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Tracker Autumn 2003

Kirby Griffin, MD DIMENSIONS OF CARE
Medical Surveillance of Pesticide Workers

by Kirby Griffin, MD

Restrictions on the use of persistent organochlorine pesticides have resulted in an increase in the use of the organophosphate pesticides. The organophosphates are less persistent in the environment but have a greater acute toxicity. I would like to discuss issues of medical and biologic monitoring for workers with potential exposure to organophosphate pesticides. I will avoid discussion of clinical manifestations and the treatment of organophosphate poisoning [which was covered in Dr. Steven Schumann’s article in Volume 5, Number 4 of the Tracker—Ed.], and focus on medical surveillance of pesticide workers.

Background

Organophosphates are inhibitors of cholinesterase. Cholinesterase is the enzyme that causes the metabolism of acetylcholine. Acetylcholine is the neurotransmitter at parasympathetic and myoneural junctions, in autonomic ganglia, and in the brain. Poisoning from organophosphates results when the inhibition of cholinesterase leads to an accumulation of acetylcholine at the nerve synapses, causing overstimulation. If the process continues, there is eventual paralysis of neural transmission. Workers who apply and mix pesticides are at risk of systemic poisoning. Agricultural workers are also at risk from exposure to these pesticides in the field. Both acute and chronic poisoning may occur. Biological monitoring is useful in assessing the effectiveness of personal protective equipment, including respirators; it is also useful in assessing work practices and compliance with safety procedures.

Designing a Monitoring Program

A comprehensive medical monitoring program for potential exposure to organophosphate pesticides would include physical examinations, air sampling, measurement of post-exposure urinary alkylphosphates, and determination of acetylcholinesterase levels. However, such a comprehensive program may be too expensive or otherwise impractical for many companies. Therefore, medical monitoring should adhere to the following recommended hierarchy:

  1. first priority is to monitor plasma and RBC
    cholinesterase levels;
  2. next priority is to monitor urinary alkylphosphate levels;
  3. third priority is to perform environmental sampling;
  4. physical examinations are the final step in the standard comprehensive monitoring program.

Monitoring Cholinesterase

Measurement of the pesticide itself in blood is not useful for monitoring because of the rapid metabolism of the pesticide. Organophosphates are hydrolyzed by the liver within minutes to hours of exposure. Instead, measurement of cholinesterase activity in blood is the established procedure for monitoring organophosphate exposure. Although there is a wide range of cholinesterase levels in a population, each individual maintains a relatively stable level of cholinesterase activity in blood unless there are interfering factors to upset that stable level. There are several different laboratory methods available to measure cholinesterase activity in blood, and different units of measurement are utilized by different laboratories. Whatever laboratory you use, I strongly recommend that you verify that all determinations are made using the same units of measurement.

Following exposure, the cholinesterase level in an individual’s blood decreases. In order to detect that decrease in cholinesterase activity, it is necessary to have a baseline, pre-exposure determination of cholinesterase activity. Several medical conditions may cause depression of cholinesterase activity, including infectious hepatitis, chronic gastritis, chronic pneumonitis, malnourishment, gastric carcinoma, and renal cancers. Cholinesterase can also be depressed by exposure to carbamate pesticides. RBC (erythrocyte) cholinesterase is considered the more accurate reflection of the degree of synaptic cholinesterase inhibition. Plasma pseudocholinesterase determinations, however, are easier to obtain. Both RBC and Plasma cholinesterase need to be assessed. The two tests have different meanings and must be evaluated together to assess an individual’s exposure. Plasma cholinesterase is more labile than RBC cholinesterase, but it recovers much more quickly since it is manufactured in the liver. RBC cholinesterase is a better indicator of acute depression, but it recovers slowly. RBC cholinesterase recovers as new red blood cells are regenerated at a rate of about 1% per day. It is recommended that baseline cholinesterase levels be measured in duplicate by the same laboratory. If the two determinations differ by 15% or more, then a third determination needs to be made. Blood samples drawn for cholinesterase determination should be ICED. An un-iced specimen is prone to loss of activity while in transit to the laboratory. Category I pesticides are those with an oral toxicity of < 50 mg/kg in laboratory animals and Category II pesticides are those with an oral toxicity of < 500 mg/kg. Employees working with category I or II organophosphate pesticides should undergo a baseline cholinesterase activity determination followed by a first monitoring test not more than three days after working with the pesticide for seven days. Additional monitoring for new employees should occur every 30 days. After an employee has three monitoring tests, the frequency may be reduced to every 60 days unless medical evaluation indicates a more frequent test interval is appropriate.

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Monitoring Urinary Alkylphosphates

Measurement of alkylphosphate metabolites in urine is perhaps the most sensitive measurement of organophosphate exposure. The most common metabolites found in urine are diethylphosphate (DEP), diethylphosphorothioate (DETP), diethylphos-phorodithioate (DEDTP), dimethylphosphate (DMP), dimethylphosphorothioate (DMTP), and dimethylphos-phorodithioate (DMDTP). These metabolites are found at peak levels about three days after exposure and they may be detected in urine up to six or seven days after exposure. Although measuring alkylphosphate metabolites in urine is a sensitive method of assessing exposure, there is an innate difficulty in using this method as the base form of monitoring because of the sophisticated analytical method required. In some situations this technique can be utilized with impressive results, but it does not replace cholinesterase monitoring.

Monitoring of Workers

Chronic exposure to organophosphate pesticides may cause symptoms that are nonspecific and resemble illnesses like flu, simple fatigue, or heat exhaustion. A clinical picture of weakness, loss of appetite, malaise, or "orange pickers’ disease" (a severe dermatitis), is cause for evaluation of the work environment and work practices. Small, repeated exposures to organophosphates may gradually depress cholinesterase activity to relatively low levels, with little, or no, symptomatology. In general, symptoms for acute poisoning occur after the serum cholinesterase is depressed to 50% of normal. In mild poisoning, the cholinesterase activity is depressed to 20–50%; in severe poisoning, activity is 10% or less of normal. Depression of an individual’s cholinesterase activity to 70% of baseline indicates significant exposure. If depression of activity is 60% of baseline, the individual must be removed from exposure and must be monitored medically until activity levels return to 80%. For cases of acute poisoning, treatment is started based on clinical findings and patient history and should not be delayed until cholinesterase determinations are available. Continuing clinical decisions, however, need to be based on the current cholinesterase level compared to the individual’s baseline. Because of the need for such information, we recommend that individuals with potential exposure to organophosphate carry their baseline cholinesterase level with them, and we issue a small laminated card with the individual’s baseline cholinesterase levels for this purpose. The card is kept in a wallet or purse and is immediately available if needed. This provides a solution to the ubiquitous problem of trying to find someone’s baseline cholinesterase levels in the company’s files or the doctor’s office, particularly after hours, or on weekends, etc.

Regulations for organophosphate pesticides vary from state to state, but there is no OSHA standard, per se, for these materials. It is important to check your own state regulations in regard to monitoring and reporting requirements. Perhaps the strongest regulations are found in California, where workplace monitoring is required if a worker’s RBC or plasma cholinesterase falls below 80% of normal.

The growing use of organophosphate pesticides has given rise to a growing need for biological monitoring for workers with potential exposure to organophosphate pesticides. Now is the time to establish medical monitoring procedures for workplace exposures.

Happy Monitoring!

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[Return to Autumn 2003 main page]

Articles in the Tracker may be printed and/or photocopied for personal use. To reprint an article in print or on-line media, include the following in the reproduced copy: "This article originally appeared in the Occupational Health Tracker, Vol.6, No.3. Reprinted with permission of Occupational Health Research, www.systoc.com."


About the author:
Kirby Griffin, MD, is a board-certified specialist in Occupational Medicine and has 22 years of experience in this field. At St. Vincent Hospital in Portland, Oregon, Dr. Griffin was the Medical Director of Occupational Health Services and established that institution’s Center for Occupational Health. In 1989 he founded Northwest Occupational Health Associates. Dr. Griffin has extensive experience in medical surveillance and biologic monitoring. Additionally, he has been a course instructor and speaker at numerous seminars and national meetings and is a past president of the Northwest Association of Occupational and Environmental Medicine. You may reach Dr. Griffin via e-mail: NOHAOCCMED@AOL.com.

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