Mercury: Your Health and the Environment: A Resource Tool
Health Canada Mercury Issues Task Group
Table of Contents
- Q.7 What are the main sources of mercury exposure?
- Q.8 Are Canadians at risk from methyl mercury exposure?
- Q.9 What uses of metallic (elemental) mercury in the home increase mercury exposure?
- Q.10 What types of workplace environments potentially increase mercury exposure?
- Q.11 Is there any method of testing that will determine individual exposure to mercury?
- Exposure through the Consumption of Fish
- Q.12 How do mercury releases end up in fish?
- Q.13 Does eating fish increase my exposure to mercury?
- Q.14 What advice would Health Canada offer Canadians concerning fish consumption?
- Q.15 What measures has Health Canada taken to reduce exposure to mercury through fish consumption?
- Q.16 Are any fish species exempt from the mercury content restrictions?
- Q.17 What are the current Health Canada total intake limits for methyl mercury for Canadians?
- Exposure through Consumer Products
- Q.18 Which consumer products are known to contain mercury?
- Q.19 Why was mercury used in paints and what should I do about mercury-based paint in my home?
- Q.20 As an artist, how can I reduce exposure to mercury?
- Q.21 Does mercury in children's toys represent a hazard?
- Q.22 What can I do to manage mercury exposure in my home?
- Q.23 What happens when I use metallic mercury unsafely in the home?
- Q.24 What should I do with a mercury-containing product when it has reached the end of its useful life?
- Q.25 How should I clean up a mercury spill in my home (including a broken mercury fever thermometer)?
- Q.26 How much mercury is released from cigarette smoke?
- Q.27 What is the source of mercury in cigarettes?
- Exposure from Dental Amalgam and Thimerosal Vaccines
- Q.28 Should I avoid mercury amalgam dental fillings?
- Q.29 Should I have my existing mercury amalgam dental fillings replaced?
- Q.30 What is thimerosal and why is it used in vaccines?
- Q.31 If patients have a choice of vaccines, one with mercury or one without, which should they choose?
- Q.32 Why is the federal government not recommending removal of thimerosal vaccines from use if there is a concern?
- Q.33 What degree of mercury exposure has my six-month-old baby encountered from vaccines? Is there a health risk associated with this level of exposure?
- Q.34 Do children receive toxic levels of mercury from vaccines?
- Health Concerns
- Q.35 What happens to elemental mercury in the body and where does it accumulate?
- Q.36 What happens to inorganic mercury in the body and where does it accumulate?
- Q.37 What happens to methyl mercury in the body and where does it accumulate?
- Q.38 How long does it take to excrete mercury (all forms) from the body?
- Q.39 What are the health effects and symptoms of inorganic mercury exposure in adults?
- Q.40 What are the health effects and symptoms of methyl mercury exposure in adults?
- Q.41 What type of treatment exists to remove mercury from blood?
- Q.42 Should I be concerned about mercury concentrations in drinking water?
- Pregnant Women & Children
- Q.43 Why is mercury a special concern for pregnant and breastfeeding women?
- Q.44 Why are children and the developing fetus at a greater risk than adults for adverse health effects associated with mercury?
- Q.45 What are the health effects of metallic or inorganic mercury exposure in children?
- Q.46 What are the health effects associated with exposure to methyl mercury in children?
- Mercury in the Environment
- Q.47 How much does Canada contribute to worldwide mercury releases?
- Q.48 How are anthropogenic (human) mercury emissions transported through the atmosphere?
- Q.49 How is mercury transformed in the environment?
- Q.50 What is polar sunrise depletion?
- Q.51 How does mercury affect fish and wildlife?
- Q.52 Is mercury present in the air and at what concentration?
- Q.53 Is mercury present in dust and soil and at what concentration?
- Q.54 Is mercury present in precipitation and at what concentration?
- Q.55 Is mercury present in fresh water and at what concentration?
- Q.56 Is mercury present in sediment and at what concentration?
- Government Action on Mercury
- Q.57 What Canadian legislation pertains to the management of mercury?
- Q.58 What is the Government of Canada doing, in collaboration with provincial and international governments, to reduce mercury in the environment?
- Q.59 How is Health Canada helping to reduce mercury exposure?
- Q.60 Does Canada monitor the release of mercury into the environment from anthropogenic (human) sources?
- Q.61 Does Canada monitor levels of mercury in the environment?
- Q.62 What mercury research is supported by the Government of Canada?
- Q.63 Are consumer products regulated for acceptable levels of mercury?
- Q.64 What action has Health Canada taken to reduce mercury levels in paint used in the home?
- Q.65 Does Canada have regulations in place to control the amount of mercury in compost?
- Q.66 Does Canada have regulations in place to control mercury levels in mercury-containing fluorescent lamps?
- Q.67 Does Canada have regulations in place to control mercury releases from dental amalgam waste?
- Q.68 Does Canada have regulations in place to control mercury releases from base metal smelting?
- Q.69 Does Canada have regulations in place to control mercury emissions from waste incineration?
- Q.70 Does Canada have regulations in place to control mercury emissions from the Electric Power Generating Sector?
- Q.71 Does Canada regulate mercury-containing waste disposal at sea?
- Q.72 What actions has Health Canada taken to eliminate the use of mercury in fungicides?
- Sources of Information on Mercury
- Glossary of Terms
This compendium of commonly asked questions and answers is intended to provide key information to Canadians on the topic of mercury, human health and the environment. In this section, the following general questions and answers describe why mercury can be a problem.
Q1. What is mercury?
Mercury is a naturally occurring element found in the earth's crust with natural deposits generally found as a vermilion red ore called cinnabar. Mercury exists in three different forms: elemental, inorganic and organic.
- Elemental (Hg+ or Hg2+) or metallic mercury is a silvery, shiny liquid at room temperature that produces a colourless, odourless vapour at room temperature. The unique properties of elemental mercury, such as its ability to conduct electricity and its coefficient of expansion, make it useful for a variety of specialized uses, (e.g. temperature measurement in thermometers).
- Inorganic compounds can be formed when elemental mercury combines with elements such as sulphur, chlorine or oxygen. These compounds are usually known as mercury salts.
- Organic mercury compounds occur when elemental mercury combines with carbon and hydrogen.
In the environment, microorganisms (bacteria and fungi) and natural processes can change mercury from one form to another.
Q2. Why is mercury considered a health and environmental problem?
Mercury compounds can be toxic at low levels in the environment. The characteristics of mercury that make it a health and environmental problem are its toxicity and persistence in the environment, and its ability to accumulate and bioconcentrate as methyl mercury in fish and fish-eating predators such as large fish or loons (see Q.12). Mercury also moves over long distances on air currents and can be deposited on land and in rivers, lakes and oceans far from the source of release (see Q.12 & Q.48), therefore spreading the potential exposure to many more people.
Q3. What is methyl mercury?
Methyl mercury is an organic form of mercury. Biological processes, such as bacterial activity in plants and sediments on lake bottoms, in rivers and oceans, can transform elemental mercury to methyl mercury, the most bioaccumulative and toxic form. Levels of methyl mercury in animals increase up the food chain, from plankton to large fish, to birds and mammals, including humans. Once in the body, methyl mercury can affect many systems in the body, particularly fetal and adult nervous systems (see Q.35-46).
Q4. What are the main sources of natural mercury releases?
Mercury is released into the air, water and soils from a range of natural sources. These include volcanic eruptions, mercury-rich geologic zones and geothermal vents. Mercury is mobilized in the environment by natural weathering processes, forest fires and flooding.
Q5. What are the main sources of anthropogenic (human) mercury releases?
Mercury is released by a range of human activities, such as the burning of fossil fuels (particularly in coal fired power plants), mining and base metal smelting, the production of chlorine and sodium hydroxide in the mercury-cell chlor-alkali industry, cement production, and municipal and medical waste incineration. In addition, the improper disposal of mercury-containing products such as fluorescent light bulb tubes, high intensity discharge lamps, mercury vapour lamps, mercury fever thermometers and thermostats and dental amalgam waste can lead to the release of mercury from municipal landfills. Methyl mercury can also be generated by bacterial activity in submerged soil at new hydroelectric dam sites and from other flooded areas and be released to drainage systems.
Q6. Have mercury levels increased?
Relative to pre-industrial times, human activities have increased the amount of mercury circulating in the atmosphere, soils, and in lakes, streams and oceans by a factor of two to four. In Canada, mercury releases have declined since the 1980's, due to anti-pollution measures, particularly in the base metal smelting sector. In addition, the closure of all but one mercury cell chlor alkali facility in New Brunswick has assisted in reducing mercury releases in this sector. Although Canada and many other industrialized countries continue to substantially reduce mercury uses and releases from point source locations, these reductions are not generally reflected in lower environmental concentrations. This is mainly due to the persistent nature of mercury and the increased industrialization of other countries.
This section covers the various potentially hazardous sources of exposure to mercury such as exposure through the consumption of fish, the use of certain consumer products, dental amalgam and thimerosal vaccines. Exposure to mercury can occur as part of everyday activities through contact with water and soil, exposure to products containing mercury and even in the air we breathe.
Q7. What are the main sources of mercury exposure?
Because mercury occurs naturally in the environment at low levels, everyone is exposed to some level of mercury in air, water and food.
- In the general population, the major sources of exposure to mercury occur through the consumption of larger species of fish (see Q.12 - Q.17) and from dental amalgam (see Q.28 - Q.29).
- Exposure can also occur when mercury-containing products are broken and mercury is released or spilled at home or in the workplace. (See Q.22 - Q.25)
- Another potential source of exposure is the use of mercury in various cultural practices and hobbies, including some types of jewellery, such as glass pendant necklaces and some artist's paints (see Q.20).
- Minor methyl mercury exposure can occasionally occur from handling contaminated soil or drinking contaminated water (see Q.55).
Q8. Are Canadians at risk from methyl mercury exposure?
The Canadian population, in general, is not being subjected to an increase in methyl mercury exposure, but some people may have higher exposure than others.
- People who eat a lot of fish and marine mammals as part of their daily diet tend to have higher methyl mercury exposures, because the potentially high levels of methyl mercury found in some of these species can be passed on to humans.
- Scientific research suggests that it is the developing fetus and the breast-fed children of women who consume greater amounts of the larger species of fish during pregnancy and lactation who are the most susceptible to health problems (see Q.43 - Q.46).
Q9. What uses of metallic (elemental) mercury in the home increase mercury exposure?
Any use of metallic (elemental) mercury in the home can be dangerous. A number of unsafe household uses have been identified. These include:
- Sprinkling or spreading mercury in the house or car;
- Mixing mercury with water or other liquids and using this mixture as a washing solution;
- Burning mercury in candles for good luck (white magic);
- Hobbies: heating mercury on a stove to purify gold or silver;
- Using metallic mercury, often sold under the name "azogue", including placing it in a pouch worn around the neck, sprinkling it in the home, mixing it with bath water or perfume or placing it in devotional candles;
- Folk remedies: ingesting mercury (azogue) to treat constipation, colic or stomach ache (empacho), or;
- Playing with mercury as a novelty or carrying it as a charm.
Q10. What types of workplace environments potentially increase mercury exposure?
Workplaces and occupations that have a greater potential for elemental mercury exposure include:
- Manufacturers of electric equipment (mercury switches, dry cell batteries, mercury lamps, etc.), medical devices (thermometers, manometers, etc.) or automotive parts that contain mercury;
- Chemical processing plants that use mercury (production of chlorine, caustic soda, pesticides, biocides, slimicides and fungicides, latex and antifouling paints);
- Metal processing;
- Manufacturing plants producing explosive detonators;
- Waste incineration plants (municipal, medical and hazardous wastes), incinerators, landfills and crematoriums/cemeteries;
- Construction sites where building parts contain mercury (e.g. electrical switches, thermostats, thermometers, latex paints containing organomercurial fungicides, ship repair facilities);
- Medical facilities where equipment may contain elemental mercury (e.g. some blood pressure gauges, dental amalgams, thermometers, etc.); and
- Canada uses the Threshold Limit Values (TLVs) for Chemical Substances, as determined by the American Conference of Governmental Industrial Hygienists for national occupational health standards (Canada Labour Code and its Regulations). Federal regulations use the TLV's as amended from year to year, whereas most provinces use the TLV's as adopted for a specific year. For information on occupational exposure guideline limits, please refer to Q.58.
Q11. Is there any method of testing that will determine individual exposure to mercury?
Yes. Hair, blood or urine samples are typically tested to detect elevated mercury levels in the body, if there is a suspected exposure. These samples can be easily taken in a doctor's office. Analytical methods can detect inorganic mercury and/or total mercury (the difference being considered organic mercury). The test for elemental mercury is the same test as for inorganic mercury, interpretation of the result being dependent on the type of exposure. While these tests are useful in determining the concentration of mercury, they cannot determine the type of mercury exposure beyond inorganic (includes elemental) or organic mercury exposure.
If your doctor suspects metallic (elemental) mercury poisoning, he/she will obtain a complete occupational and environmental history and may test your blood and/or urine for elemental mercury.
- For acute effects resulting from exposure to high levels of elemental or inorganic mercury, physicians often test whole blood. Whole blood is an indicator of recent mercury exposure. For occupational exposure, whole blood is collected at the end of the last work shift of the work week.
- If exposure to low levels of elemental or inorganic mercury vapour occurs over a period of time, a urine sample is preferred. Urine is collected pre-shift.
- Hair samples provide a good method for the determination of the variation of mercury intake over a long period of time, if the hair is analysed by segments.
- The concentration of mercury detectable in blood and urine in the non-occupationally exposed population is dependent on the analytical procedure used to measure the mercury and the living environment of the subject.
- Blood levels in the occupationally unexposed population vary between 0.1 and 10 micrograms of mercury per litre of blood. A whole blood concentration of 15 micrograms per litre is considered to be the biological exposure index (BEI) for occupational exposure. Blood concentrations above 15 micrograms per litre should be followed up by a physician. Symptoms should not be present at the BEI concentration. The BEI concentration of 15 micrograms per litre is equivalent to 0.008 micromoles/decilitre.
- Urine samples, for the non-occupationally exposed population, typically have a concentration of elemental or inorganic mercury of less than 3 micrograms per litre. For the occupationally exposed population or for populations with exposure to unusually high environmental concentrations, the elemental or inorganic BEI concentration limit is set at 35 micrograms mercury per gram of creatinine. The BEI concentration of 35 micrograms per gram of creatinine is equivalent to 20 micromoles of mercury per mole of creatinine.
Exposure through the Consumption of Fish
The main pathway for methyl mercury intake in humans is through the consumption of certain species of fish. Canadians living in Northern Canada whose diet consists mainly of a greater proportion of fish and marine mammals are at a higher risk for methyl mercury exposure than Canadians in more southern areas.
Q12. How do mercury releases end up in fish?
Mercury that is released into the environment may be deposited into water where microorganisms can convert it to methyl mercury, a highly toxic form of mercury that can build up, or bioaccumulate, in living tissue. Small organisms and plants take up mercury as they feed and this mercury tends to accumulate in their tissues. As larger animals, higher up the food chain, consume these plants and organisms, methyl mercury is bioaccumulatedat a more concentrated level. The process continues as you move up the food chain, with levels of mercury increasing in larger, predatory species. This process is known as biomagnification.
Q13. Does eating fish increase my exposure to mercury?
- People who eat a lot of fish and marine mammals as part of their daily diet tend to experience higher methyl mercury exposure, because the potentially high levels of methyl mercury found in some of these animals can be passed on to humans.
- Scientific research suggests that it is the developing fetus and the breast-fed children of women who consume greater amounts of the older, predatory species of fish during pregnancy and lactation who are the most susceptible to health problems (see Q.43 - Q.46) (National Academy of Sciences, 2000).
Q14. What advice would Health Canada offer Canadians concerning fish consumption?
Health Canada gives the following advice concerning fish consumption:
- Consumers are advised to limit consumption of shark, swordfish and fresh or frozen tuna to a maximum of no more than one meal per week (excluding canned tuna, because these shipments are regularly tested and usually found to be well below the Health Canada guideline of 0.5 ppm), (see Q.15).
- For children, pregnant women and women of childbearing age, consumption of these fish should be limited to no more than one meal per month.
- For sport fish caught in local waters, consumers should be aware of any fish advisory from provincial and territorial authorities, and in some cases, the federal Department of Fisheries and Oceans) (see Q.73 for website details). However, the benefits of including fish in a well balanced diet cannot be overlooked:
Fish is an excellent source of high-quality protein and omega-3 fatty acids, and it is low in saturated fat.
Consumers must consider the significant beneficial health effects of including fish in their diet, and take a best-balanced approach to possible exposure to methyl mercury and fish consumption.
Q15. What measures has Health Canada taken to reduce exposure to mercury through fish consumption?
Canada has set guidelines for mercury levels in domestically produced and imported fish.
- The Food Directorate of Health Canada has established a guideline level of 0.5 parts per million (ppm) for total mercury in domestically produced and imported fish considered to be the major source of dietary exposure (see Q.14). This guideline is enforced by the Canadian Food Inspection Agency (CFIA). It was first set in the 1970's and is currently undergoing further evaluation by the Bureau of Chemical Safety, Health Canada.
- Shark, swordfish, and fresh and frozen tuna sold commercially in Canada can contain mercury at levels that are known to exceed the 0.5 ppm guideline. However, an occasional meal of these types of fish would not significantly contribute to overall mercury exposure. Canned tuna tends to contain lower levels of mercury than fresh and frozen tuna because different species of tuna are used for canning. These species tend to be smaller and therefore have lower accumulations of mercury.
- The CFIA regularly tests domestic and imported commercial fish and shellfish, both freshwater and marine, in order to enforce the mercury guideline.
- CFIA laboratory test results for mercury in canned tuna indicate that mercury levels will vary among species, but that these products consistently meet the guideline, with the lowest levels being found in light canned tuna (yellowfin and skipjack) (see Q.14).
Q16. Are any fish species exempt from the mercury content restrictions?
The Health Canada guideline for total mercury content in commercial fish species is 0.5 part per million (ppm). Large predatory fish species, such as swordfish, shark, and fresh and frozen tuna (not canned tuna) have been exempted from the 0.5 ppm mercury guideline. This means that the guideline does not apply to these fish, but instead a maximum consumption limit has been established by Health Canada for these species.
Although swordfish, shark, and fresh and frozen tuna (not canned tuna) are exempted from the 0.5 ppm guideline, CFIA tests these species as part of its overall contaminant monitoring program. Results from these tests are provided to Health Canada and used in their ongoing review of guidelines and exemptions. (see Q.14 & Q.73 - Health Canada Advisory: Information on Mercury Levels in Fish).
Q17. What are the current Health Canada total intake limits for methyl mercury for Canadians?
A provisional Tolerable Daily Intake (pTDI) of 0.47 microgram perkilogram of body weight perday for methyl mercury was established in 1972 by the Joint Food and Agriculture Organization/World Health Organization Expert Committee on Food Additives (JECFA) and was adopted by Health Canada. This level was reaffirmed in 1989 for the general population. However, through further studies, JECFA cautioned that pregnant women and nursing mothers were likely to represent a greater risk from the adverse effects of methyl mercury (WHO, 1989). This concern was shared by the bureau of Chemical Safety in the Foods Directorate of Health Canada and, in 1998, the Foods Directorate of Health Canada reviewed the new studies and lowered the maximum pTDI for methyl mercury to 0.2 microgram perkilogram of body weight perday for pregnant women, women of childbearing age and young children. A recent evaluation by JECFA (WHO, 2003) derived a similar value (pTWI of 1.6 microgram perkilogram of body weight perweek or 0.23 microgram perkilogram of body weight perday) to the Health Canada pTDI.
Exposure through Consumer Products
Q18. Which consumer products are known to contain mercury?
Despite its toxic nature, humans have used mercury in a range of products in order to take advantage of its unique properties to conduct electricity, measure temperature and pressure, and to act as a fungicide, preservative and disinfectant. These uses have been in decline in recent years.
Mercury-containing products currently used in Canada include the following:
- Fluorescent lamps, high intensity discharge lamps and mercury vapour lamps;
- Some fever thermometers;
- Some thermostats;
- Some electrical switches;
- Some medical equipment such as pressure sensing devices and blood pressure gauges;
- Dental amalgam;
- Disk ("button") batteries.
Other products that have been known to contain mercury in the past and that might still be in circulation, include:
- Lighted athletic shoes;
- Old latex and oil based paints;
- Vacuum gauges;
- Solvents, dyes and pigments;
- Wooden windows and doors;
- Barometers and manometers;
- Pottery and art objects;
- Pharmaceuticals including human and animal vaccines and cosmetics;
- Fungicides for seed and turf;
- Old toys, chemistry sets and scientific apparatus.
Also, note that mercury is no longer used in the manufacture of vinyl blinds, candles, shot, fishing jiggers or sinkers.
Q19. Why was mercury used in paints and what should I do about mercury-based paint in my home?
Mercury was used in paints as an anti-microbial pesticide or preservative in order to prevent mould growth. This practice ceased more than 10 years ago. It is possible that homes more than 10 years old have paint on their walls and/or ceilings that contains minute quantities of mercury. This should pose virtually no health risks to inhabitants of these homes. Once a mercury-containing paint has cured, the mercury is incorporated into the paint matrix and cannot be released.
There is no need to remove mercury-containing paint from homes where it has been applied. If there is any concern over the presence of mercury-containing paint on walls or ceilings, application of a fresh coat of new paint will seal in all of the layers of paint beneath it and provide some peace of mind.
When stripping old paint, follow the instructions and recommendations found in the following pamphlets in order to ensure safe working conditions.
Q20. As an artist, how can I reduce exposure to mercury?
Follow safe studio practices for reducing exposure to chemicals, such as the following:
- Do not eat, drink or smoke while using art materials;
- Always wash your hands carefully after using art materials;
- Use fume hoods or spray booths exhausting to the outside, or force the air to the outside by using fans;
- Be aware of the supplies you buy and, if available, obtain a Material Safety Data Sheet in order to ascertain the contents of the paint (mercury may be a preservative) used for arts and crafts.
- The following Health Canada webpage provides more information on precautionary practices for the artisan: http://www.hc-sc.gc.ca/english/iyh/products/arts.html
Q21. Does mercury in children's toys represent a hazard?
Health Canada's Consumer Product Safety Bureau is unaware of any manufacturers intentionally adding mercury to toys. If mercury were to be found in toys, it could represent a hazard, because children, especially under the age of three, tend to place objects in their mouths. In addition, the Hazardous Products Act prohibits the use of mercury in decorative or protective coatings applied to toys, equipment and other products destined for the educational or recreational use of children. The Consumer Product Safety Bureau has conducted surveys to ensure that toys do meet these requirements.
Q22. What can I do to manage mercury exposure in my home?
Although some consumer products such as electrical switches and fever thermometers still contain mercury, most products today can be manufactured without it. Because pollution prevention is preferable to pollution clean-up, consumers can help reduce mercury releases by identifying household items that might contain mercury, avoiding the purchase of mercury-containing products, and disposing of mercury-containing waste appropriately.
The best way to avoid mercury exposure from consumer products is to limit the presence of mercury-containing items in your home. Buy rechargeable batteries or batteries that are labelled "mercury free" or "no added mercury", and use digital or spirit (red) thermometers.
There is little chance for exposure to mercury when proper directions are followed for mercury-containing products. If unbroken, fluorescent light bulbs and mercury thermometers emit no mercury and are safe household items. If a breakage does occur, the risk of inhaling mercury vapour can increase, especially in enclosed indoor spaces with poor ventilation.
Q23. What happens when I use metallic mercury unsafely in the home?
At room temperature and especially when heated, elemental mercury produces a vapour that can cause serious lung damage and possible death if inhaled. In addition, as mercury cools, it condenses on household surfaces such as rugs, walls and furniture. These household surfaces can then continue to release low concentrations of mercury vapour slowly into the air. Mercury vapour is invisible, odourless and tasteless, and adults and children breathing this vapour at low levels for weeks or months will accumulate mercury in their bodies and may eventually become ill.
Q24. What should I do with a mercury-containing product when it has reached the end of its useful life?
Never discard mercury-containing products with household trash. Treat these items as hazardous waste and consult your local municipality for information on proper handling and disposal.
Q25. How should I clean up a mercury spill in my home (including a broken mercury fever thermometer)?
If mercury is burned, heated, sprinkled or spilled in the home, a poisonous gas can be produced, requiring a clean-up procedure. Mercury vapour is odourless and invisible, and special equipment is required to measure mercury concentrations in the home. A professional can determine the areas of the house that are affected by measuring the level of mercury vapour with special equipment, and by assessing how mercury was used in the house.
The amount of mercury found in household products does not usually lead to serious health problems and can often be cleaned up without the help of a trained professional. However, even small spills should be treated as hazardous and cleaned up with caution. Remember to report these spills to the local environmental health authorities. Depending on the size of the spill, hiring a Contractor to monitor mercury levels in air, and to conduct a professional clean-up, may be advisable. There are also commercially available small mercury spill kits that can be obtained. Never vacuum a mercury spill with a household vacuum cleaner. It will increase the vaporization of the mercury.
A few helpful hints to remember are:
- Do not put contaminated items in the washing machine;
- Do not vacuum the spill;
- Do not use a broom or a brush;
- Do not pour mercury down the drain; and
- Do not throw mercury or contaminated items in the garbage.
Risks to exposure from mercury can be minimized by taking the effective steps described in the Environment Canada website accessible through the following link:
Q26. How much mercury is released from cigarette smoke?
Cigarette smoke contains up to 11.5 nanograms of mercury per cigarette in mainstream smoke and up to 16.6 nanograms of mercury per cigarette in side stream smoke.
Q27. What is the source of mercury in cigarettes?
Mercury is taken into the plant primarily by the growing root and subsequently translocated to the leaves along with other nutrients. Mercury exists in the tobacco plant as a result of its deposition from the air, combined with the soil uptake of mercury. It is released in tobacco smoke as the cigarette burns, and exposure to tobacco smoke contributes to the total body burden of mercury.
Exposure from Dental Amalgam and Thimerosal Vaccines
Q28. Should I avoid mercury amalgam dental fillings?
Current evidence does not indicate that dental amalgam is causing illness in the general population. However, it is generally a good idea to reduce exposure to mercury if this can be achieved at a reasonable cost and without other adverse effects. Health Canada recommends non-mercury filling materials be considered for restoring the primary teeth of children where the mechanical properties of the material are suitable. Pregnant women and people who may have allergic hypersensitivity to mercury or who have impaired kidney function should avoid the use of dental fillings containing mercury amalgam.
Q29. Should I have my existing mercury amalgam dental fillings replaced?
Health Canada does not support removal of sound amalgam fillings in patients who have no indication of related adverse health effects. Individuals who have developed hypersensitivity to amalgam should replace existing mercury amalgam fillings with another material if their physician recommends this. Amalgam fillings should not be removed while a woman is pregnant because she might be exposed to mercury vapour during removal.
Q30. What is thimerosal and why is it used in vaccines?
Thimerosal is a preservative that contains mercury and it has been used in some vaccines and other products since the 1940's to prevent spoilage and contamination. Efforts are under way to eliminate thimerosal from product formulations, where possible.
Q31. If patients have a choice of vaccines, one with mercury or one without, which should they choose?
They should choose mercury-free vaccines, if they are available and if they are just as suitable as thimerosal vaccines. Patients should discuss this with their doctor and follow his/her advice. The most important consideration is that parents should not miss an opportunity to have their children immunized. Currently, the only thimerosal-containing vaccine in routine use in the infant immunization schedules of some Canadian jurisdictions is the hepatitis B vaccine.
Q32. Why is the federal government not recommending removal of thimerosal vaccines from use if there is a concern?
Making vaccines safer and more effective is a constant goal for the federal government and vaccine manufacturers. But decisions must be based on weighing the risks and benefits of each vaccine. In some cases, mercury-free alternatives may not be available or may not be as suitable as the thimerosal formulations. Missing vaccinations would put children at risk from disease. Since thimerosal vaccines contain only minute levels of mercury, the benefits of vaccination with them far outweigh the minimal risks associated with thimerosal.
Q33. What degree of mercury exposure has my six-month-old baby encountered from vaccines? Is there a health risk associated with this level of exposure?
There is little chance for a six month old to be exposed to mercury through vaccination. Most vaccines licensed in Canada do not contain thimerosal. Since 1994, all routine childhood vaccines, with the exception of the flu vaccine, administered in Canada have not contained thimerosal. Thimerosal is not added to single dose vaccines.
In Canada, vaccines to prevent the following diseases are used for routine immunization of children and do not contain thimerosal:
- tetanus (lockjaw)
- pertussis (whooping cough)
- rubella (German measles)
- measles (red measles)
- hepatitis B (available free to children only in some provinces and territories)
- Haemophilus influenzae type b disease
For immunization of infants against hepatitis B, parents or guardians in some provinces and territories have the choice of a thimerosal-free vaccine.
Q34. Do children receive toxic levels of mercury from vaccines?
No. Children who receive vaccines containing thimerosal may be exposed to minute levels of mercury, but these are very far below any toxic level.
In this section, health concerns resulting from mercury exposure in adults, pregnant women and children are discussed. Exposure to mercury mostly affects the nervous system, the cardiovascular system, the immune system, and the kidneys. Fetal mercury exposure can lead to neurodevelopmental problems in children.
The health effects of mercury in its various forms are well documented. For further consultation, the public health statement for mercury produced by the Agency for Toxic Substances and Disease Registry is available at the following site (PDF Version - 151 K):
Q35. What happens to elemental mercury in the body and where does it accumulate?
- Elemental mercury can enter the body by absorption through the skin, by absorption through the stomach if swallowed, or by inhalation. Absorption depends on the route of exposure (inhalation, ingestion or dermal).
- When mercury vapour is inhaled, the lung is the main site of absorption. Approximately 80% of the inhaled vapour enters the bloodstream and is rapidly transported to other parts of the body, including the brain and kidneys. It readily crosses the blood-brain and placental barriers. Elemental mercury, in the blood of pregnant women, may be passed on to the developing fetus.
- If small amounts of metallic mercury are ingested from a broken oral thermometer, less than 0.01% of the mercury will be absorbed by the body through the stomach or intestine. A condition such as a bleeding ulcer in the gastrointestinal tract can increase the rate of absorption into the bloodstream.
- Once in the body, elemental mercury can stay there for weeks or months. Most of it will accumulate in the kidneys and, to a lesser extent, in the brain, where it is readily converted to an inorganic form and remains there for a long time. More mercury is deposited in the brain after exposure to elemental mercury than after exposure to inorganic mercury compounds.
Q36. What happens to inorganic mercury in the body and where does it accumulate?
- Inorganic mercury salts or compounds do not generally vaporize at room temperatures and, upon inhalation, these compounds are not as likely to enter your body as easily as inhaled metallic mercury vapour.
- When inorganic mercury compounds are ingested, generally less than 10% is absorbed through the intestinal tract; however, under certain conditions, such as bleeding ulcers, up to 40% can be absorbed into the body through the lesion in the stomach and/or intestines.
- Smaller amounts of inorganic mercury can be absorbed through the skin, but ingestion is the main pathway into the body.
- Absorbed inorganic mercury accumulates mostly in the kidneys and does not cross placental or blood-brain barriers as easily as elemental or methyl mercury. It is, however, accumulated in placental tissues.
- In a nursing mother, some of the inorganic mercury from her body will be passed on to her child through her breast milk.
Q37. What happens to methyl mercury in the body and where does it accumulate?
- When fish or other foods contaminated with methyl mercury are consumed, approximately 95% of the methyl mercury is absorbed through the stomach and intestinal tract, then transferred to the blood stream and distributed throughout the body.
- Only small amounts of methyl mercury can be absorbed into the bloodstream directly through the skin, but other forms of organic mercury (in particular dimethyl mercury) can rapidly enter the body through skin.
- It readily passes the blood-brain barrier and enters the brain.
- In pregnant women, methyl mercury easily crosses the placental barrier and moves into the blood of the developing child and subsequently into the child's brain and other tissues. As with inorganic mercury, some of the methyl mercury in a nursing woman's body will mobilize into her breast milk.
- Methyl mercury can be changed, within the body, into inorganic mercury. When this happens in the brain, mercury can remain there for a long time.
Q38. How long does it take to excrete mercury (all forms) from the body?
- The majority of inorganic and elemental mercury compounds exit the body in the urine and faeces over a period of several weeks to months; smaller amounts of absorbed mercury vapours exit the body in exhaled breath and through perspiration, more rapidly.
- The half-life in the whole body has been observed to be within the range of 29 to 60 days, with an average of 42 days for inorganic mercury.
- Methyl mercury leaves slowly over a period of several months, mostly as inorganic mercury in faeces. After stopping exposure to methyl mercury, it takes between 45 and 70 days to decrease methyl mercury concentrations by half in a person's blood and slightly longer in the whole body.
Q39. What are the health effects and symptoms of inorganic mercury exposure in adults?
- Acute poisoning following exposure to mercury vapours at high levels (over 1 milligram per cubic meter) for a short period, may cause severe irritation of the airways, pneumonitis, pulmonary edema and other symptoms of lung damage. It can damage the brain, nerves, kidneys and lungs and, in extreme cases, may cause coma or death. Some people have experienced tremors, difficulty in coordinating the movement of their feet or hands, problems with balance, and a numbness or prickly sensation in their fingers.
- Following chronic exposure to low levels of mercury vapour (50 to 100 microgram per cubic meter), it may take some time to cause adverse effects on the central nervous system, kidney and thyroid, and the effects could be more subtle. It is difficult to distinguish mercury symptoms from some other common ailments. Symptoms include tremors (shaking), muscular weakness, depression, personality changes and short-term memory loss in adults, and skin rashes, particularly redness and peeling of the hands and feet, in children.
- Acute poisoning from inorganic mercury salts is rare, except in cases of accidental ingestion. The kidney is the primary target organ. Chronic occupational exposure to mercury salts has been associated with effects on the central nervous system similar to those associated with exposure to elemental mercury vapour.
Q40. What are the health effects and symptoms of methyl mercury exposure in adults?
A wide range of adverse health effects have been observed in adults following methyl mercury exposure, the severity depending largely upon the magnitude of the dose and the duration of exposure.
- Devastating neurological damage, and death occurred after the extremely high exposures stemming from the poisoning episodes in Minamata, Japan and in Iraq. Methyl mercury may also cause adverse effects on other organs in the body.
- Effects noted at the earliest stages of exposure include paresthesia (numbness or "pins and needles" sensation) in the extremities of the hands and feet, malaise or blurred vision. This may progress to ataxia (loss of the ability to coordinate muscular movement), dysarthria (speech difficulties) or loss of hearing and constriction of visual fields.
- Methyl mercury poisoning is characterized by a latent period between exposure and onset of symptoms. The latent period can vary from one to several months, depending on the dose and duration of the exposure.
- In Nunavik, mercury exposure is chronic (exposure at low doses over a long period of time) and, so far, no cases with these symptoms have been reported. Nutritional benefits of selenium and omega-3 fatty acid, both commonly found in fish and/or marine mammals, might counteract the adverse effects of methylmercury to some degree.
Q41. What type of treatment exists to remove mercury from blood?
If the level of mercury detected in the blood or urine is considered high, a doctor might prescribe chelating agents that bind mercury ions. The mercury and the chelating agent are then excreted from the body together. If no chelating agent is used, mercury can still be excreted by the body, but not as quickly. The excretion half-life (time for the amount of mercury to be reduced by half in the body) for metallic mercury is 33.1 days. A number of chelating agents that bind to the mercury are available and can increase the excretion rate up to threefold. As with any medicine, chelating agents can cause side effects.
Q42. Should I be concerned about mercury concentrations in drinking water?
Mercury levels in Canadian drinking water are generally well below the established maximum acceptable concentration (MAC) of 0.001 milligram per litre (Health Canada, Guidelines for Drinking Water Quality). While mercury levels may be elevated in certain source waters, because of natural mercury deposits or pollution, exposure via drinking water is not generally a concern. In those situations where mercury levels are deemed to be too high, effective treatment technologies exist for private and municipal water supplies.
Pregnant Women and Children
Q43. Why is mercury a special concern for pregnant and breastfeeding women?
Methyl mercury ingested by a pregnant woman, or metallic mercury that may enter her body from breathing contaminated air, can be passed from the maternal blood to the developing fetus by crossing the placental barrier. Inorganic mercury and methyl mercury can be transferred from maternal breast milk to a nursing infant. Methyl mercury can also accumulate in an unborn baby's blood to a concentration higher than the concentration in the mother. The amount of mercury in milk will vary, depending on the degree of exposure and the amount of mercury taken up by the nursing mother. Concern over mercury levels in breast milk should be discussed with the nursing mother's doctor, considering the significant benefits of breastfeeding to the developing infant. Advice on fish consumption is given in Q.13.
Q44. Why are children and the developing fetus at a greater risk than adults for adverse health effects associated with mercury?
There are a number of reasons why the developing fetus and children are at greater risk for acquiring a higher blood mercury level than adults.
- Children have different behaviours than adults, which involve direct contact with surfaces that may be contaminated (such as crawling and producing mouth contact with surfaces and toys). These activities may place them at higher risk.
- The intake of air, water and food for children may be greater per kg of body weight than for an adult, which could result in far greater exposure to the different forms of mercury.
- Because children are developing rapidly, their metabolic rate is higher than that of an adult, resulting in a greater efficiency at absorbing substances (e.g. their level of gastro-intestinal absorption and retention are greater).
- In addition, the immature or developing organs and systems of children are less able to eliminate mercury. Cellular repair mechanisms are similarly underdeveloped, providing a diminished capacity to repair damage caused by mercury.
- Scientific evidence indicates that exposure to methyl mercury is more dangerous for young children than for adults. This is because of lower neurological effect thresholds for methyl mercury and the distribution of higher levels of methyl mercury to the developing brain of young children, which may interfere with the development of motor and cognitive skills.
Q45. What are the health effects of metallic or inorganic mercury exposure in children?
- Limited information is available on the effects of mercury vapour on early stages of childhood. High exposure to mercury vapours can cause lung, stomach and intestinal damage. In severe cases, induced respiratory failure may result in death. "Pink disease" or acrodynia has been reported most frequently in children treated with teething powders that contained calomel (mercury) or in children who inhaled mercury vapour, such as from broken thermometers. These children also developed irritability, insomnia, increases in perspiration and photophobia (sensitivity to light). Teething powders are no longer used in Canada (see Q.43 - Q.44).
- Children exposed to excessive amounts of mercury chloride tablets for constipation, worms or to mercurous chloride-containing powders for teething discomfort, had swollen red gums, excessive salivation, weight loss, diarrhea and/or abdominal pain, and muscle twitching or cramping in the legs and/or arms, increased heart rates and elevated blood pressure. Kidney damage is very common after exposure to toxic levels of inorganic mercury.
Q46. What are the health effects associated with exposure to methyl mercury in children?
Children are more susceptible to the adverse effects of methyl mercury than adults. Methyl mercury exposure is commonly associated with neurodevelopmental effects. The effects on infants may be subtle or more pronounced, depending on the degree of exposure received by the fetus or young child.
- Infants exposed in utero to high levels of methyl mercury during the Minamata and Iraqi incidents were born with severe disabilities, such as intellectual disability, seizure disorders, cerebral palsy, blindness, and deafness.
- At much lower doses resulting from chronic maternal fish consumption, infants might appear normal during the first few months of life but later display IQ deficits, abnormal muscle tone, reduced motor function, and lower attention and visuospatial performance. In recent human studies, neuropsychological deficits are detected in children aged seven years, following prenatal exposure to methyl mercury.
- Increased blood pressure in children exposed prenatally to methyl mercury has also been reported.
Mercury in the Environment
Mercury and its compounds can be toxic to living organisms at very low concentrations in aquatic and terrestrial ecosystems. Since mercury is an element, it cannot be created or destroyed and it persists in the environment. In addition, mercury can bioaccumulate in organisms. This ongoing accumulation in the body tissues of various species leads to biomagnification in the predator species as they consume organisms lower down in the food chain.
This section covers topics such as how mercury affects fish and wildlife and the concentrations of mercury present in various components of the environment such as air and freshwater.
Q47. How much does Canada contribute to worldwide mercury releases?
Total global mercury emissions from human sources are currently thought to be approximately 2400 tons per year. In 2000, the Canadian contribution to global releases was approximately 8 tons.
It is assumed that a large portion of the mercury present in the atmosphere today is a result of many years of releases stemming from anthropogenic activities. The natural component of the total atmospheric burden is difficult to estimate, but is probably in the order of 25% to 50%. Anthropogenic activities have thus increased the levels of mercury in background air by roughly a factor of 3. Current estimates indicate that total global mercury releases to the atmosphere are in the area of 5000 metric tons peryear, of which roughly 50% are of anthropogenic origin.
Q48. How are anthropogenic (human) mercury emissions transported through the atmosphere?
- Because mercury evaporates relatively easily, mercury emissions can be transported on wind currents, either as a vapour or bound to particles.
- Elemental or metallic mercury vapour can circulate in the atmosphere for a year or more and can travel long distances. In contrast, oxidized or reactive mercury has an atmospheric residence time of less than two weeks due to its solubility in water and its reactivity.
- As a result, mercury emissions from industrial point sources might remain localized in the environment, or might be transported regionally and even globally. In addition, mercury is thought to participate in a global distillation phenomenon that transfers mercury and other chemical emissions from equatorial, subtropical and temperate regions to the polar regions via the "grasshopper effect". When this phenomenon takes place, the emitted substance reenters the atmosphere by volatilizing after initial deposition and continues over time to "hop" through the environment until there is insufficient solar energy to revolatilize the substance. This favours contaminant accumulation in the colder polar regions.
Mercury from the atmosphere reaches land and surface waters either through wet deposition in precipitation or through dry deposition bound to particles, and can also enter water bodies as runoff from soil or through groundwater. In surface waters and sediments, biological processes can transform mercury into methyl mercury - a highly toxic form that can accumulate in living organisms and biomagnify up the food chain.
Q49. How is mercury transformed in the environment?
- Natural transformations and environmental pathways of mercury are very complex and are greatly affected by local conditions.
- There are two main types of chemical reactions in the mercury cycle that convert mercury through its various forms: oxidation-reduction and methylation-demethylation.
- In oxidation-reduction reactions, mercury is either oxidized to a higher valence state through the loss of electrons (e.g. from elemental mercury as Hg0 to the more reactive form as Hg2+) or mercury may be reduced to a lower valence state by gaining electrons.
- Mercury is transformed into methyl mercury when the oxidized, or mercuric species (Hg2+), gains a methyl group (CH3). The methylation of Hg2+ is primarily a natural, biological process resulting in the production of highly toxic and bioaccumulative methyl mercury compounds that build up in living tissue and increase in concentration up the food chain.
Q50. What is polar sunrise depletion?
A Canadian atmospheric researcher, Dr. Bill Schroeder, has shown in recent studies the rapid oxidation of Hg0 vapour to Hg2+ in Arctic surface air during and after the polar sunrise at Alert, Nunavut Territory, and this has more recently been observed in Pt. Barrow, Alaska. This reaction is thought to occur photochemically (in the presence of sunlight) and in the presence of reactive chemicals released from sea salt (for example, bromine and chlorine ions). As a result, a pulse of reactive mercury enters the Arctic environment when the short-lived growing season is beginning. It remains a research question to determine what fraction of this reactive mercury is converted to toxic methyl mercury and taken up by animals and plants.
It is suggested that significant atmospheric mercury is being deposited to the snow pack during the period following polar sunrise. It has been found that, in the springtime, the accumulation rate of mercury in the snow is enhanced by a factor of four. Elevated concentrations of mercury have been found in snow melt-water collected near Arctic communities. Concentrations of mercury ranged from 2.1 nanograms per litre at Baker Lake to 237 nanograms per litre at Cambridge Bay. A nanogram is one-billionth (10-9) of a gram. Future research will help to assess the environmental fate and impacts of this significant influx of mercury into the Arctic ecosystem.
Q51. How does mercury affect fish and wildlife?
Mercury is toxic, persistent, and can build up or bioaccumulate in living organisms, inflicting increasing levels of risk on higher order species (see Q.12). Although the long-term effects of mercury on whole ecosystems are unclear, the survival of affected populations and overall biodiversity could be at risk.
Methyl mercury is bound tightly to fish protein when absorbed through the gills or when contaminated food sources are eaten. In some cases, methyl mercury levels in higher trophic level (food chain) fish species such as freshwater bass, walleye and pike, and marine shark and swordfish, can be up to a million times greater than in the surrounding water. In general, levels of mercury increase with fish size and age. Levels also vary by species and location. Bioaccumulation in fish is influenced by the amount of methyl mercury present, which is in turn affected by local biogeochemical processes.
Piscivorous (fish eating) predators such as loons, merganser ducks, osprey, eagles, herons and kingfishers generally have high concentrations of mercury in their systems. Mercury has been detected in common loons from Alaska to Atlantic Canada, and blood concentrations have been correlated with levels in prey fish species. Research indicates that loon blood mercury concentrations increase from west to east across Canada and the United States, with the highest levels in Southeast Canada. High levels of mercury are associated with impaired loon reproductive success as well as with growth related problems. These problems can lead to an increased death rate and a decreased birth rate, resulting in a reduction in the abundance of natural populations.
Mercury has been found in predatory mammals such as otters from south central Ontario. It is thought that elevated mercury levels in otters may cause early mortality due to toxicity and behavioural changes. While the reproduction and behaviour of bird species is generally affected by exposure to methyl mercury, mammals most often suffer neurological effects. The severity of the toxic effects will depend on the degree of exposure and can range from a slight impairment to reproductive failure or death.
Q52. Is mercury present in the air and at what concentration?
In 1996 Environment Canada initiated the Canadian Atmospheric Mercury Measurement Network (CAMNet). Currently, there are stations in rurally representative locations across Canada measuring gaseous elemental mercury on a continuous basis. Typical ambient air concentrations at these sites range from 1.5 to 1.7 nanograms per cubic metre. The concentrations show a seasonal variation and, when air from industrialized regions arrives at a site, are correlated with other pollutants. Studies are also being undertaken in urban areas to further investigate the behaviour of mercury.
Q53. Is mercury present in dust & soil and at what concentration?
Concentrations of mercury in Canadian soils are in the range of 0.01 to 0.4 milligram per kilogram of dry weight, though higher levels tend to be reported in areas of ore deposits, spills, landfills and metal processing plants.
Q54. Is mercury present in precipitation and at what concentration?
Results at seven Canadian Atmospheric Mercury Measurement Network sites in 2001 showed an average concentration of 6.8 nanograms of mercury per litre of precipitation, with higher values recorded in the summer. Concentrations and deposition were highest in summer and lowest in winter. Deposition is a function of the concentration of mercury in precipitation and the amount of precipitation. The average annual deposition rate in 2001 for the seven sites noted above was 5.5 micrograms of mercury per square metre per year.
Q55. Is mercury present in freshwater and at what concentration?
Based on information largely from Ontario and Quebec, levels for methyl mercury are usually less than 1 nanogram per litre in natural surface waters, although concentrations up to 4.1 nanograms per litre have been reported. Methyl mercury concentrations are higher (0.6 nanogram per litre) in water draining from wetland areas relative to concentrations in water from other areas (0.03 nanogram per litre). Generally, methyl mercury accounts for less than 10 percent of total mercury found in surface water (see Q. 7).
Q56. Is mercury present in sediment and at what concentration?
Concentrations of mercury in freshwater and marine sediments vary considerably.
Background levels in lakes and rivers average 0.07 milligram per kilogram of dry weight. Mercury levels in contaminated lake sediments are as high as 15 milligrams per kilogram of dry weight, and as high as 25 milligrams per kilogram of dry weight for contaminated river sediments
In marine environments (coastal and estuary), background concentrations range from 0.010 to 0.521 milligram per kilogram of dry weight, while concentrations up to 23 milligrams per kilogram of dry weight have been measured in contaminated marine sediments.
Government Action on Mercury
The Government of Canada is involved in the development and implementation of several initiatives to help reduce mercury releases and manage risks associated with exposure to mercury. Although domestic measures will continue to reduce the risk of mercury in Canada, efforts must also be made on a regional and global scale, because a portion of the mercury in our lakes and soil originates from other countries via long-range atmospheric transport. This section covers strategies to manage mercury in Canada, and provides further sources of information.
Q57. What Canadian legislation pertains to the management of mercury?
Canadian Environmental Protection Act, 1999 (CEPA)
The goal of the renewed CEPA (1999) is to contribute to sustainable development through pollution prevention and to protect the environment, human life and health from the risks associated with toxic substances. CEPA also recognises the contribution of pollution prevention and the management and control of toxic substances and hazardous waste to reducing threats to Canada's ecosystems and biological diversity.
An Act to regulate agricultural fertilizers.
An Act respecting fisheries; the proper management and control of the
sea-coast and inland fisheries; the conservation and protection of fish; the catching, loading, landing, handling, transporting, possession and disposal of fish; the operation of fishing vessels and other regulations.
Food & Drugs Act
This Act applies to all food, drugs, cosmetics and medical devices sold in Canada, whether manufactured in Canada or imported. The Act and Regulations ensure the safety of and prevent deception in relation to foods, drugs, cosmetics and medical devices by governing their sale and advertising and in addition set out the labelling requirements for food.
Hazardous Products Act
The Act and its Regulations, are in place to protect the health and safety of Canadians by prohibiting, regulating or controlling the sale, advertisement, or importation of hazardous or potentially hazardous products used by consumers and workers. However, this Act does not cover products that are regulated by other federal legislation, for example, pesticides (regulated by the Pest Control Products Act) or food, drugs or cosmetics (regulated by the Food and Drugs Act).
Pest Control Products Act
This Act and Regulations are intended to protect people and the environment from risks posed by pesticides. Pesticides include a variety of products such as insecticides, herbicides and fungicides. Any pesticide imported, sold or used in Canada must first be registered under this Act, which is administered by the Pest Management Regulatory Agency of Health Canada.
Transportation of Dangerous Goods Act
The Transportation of Dangerous Goods Directorate and its corresponding Act and Regulations are the focal point for the national program to promote public safety during the transportation of dangerous goods. The TDG Directorate serves as the major source of regulatory development, information and guidance on dangerous goods transport for the public, industry and government employees.
Q58. What is the Government of Canada doing, in collaboration with provincial and international governments, to reduce mercury in the environment?
- The primary policy tools currently in use for mercury release reductions in Canada are Canada-wide Standards (CWS). These are standards developed cooperatively by the Canadian Council of Ministers of the Environment (CCME), which comprises the environment ministers of the 14 jurisdictions in Canada (federal, provincial, and territorial). While CWSs are developed jointly, ministers are responsible for implementation in their jurisdiction.
- In 2000, CCME developed several Canada-wide Standards for mercury. Standards have been developed, or are being developed, for certain mercury containing products and for mercury emissions from selected industries. For more information on Canada-wide Standards, see Q.66 - Q.70, or visit: http://www.ccme.ca/initiatives/standards.html
- In addition, the 1994 Canada-Ontario Agreement Respecting the Great Lakes Basin Ecosystem (COA) targeted mercury pollution for control. A new COA was signed by the Governments of Canada and Ontario in March, 2002. One of the anticipated results of this agreement is a 90% reduction in mercury by 2010. For more information, visit:
Canada is working with the USA and Mexico through the North American Commission for Environmental Co-operation to address mercury issues under the North American Regional Action Plan on Mercury. For more information, see:
In addition, Canada is taking a lead role to reduce mercury releases into the environment both in Canada and on a global scale through other regional and international initiatives, including:
- Great Lakes Binational Toxics Strategy;
- New England Governors and Eastern Canadian Premiers (PDF Version - 174 K);
- United Nations Economic Council for Europe Convention on Long-Range Transboundary Air Pollution;
- United Nations Environment Program, Global Mercury Assessment;
Q59. How is Health Canada helping to reduce exposure to mercury?
Health Canada, as the federal regulatory body, sets the health standards and issues health advisories, when necessary, to help reduce mercury exposure (see Q.7 - Q.34). Health Canada has a number of guidelines/recommendations on mercury as follows:
Table 1 footnotes
|Guideline:||Canadian Drinking Water Quality; (Maximum Acceptable Concentration; MAC)||0.001 mg total mercury per Litre|
|Guideline:||Soil (inorganic mercury)|
|- Agricultural||6.6 mg/kg|
|- Residential/Parkland||6.6 mg/kg|
|- Commercial||24 mg/kg|
|- Industrial||50 mg/kg|
|Guideline:||Commercial Fish||0.5 part per million total mercuryTable 1 footnote 1|
|Guideline:||Provisional Tolerable Daily Intake (pTDI)
|0.47 µg MeHg per kg bw per day|
|Provisional Tolerable Daily Intake (pTDI)
- children and women of childbearing age
|0.2 µg MeHg per kg bw per day|
|- Normal Acceptable Range||<20 ppb||<6 ppm|
|- Increasing Risk||20-100 ppb||6-30 ppm|
|- At Risk||>100 ppb||>30 ppm|
|Guideline:||Occupational Exposure||TLV-TWATable 1 footnote 2||TLV-STELTable 1 footnote 3|
|- Mercury-alkyl compounds||0.01 mg/m3||0.03 mg/m3|
|- Mercury-aryl compounds||0.1 mg/m3|
|- Mercury - elemental & inorganic forms||0.025 mg/m3|
Q60. Does Canada monitor the release of mercury into the environment from anthropogenic (human) sources?
Yes, the public can access information on mercury released into air, water and soil from Canadian industry and transportation sectors through the National Pollutants Release Inventory (NPRI), established in 1992 to provide a national, publicly accessible database of pollutants. Each year, releases and transfers of pollutants from facilities nationwide are reported. Mercury (and its compounds) have been on the NPRI substance list since 1992, at the 10-tons reporting threshold. In the year 2000, the NPRI reporting threshold for mercury was reduced to five kilograms. For more information see: http://www.ec.gc.ca/pdb/
Q61. Does Canada monitor levels of mercury in the environment?
Mercury levels in the Canadian environment are measured through a number of programs, including:
- The Canadian Atmospheric Mercury Measurement Network
- The Ecological Monitoring and Assessment Network;
- The National Air Pollution Surveillance System;
- The Arctic Monitoring and Assessment Program;
- The Integrated Atmospheric Deposition Network;
Q62. What mercury research is supported by the Government of Canada?
The Government of Canada is involved in a number of mercury-related research and monitoring initiatives including:
- Northern Contaminants Program;
- The National First Nations Environmental Contaminants Program;
- Great Lakes Program and the St. Lawrence Vision 2000 Program;
- COMERN (Collaborative Mercury Research Network-includes Health Canada);
- METAALICUS (Mercury Experiment to Assess Atmospheric Loading In Canada and the United States);
- Work conducted through the Atlantic Region Mercury Team;
- The Northeastern Mercury Cooperative (NSRC) Mercury Research Group;
- Natural Resources Canada mercury research;
Q63. Are consumer products regulated for acceptable levels of mercury?
Yes, the amount of mercury allowed in some consumer products is prohibited or restricted under the authority of Health Canada's Hazardous Products Act. Selling, advertising or importing toys, equipment and other products for use by a child in learning or play is prohibited if there is any decorative or protective coating on these items that contains any mercury compound. Restrictions are also being introduced on the sale, advertisement or importation of surface coating materials containing mercury.
Q64. What action has Health Canada taken to reduce mercury levels in paint used in the home?
- The Hazardous Products Act prohibits the use of mercury in decorative or protective coatings applied on toys, equipment and other products for use by a child in learning or play.
- In 1991, a voluntary agreement between Health Canada and the Canadian Paint and Coatings Association resulted in removal of mercury compounds from interior latex paints. As of December 2000, mercury-based anti-microbial pesticides are no longer registered under the Pest Control Products Act administered by the Pest Management Regulatory Agency and are not allowed to be intentionally added to any Canadian-produced interior and exterior paints.
- Revisions are being made to existing regulations, which will prohibit the intentional addition of mercury to all paints.
- Mercury limits in recycled paint will be decreased from 65 milligram per kilogram to 10 milligram per kilogram over a number of years. For these paints, the presence of mercury must be clearly identified on the paint container label, along with a warning not to apply the paint to surfaces accessible to children or pregnant women.
Q65. Does Canada have regulations in place to control the amount of mercury in compost?
Centralized composting sites are becoming increasingly widespread as a result of recycling activities. The number of centralized, private and municipal composting facilities throughout Canada has more than quadrupled, from 30 sites in 1989 to over 120 sites in 1994. The maximum amount of mercury allowed in compost is 5 milligrams per kilogram under the Fertilizers Act, administered by Agriculture Canada.
Q66. Does Canada have regulations in place to control mercury levels in mercury-containing fluorescent lamps?
The Canadian Council of Ministers of the Environment has developed a Canada-wide Standard for mercury-containing lamps. The standard takes a pollution prevention approach by reducing the mercury content of lamps sold in Canada. The standard has set a goal of a 70% reduction by 2005, as compared to a 1990 baseline, and an 80% reduction by 2010 in the average content of mercury in all mercury-containing lamps sold in Canada.
Q67. Does Canada have regulations in place to control mercury releases from dental amalgam waste?
The Canadian Council of Ministers of the Environment has developed a Canada-wide Standard for Dental Amalgam Waste. The standard is the application of "best management practices" to achieve a 95% national reduction in mercury releases from dental amalgam waste discharges to the environment by 2005, from a base year of 2000. Best Management Practices are defined as including the use of an ISO-certified amalgam separator, or its equivalent, and the appropriate management of waste to minimise mercury discharge to the environment.
Q68. Does Canada have regulations in place to control mercury releases from base metal smelting?
The Canadian Council of Ministers of the Environment has developed a Canada-wide Standard for mercury releases from this sector. The standard establishes environmental source performance guidelines for base metal smelters. For existing facilities, the guideline is 2 grams mercury released per ton of finished metal produced. For new and expanded facilities, the performance guideline is 0.2 gram of mercury perton of finished zinc, nickel and lead produced; and 1 gram of mercury perton of finished copper produced.
Q69. Does Canada have regulations in place to control mercury emissions from waste incineration?
The Canadian Council of Ministers of the Environment has developed a Canada-wide Standard for mercury emissions from the waste incineration sector, which includes medical, hazardous, sludge and municipal wastes. Improvements in process and treatment technologies and reductions in waste inputs have resulted in lowered mercury emissions from these incinerators by 60% (2 tons) since 1990. The Canada-wide Standards for the allowable concentration of mercury ranges from 20 to 70 microgram percubic metre. These standards are among the lowest found globally, and will further trim present emissions of 1200 kilograms per year by over 70% by 2006.
Q70. Does Canada have regulations in place to control mercury emissions from the Electric Power Generating Sector?
The Canadian Council of Ministers of the Environment has committed to develop a Canada-wide Standard by 2005 to reduce mercury emissions from the coal-fired electric power generation sector by 2010, to explore the national capture of mercury from coal burned in the range of 60-90%, and to align with US standards for mercury. The standard will apply to existing and new plants.
Q71. Does Canada regulate mercury-containing waste disposal at sea?
Yes, Canada controls waste disposal at sea and meets its international obligations under the London Convention (and its 1996 Protocol) by means of a permit system, in place since 1975. CEPA (1999) contains provisions concerning disposal at sea.
Q72. What action has Health Canada taken to eliminate the use of mercury in fungicides?
The sale of all mercurial fungicides was discontinued under the authority of the Pest Control Products Act as of December 31, 1995. Existing stocks of these products were allowed to be sold and used until December 31, 2000, at which time it was assumed that the supply of products would be exhausted.
Sources of Information on Mercury
Q73. Where can I get more information about mercury?
Canada-wide Standards for Mercury. Canadian Council of Ministers of the Environment, 123 Main Street, Suite 360, Winnipeg, Manitoba R3C 1A3;
Environment Canada. Mercury and the Environment;
http://www.ec.gc.ca/mercury/ This website includes information and links regarding:
- Sources and environmental cycling and fate of mercury;
- Environmental impacts of mercury;
- Federal/Provincial/Territorial and International initiatives to manage mercury releases;
- Information on fish consumption advisories;
- Information on cleaning up small mercury spills.
Health Canada. 1994. Health and Environment - Partners for Life.;
Health Canada. 1996. The Safety of Dental Amalgam;
Health Canada Advisory: Information on Mercury Levels in Fish. May 29, 2002;
Agency for Toxic Substances and Disease Registry (ATSDR). US Department of Health and Human Services. Public Health Service. 1999. Toxicological Profile for Mercury (Update). March.
Andersen, H.R., Nielsen, J.B., Grandjean, P. 2000. Toxicologic Evidence of Developmental Neurotoxicity of Environmental Chemicals. Toxicology. 144 (1-3): 121-127.
Canadian Food Inspection Agency Fact Sheet: Mercury and Fish Consumption. P0083E-99;
Canadian Council of Ministers of the Environment. 1999. Canadian Environmental Quality Guidelines.
Clarkson, Dr. T.W. February 2002. The Three Modern Faces of Mercury. Environmental Health Perspectives. 110, Supplement 1: 11-23.
Environment Canada, Pollution Data Branch. 2002. Preliminary Mercury Emissions Inventory for the Year 2000.
Environment Canada, Guidelines and Standards Division.2000. Canadian Tissue Residue Guideline for Methyl Mercury for the Protection of Wildlife Consumers of Aquatic Biota.
Evers, D., Kaplan, J., Meyer, M., Reaman, P., Braselton, W. Major, A., and Burgess, N., 1998. Mercury in Loons. Environ. Toxicol and Chem. 2: 173-183.
Garrett, R.G. 2000. Natural Sources of Metals to the Environment. Human and Ecological Risk Assessment. 6 (6): 945-963.
Grandjean P., Weihe P., White R.F., Debes F., Araki S., Murata K., Sørensen N., Dahl D., Yokoyama K., Jorgensen P.J. 1997. Cognitive Deficit in 7-year-old Children With Prenatal Exposure to Methylmercury. Neurotoxicol Teratol. 19: 417-28.
Health Canada. 1986. Guidelines for Drinking Water Quality, Supporting Document for Mercury.
Health Canada. Nutrition for a Healthy Pregnancy: National Guidelines for the Childbearing Years. Ottawa: Minister of Public Works and Government Services Canada; 1999;
Health Canada. 1996. The Safety of Dental Amalgam;
Health Canada, Population and Public Health Branch, Division of Immunization and Respiratory Diseases. Updated June 01, 2004;
Health Canada, Health Products and Food Branch. 2001. Advisory on Mercury in Fish. Document 2001-60, May 29;
Health Canada, Health Protection Branch. 1998. Memorandum to the Members of the Federal/Provincial/Territorial Committee on Food Safety Policy. Food Directorate.
Kaiserman, M.J. and Rickert, W.S. 1994. Levels of Lead, Cadmium, and Mercury in Canadian Cigarette Tobacco as Indicators of Environmental Change: Results from a 21-Year Study. Environmental Science and Technology. 28; 924.
Mason, R. P., W. F. Fitzgerald, and M. M. Morel. 1994. The Biogeochemical Cycling of Elemental Mercury: Anthropogenic Influences. Geochim. Cosmochim. Acta. 58 (15): 3191-3198.
Metal Ions in Biological Systems: Mercury and its Effects on Environment and Biology. Volume 34. Editors A. Sigel and H. Sigel. Marcel Dekker Inc., New York, New York. 1997.
Ministry of Health Services of British Columbia. Tobacco Strategy / What's in Tobacco / Index of Smoke Constituents:
Munthe, J., Wangberg, I., Pirrone, N., Iverfeld, A., Ferrara, R., Ebinghaus, R., Feng, R., Gerdfelt, K., Keeler, G. J., Lanzillotta, E., Lindberg, S. E., Lu, J., Mamane, Y., Prestbo, E., Schmolke, S., Schroder, W. H., Sommar, J., Sprovieri, F., Stevens, R. K., Stratton, W., Tuncel, G., and Urba, A. 2001. Intercomparison of Methods for Sampling and Analysis of Atmospheric Mercury Species. Atmospheric Environment. 35: 3007-3017.
National Academy of Sciences. 2000. Toxicological Effects of Methyl Mercury.
Ontario Ministry of Environment. 1997-1998. Guide to Eating Ontario Sport Fish. 19th rev. ed. Toronto Ministry of the Environment, Communications Branch.
Pacyna et. al. 2002. In preparation.
Scheuhammer, A., Atchison, C., Wong, A. and, Evers, D. 1998. Mercury Exposure in Breeding Common Loons (Gavia Immer) in Central Ontario. Environmental Toxicology and Chemistry. 17 (2): 191-196.
Schroeder, W. and Munthe, J. 1998. Atmospheric Mercury - An Overview. Atmospheric Environment. 32 (5): 809-822.
Schroeder, W. 2002. Personal Communication.
United Nations Environment Programme. December 2002. Chemicals: Global Mercury Assessment. Geneva, Switzerland.
World Health Organization.1989. Evaluation of Certain Food Additives and Contaminants: Thirty-third Report of the Joint Expert Committee on Food Additives. WHO Technical Report Series 776. Geneva, Switzerland.
World Health Organization. 2003. Sixty-first meeting of the Joint FAO/WHO Expert Committee on Food Additives . Geneva, Switzerland.
Wren, C.D., Stokes, P.M., and Fischer, K. 1986. Mercury Levels in Ontario Mink and Otter Relative to Food Levels and Environmental Acidification. Can. J. Zool. 64: 2854-2859.
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