighteen (14%) of 126 hockey players reported a history of reactive airway disease (asthma). Of these, 16 (89%) reported an exacerbation of their asthma symptoms after playing at the arena.

Attack rates for the groups are listed in Table 2. Although the attack rate for acute onset of symptoms for members of team D was only 56%, 11 (73%) of 15 players on team D who did not have acute onset of symptoms admitted to chronic respiratory symptoms (primarily cough). The attack rates for cheerleaders (who were on the ice) and band members (who sat in the stands) were similar to the attack rates for hockey players on teams A, B, and C. However, hockey players and cheerleaders were 3.2 times as likely as band members to develop hemoptysis (P=.05, Mantel-Haenszel χ2 test). Length of time spent in the arena, length of time spent on the ice, and position played did not substantially increase the risk of developing hemoptysis.

Results of initial and follow-up spirometry performed on team C (single exposure), team D (multiple exposures), and the unexposed comparison group of basketball players are shown in Table 3. Overall, no differences in five lung function parameters at initial testing or at 2 months’ follow-up (when comparing percent of predicted) were noted between the two hockey teams and the basketball comparison group.

Ninety-two hockey players sought medical attention; abnormal findings and treatment prescribed at the initial clinic visit are shown in Table 4. Ten patients had follow-up physician visits; none had ongoing signs or symptoms noted.

Environmental Investigation

Mechanics at the ice arena reported that the ice resurfacer had not been running properly during the preceding 6 months and that it had been emitting

Page
539
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)