SAFETY--Potential Hazards from Exposure to Elemental Mercury and Mercury Salts In Reply Refer To: July 8, 1982 EGS-Mail Stop 412 WATER RESOURCES DIVISION MEMORANDUM NO. 82.112 Subject: SAFETY--Potential Hazards from Exposure to Elemental Mercury and Mercury Salts Although most people know that elemental mercury and mercury salts are virulent poisons, it is commonly presumed that the danger is from oral ingestion. However, mercury is extremely volatile and the vapors are readily absorbed through the respiratory tract or unbroken skin. Mercury acts as a cumulative poison because the rate of elimination by body functions is low. If mercury is spilled in a gage house or field vehicle, concentrations hundreds of times greater than the maximum allowable can be attained. Air saturated with elemental mercury vapor at 2O degrees C contain a concentration which exceeds the maximum allowable concentration of 0.01 mg/m3 (milligrams per cubic meter) by about 1250 times. The saturation vapor concentration increases with increasing temperature. At 60 degrees C, the maximum allowable concentration is exceeded by nearly 25,000 times. Thus, mercury must be handled with the utmost regard for airborne contamination. According to the Hydrologic Instrumentation Facility (HIF), about 300 pounds per year of elemental mercury is shipped to Districts for replacement of mercury lost from bubble gages. Another use of elemental mercury by WRD is in thermometers, and to a lesser extent in mercury-filled barometers. We have no good estimate of how much elemental mercury is in storage or use by WRD at this time. WRD also uses mercury chloride in tablet form for water-quality sample preservation. Each tablet contains about 13 milligrams of mercuric chloride in a sodium chloride matrix. Possible sources of exposure to mercury vapor include the following: o Mercury spilled in a field vehicle or gage house will result in a continuing source of vapor. A drop or two of mercury can produce unsafe conditions. On a hot day the vapor concentration inside the vehicle or gage house may greatly exceed safe levels. o Mercury stored in metal or glass containers cannot pass through the container walls, but when stored in certain plastic containers, including polethylene bottles, the vapor can pass through the container walls to some degree. Mercury is shipped by HIF in polyethylene bottles. There are, however, mitigating factors that also need to be considered. o The concentrations that are attainable in a closed environment are reached slowly. In a partially- or well-ventilated environment the maximum vapor concentration will be considerably lower than saturation. 2 o The maximum concentration criteria are based on a lO-hour exposure. There are few situations where WRD fieldmen would have a continuous lO-hour exposure to very high mercury-vapor concentrations. Safety measures that should be inmediately instituted are as follows: o Mercury and mercuric chloride should be stored in airtight metal containers. An easy solution is to store the plastic bottles of elemental mercury and the preservative tablet packets in army surplus ammunition cans. When used for storage these cans, which have airtight, rubber-gasketed lids, should only be opened out of doors or in a fume hood. Cans should be labeled with an appropriate hazard warning. o No manometers should be transported with mercury in them. o Broken thermometers and waste mercury should also be stored in an airtight metal container. When necessary, the container can be shipped to the nearest Central Laboratory for mercury recovery. The disposal container should also be labeled with an appropriate hazard warning. o Before entering a gage house that is known or suspected to have been con- taminated by mercury, field personnel should fan the door back and forth for a minute or two to exchange the stagnant air with fresh air. The time spent in the ventilated gage house should result in negligible exposure because the vapor concentration increases slowly. o Special care should be taken to prevent contamination of vehicles. They are the most likely places for near-saturation conditions to exist. Fanning of doors or opening windows for the first few minutes after re-entering a contaminated vehicle that has been parked in the sun should quickly remove vapor-laden air. Open windows, or operation of air conditioners or heaters should keep air exchange at a maximum once the vehicle is underway. The air conditioner and heater should be operated in the "outside air" mode as opposed to the "recirculate" mode. o No special safety precautions are necessary for water samples that have been preserved with tablets containing mercuric chloride beyond the normal mercury recovery and disposal procedures presently being performed at the Central Laboratories. Please observe the above safety measures. Thomas A. Buchanan Assistant Chief Hydrologist for Operations Distribution: A, B, S, FO, PO Key Words: Potential Hazards, Elemental Mercury, Mercury Salts, Mercury "This memorandum does not supersede any existing memorandum."