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

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. "Case Study 47: Vinyl Chloride 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. The differential diagnosis at this point might include the following:

    acute hepatitis (viral or alcohol-, chemical-, or drug-induced)

    chronic active hepatitis (viral types B, C, D)

    granulomatous or neoplastic infiltration

    Among causes of acute hepatitis, alcohol is less likely because the SGPT level is greater than the SGOT level. With normal alkaline phosphatase, primary biliary cirrhosis or bile duct obstruction are also not probable.

  2. Viral hepatitis should be ruled out by serologic testing. Imaging studies such as CAT, MRI, or liver-spleen scan would be appropriate. An angiogram would be helpful if angiosarcoma is suspected. Direct indicators, such as urinary thiodiglycolic acid or vinyl chloride levels, would be helpful only if exposure to vinyl chloride were recent. Negative results in tests measuring these direct indicators, however, would not rule out drinking water contamination, for example.

  3. The differential diagnosis now most likely includes cirrhosis and malignancy. Hepatic angiosarcoma is not normally prominent in the differential diagnosis of liver function abnormalities. However, the test results thus far and the fact that this is a nonoccupational exposure to vinyl chloride (nonmalignant liver injury has not been reported in environmental exposures) make angiosarcoma of the liver a possibility. In the case of angiosarcoma of the liver, hepatic arteriography would reveal a characteristic appearance, with displacement of hepatic arteries, and a blush and “puddling” during the middle of the arterial phase. Percutaneous liver biopsy is contraindicated in cases of angiosarcoma because of the vascular nature of the tumor and the possibility of complicating thrombocytopenia or significant bleeding; laparoscopic biopsy would be more appropriate.

  4. Hepatic angiosarcoma grows rapidly and carries a poor prognosis. If untreated, most patients die within 6 to 12 months after diagnosis. The only long-term survivors have had the tumor successfully resected. As a precaution you might suggest that the patient ventilate new cars before entering them for prolonged periods and drive with the window open to maintain ventilation. Until the drinking water at his home is tested, the family should use bottled water to avoid any possible exposure there.

  5. Since the rest of the family and the nearby community may have had similar exposure to vinyl chloride, all should undergo periodic testing of transaminases, alkaline phosphatase, and serum bile acids to detect latent chemical injury. If these tests or an ICG clearance rate are positive for hepatic injury, biopsy may also be helpful. If the drinking water is not contaminated and there is no vinyl chloride waste disposal source to contaminate the water in the future, the exposure to the family and community has likely terminated.

  6. Your local, county, or state health department should be contacted and notified of the possible case. Because hepatic angiosarcoma is an extremely rare disease, even one case would alert public health authorities to a potential risk to the community around this plant. Your report should initiate case-finding investigations among the former workers at the plant as well as in the community. Public health authorities may also want to evaluate the potential for groundwater contamination around the plant.

Sources of Information

More information on the adverse effects of vinyl chloride and the treatment and management of vinyl chloride-exposed persons can be obtained from ATSDR, your state and local health departments, and university medical centers. Case Studies in Environmental Medicine: Vinyl Chloride Toxicity is one of a series. For other publications in this series, please use the order form on the back cover. For clinical inquiries, contact ATSDR, Division of Health Education, Office of Director, at (404) 639–0730.

Page
811
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)