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

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. "Case Study 46: Trichloroethylene Toxicity." 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
  1. No further studies are indicated for TCE exposure. A workup for fatigue may indicate additional tests.

  2. Based on limited evidence from animal studies, researchers believe teratogenicity does not occur at environmental TCE levels. Invasive procedures are not justified on the basis of the drinking water contamination.

  3. No, a recent survey of infections in children under 3 years of age over a September to March period found an average of 2.5 total infections and more than one episode of otitis media per child (1.4 episodes per child for those in day care). Over 3% of the children in day care were hospitalized for tympanostomies. (Reference: Bell DM, Gleiber DW, Mercer AA, et al. Illness associated with child day care: a study of incidence and cost. Am J Public Health 1989;79:479–84.) The child described in the case study appears to have an above-average rate of infections, but they are not frequent enough to suggest immunologic impairment.

  4. No, immunocompetence tests are not appropriate because no evidence of immune function abnormalities has been found in similar situations. Nevertheless, physicians may be asked to explain further why they are not performing the tests on their patients. Two references that may be of value are (1) Kahn E, Letz G. Clinical ecology: environmental medicine or unsubstantiated theory? Ann Intern Med 1989; 2:104–6; and (2) American College of Physicians. Clinical ecology. Ann Intern Med 1989;2:168–78.

    If it had been indicated, laboratory evaluation of immunologic host-defense defects would consist of three phases. The preliminary screening is a complete blood count with differential smear and quantitative immunoglobulin levels. These tests, together with history and physical examination, will identify more than 95% of patients with primary immunodeficiencies. The second phase of testing consists of readily available studies including B-cell function (such as antibodies, response to immunization), T-cell function (skin tests, contact sensitization), and complement levels. The first two phases combined will detect most immunodeficiencies amenable to conventional treatment with gamma globulin or plasma. The third phase (in-depth investigation) consists of testing induction of B lymphocyte differentiation in vitro, stimulated by pokeweed mitogen and histologic and immunofluorescent examination of biopsy specimens; T-cell surface markers; assays of T-cell helper or killer cell functions; and functional assays using appropriate target cells. It is inappropriate to perform these latter tests on environmentally exposed patients except for epidemiologic research.

    Primary immunodeficiency is suspected in an infant who has repeated upper respiratory tract or other infections. It is also suspected if repeated infection occurs in a child who has had little exposure to infectious agents, or any child with unusual infections, incomplete clearing of infections, growth failure, hepatosplenomegaly, or features associated with specific immunodeficiency disorders, such as ataxia or telangiectasia. The child described in the case study has none of these indications.

  5. EPA has not issued an emission standard for TCE. Assuming discussions with the owner or operator of the shop adjacent to the day-care center have not been effective in reducing the level of ambient TCE, the community’s air pollution control center should be notified. States may allow this control under the jurisdiction of local air pollution control districts, county health departments, or other local agencies. The agency responsible for enforcement of air standards should be contacted to investigate possible release of TCE onto the day-care center property.

Page
792
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)