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

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. "Case Study 32: Infertility in Male Pesticide Workers." 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

COMPARISON OF NON-VASECTOMISED D.B.C.P. WORKERS WITH VERY LOW (GROUP A) AND NORMAL (GROUP B) SPERM-COUNTS*

Group

No. of subjects

Age (yr)

Exposure (yr)

Sperm-count (×106/ml)

F.S.H. (mI.U./ml)

L.H. (mI.U./ml)

Testosterone (ng/dl)

A

11

32·7±1·6

8·0±1·2

0·2±0·1§

11·3±1·8

28·4±3·3

459±35

B

11

26·7±1·2

0·08±0·02

93±18

2·6±0·4

14·0±2·8

463±31

*All results given as mean±standard error of mean.

‡Difference between groups A and B significant at P<0·001.

†Difference between groups A and B significant at P<0·01.

§9 workers with 0 sperm/ml, 2 with 1×106/ml.

cesses affecting production or transport of sperm. Infection, trauma, varicocele, cryptorchidism, exposure to toxic agents, and autoimmunity have all been cited as causes of male infertility, but in many cases the cause is unknown.1

We have investigated infertility observed in a group of men working in a California pesticide factory. Although the connection has not been proved beyond doubt, the cause in these cases seems to be exposure to the nematocide, 1,2-dibromo-3-chloropropane (D.B.C.P.).

BACKGROUND

The company employing the affected men manufactures fertilisers and ammonia, and it formulates pesticides for agricultural and household use. In the latter process, workers mix, dilute, and repackage technical-grade pesticides obtained from primary chemical manufacturers. Some 100 different chemicals are used in the formulation of approximately 200 different products, including organophosphorus compounds, halogenated hydrocarbons, and carbamates. The products manufactured or formulated vary with market demand. Since 1962 the company has regularly formulated D.B.C.P. in a special agricultural chemical division (A.C.D.). For several years before the infertility was brought to our attention men working in the A.C.D. had become increasingly aware that few of them had recently fathered children. After a preliminary evaluation of 5 men had revealed oligospermia or azoospermia, other male employees were studied in more detail.

METHOD
Subjects

All 39 employees in the A.C.D. took part in the study. There were 3 supervisors, 24 production workers, 4 maintenance mechanics, 2 clerks, and 6 laboratory workers. 36 of the group were men, 11 of whom had had vasectomies. There was no way of determining exact differences in chemical exposure received by the production workers, since they were assigned interchangeably to different tasks. Thus, only the length of time they had worked in the A.C.D. could be used as a measure of exposure.

Procedure

Each of the 39 employees was asked to complete a medical-history questionnaire, and one of us (D.W.) then asked each subject specific questions about his or her reproductive system. All participants were also examined thoroughly.

Semen samples were obtained from all non-vasectomised men and were promptly taken to the laboratory for determination of sperm-count, motility, and morphology. Other laboratory tests done on all 39 subjects included urinalysis, complete and differential blood counts, blood chemistry, T3-resin uptake, and assays for serum-levels of thyroxine, testosterone, follicle stimulating hormone (F.S.H.), and luteinising hormone (L.H.). The last four tests were done by radioimmunoassay. All the analyses were performed by the clinical and endocrine laboratories of Alta Bates Hospital.

Early in the investigation it became apparent that infertility was associated with length of time worked in the A.C.D. To examine the relationship between exposure duration and sperm-count, we first excluded from our original group 3 women, 11 vasectomised men, and 3 men with sperm-counts between 10 million and 30 million. This left 11 men with indisputably low sperm-counts (≤1 million, group A) and 11 men with normal sperm-counts (≥40 million, group B). We then compared these two groups by age, time worked in the A.C.D., and serum L.H., F.S.H., and testosterone levels. After the preliminary evaluations, bilateral open testicular biopsies were performed on 9 volunteers representing a spectrum of chemical-exposure times and sperm-counts within the A.C.D.

RESULTS

None of the 3 women had had abnormal menstrual cycles, and all had borne children. None of the men had loss of libido, difficulty with erection or ejaculation, loss or altered distribution of facial or body hair, testicular atrophy, epididymal abnormalities, gynæcomastia, or abnormalities of the prostate. 3 had varicoceles, but all 3 had previously fathered children. 7 of the 36 men had never fathered children.

Some of the production workers had occasional symptoms, such as mild headache, nausea, light-headedness, and weakness, when formulating some organophosphorus pesticides. Symptoms due to irritation of the upper respiratory tract were also mentioned by some as being associated with their work in the manufacture of certain thiocarbamate compounds. No other important information was brought to light by the history or physical examination of any of the subjects. The few hepatic, renal, hæmopoietic, and thyroid abnormalities revealed by laboratory studies were consistent with previous medical problems.

The relationship of length of chemical exposure (time of employment) to sperm-count was striking (see table). Workers with sperm counts ≤1 million had been exposed at least three years. None with sperm-counts above 40 million had been exposed for more than three months.

The 2 men in group A (see table) who were not azoospermic showed great reduction of sperm motility and increases in abnormal forms. Sperm motility and morphology were normal in all the men in group B. The mean age in group A was slightly higher than in group B, but differences in testicular function would not be expected to result from this small age difference.

The mean level of F.S.H. was significantly higher in group A—a finding consistent with the severe impairment in spermatogenesis in these individuals.1,2 F.S.H. levels in group B were in a range comparable with those in a larger, unexposed population of male employees from elsewhere in the company who are now being studied. Group A also had a higher mean L.H. level. This also probably represents a response to testicular damage, although serum-testosterone levels were comparable in the two groups. Thus, the stimulus for the increase in L.H. is not known. Studies are planned to evaluate testi-

Page
586
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)