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

Page
394
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Environmental Medicine: Integrating a Missing Element into Medical Education

water supply during showering, dishwashing, laundering, and other activities does not indicate significant exposure by this route. To evaluate this exposure route, levels of gasoline constituents in the household drinking water should be measured and more information about the storage-tank leak should be obtained.

The potential for gasoline or hydrocarbon-based solvent exposure through the patient’s hobby should be explored carefully. Detailed information should be obtained regarding the patient’s use of gasoline as a solvent to clean his hands or automobile parts. What is the frequency and duration of exposure? Is gasoline stored in open containers in the garage? Is the garage ventilated while he is working? If there is any indication of recreational gasoline abuse, his symptoms could be related to overexposure.

  1. Several of the hydrocarbons in gasoline can produce CNS toxicity. The most likely components, based on their percentage volume, would be toluene and xylene. n-Hexane can also cause CNS, as well as peripheral nerve, toxicity; however, the low concentration of n-hexane in gasoline makes it an unlikely candidate.

  2. Nonspecific symptoms can be very difficult to evaluate. If there is no objective evidence of disease and no laboratory or physical abnormalities, the clinician should consider other contributory factors. Are the readjustment stresses to the new community? Are there financial or marital difficulties or other external considerations?

  3. If a careful history indicates that the patient has had recent onset of frequent headaches, as well as other neurobehavioral symptoms, a thorough neurologic examination should be performed. If deficits are demonstrated, further neurologic workup, such as scans, EEG, and neurobehavioral testing, is indicated. If gasoline toxicity is a consideration, liver and kidney function should be evaluated, although abnormalities are unlikely unless there has been severe acute overexposure.

  4. No, the measured results are well within normal limits and do not indicate a toxic exposure. Given the potential variability of water analyses, it would be appropriate to confirm these insignificant levels by performing two or three analyses.

  5. Occasional misuse of liquid gasoline to clean hands or machinery parts is unlikely to cause significant toxicity, although the practice may present a serious fire or explosion hazard. Repeated skin contact can lead to defatting of the skin and dermatitis. The dermatitis on the patient’s hands in this case study could indeed be from dermal contact with liquid gasoline.

    Prolonged and repeated misuse of gasoline as a solvent or cleaning agent can, however, cause significant toxicity. If the patient has frequent extensive skin contact with liquid gasoline or is frequently exposed to high concentrations of gasoline vapors via open containers of gasoline in a confined space, his headaches, confusion, and forgetfulness could be from gasoline overexposure.

  6. The single most important intervention in this case would be to counsel the patient on the hazards of gasoline and to eliminate further misuse. Removal of exposure would most likely lead to a complete resolution of symptoms without further sequelae. In a few cases, some residual deficits might persist.

Page
394
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)