Executive Summary: Tritium Study
What did we conclude from this study ?
A study of the effect of tritium release
from Bruce Power on Lake Huron shoreline was conducted during the summer of
1996. Based on the current Ontario Drinking Water Objectives, the municipal
water supplies at Kincardine, Southampton and Port Elgin are safe to drink.
Drilled wells are relatively unaffected by the releases of tritium. Shallow
wells north of Bruce Power exhibit the highest levels of tritium.
Recreational use of the Lake Huron beach waters in the study areas and
during the study period did not pose a health risk to the public. Typically,
the tritium concentrations in drinking water are highest north of Bruce
Power and decrease exponentially with distance. Concentrations of tritium
are commonly 14 times lower by the time they reach Port Elgin, two to four
days after their release at Bruce Power.
Why did we do this study?
The availability of safe, clean drinking
water has been a public health interest around the world for over a century.
In Bruce County there was a growing public concern regarding radioactive
tritium released into Lake Huron during nuclear power production at Bruce
Power. Although the area’s municipal water treatment plants are monitored
for tritium, nothing was known about the private water supplies in the area.
The study was designed to obtain specific, local information on the average
or background tritium levels in drinking and recreational waters along the
Lake Huron shoreline. Furthermore, fluctuations in the release of tritium at
Bruce Power would be observed and tracked to evaluate their effect on the
local water supply.
What are the current standards?
The maximum acceptable level of tritium in
drinking water, set by the Ontario Drinking Water Objectives, has been
lowered from 400,000 to 40,000 and now stands at 7,000 Bq/L as an annual
average. This standard ensures that the annual effective dose from drinking
water sources does not exceed 0.1 mSv per year. In other words, no more than
10% of the recommended maximum public dose of radiation (1 mSv/year) may
come from drinking water. Within these guidelines, individual releases of
more than 7,000 Bq/L are not considered to pose a health risk unless they
result in an annual average dose over 7,000 Bq/L.
Who participated?
On April 4, 1996, a meeting was held to
discuss acquiring better information on tritium levels in private water
supplies. The meeting was hosted by the Bruce Township and attended by the
Regional Emergency Planning Co-ordinator, representatives from Kincardine
Township Council, Bruce Township Council, Ontario Hydro, Ministry of Labour,
Ministry of Natural Resources and the Health Unit. The group decided the
study was needed along the lakefront area from Kincardine to Southampton.
The neighbouring township of Saugeen was, at that time, invited to
participate. An Ontario Environmental Youth Corps Grant, Bruce Township and
Ontario Hydro provided financial support for the study.
What did we do?
The Health Unit managed a pilot study
involving three major steps:
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Step1: Establish baseline data on land use,
drinking and recreational water use along the Lake Huron shoreline,
north and south of Bruce Power in June 1996.
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Step 2: Monitor the level of tritium in a
representative drinking water sample and recreational water sample along
the shoreline from July 8 to August 23, 1996.
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Step 3: Describe the movement of tritium
through the water supply by relating the level of tritium in the local
water supplies with the discharge of tritium from the two nuclear power
plants, Bruce A and Bruce B.
Lake Huron Shoreline Study
Area Map
What information did we get?
The majority of land use was seasonal
residential (76%), with the remaining (24%) being permanent residential. The
reported water sources were drilled wells (27%), communal water supplies
(26%), dug wells (22%), sandpoints (16%), bottled water (6%) and pumped
water (3%). All the communal water supplies, with one exception, were served
by drilled wells. Drilled wells had a mean depth of 39 meters and dug wells
had a mean depth of 5 meters. There were three water treatment plants within
the study area.
Water movement in the vicinity of Bruce Power is predominately along the
shore in a northeasterly direction. Tritium discharges from Bruce Power
generally have the greatest effect on the shoreline area north of the site,
excluding drilled wells.
The closest recreational site directly north of Bruce Power was Baie du
Dore, which recorded an average reading of 141 Bq/L and a peak reading of
240 Bq/L. Drilled wells, regardless of location, measured at or near the
level of detection. Drilled wells do not appear to be affected by tritium
discharges into Lake Huron. Surface wells south of Bruce Power recorded
tritium levels higher than the nearby recreational water supplies. This may
be caused by the additional burden of airborne tritium.
The closest water treatment plant to Bruce Power is the Port Elgin Water
Treatment Plant on the north side. The mean tritium concentration at the
plant during the study period was 25.9 Bq/L with a peak reading below 180
Bq/L. Readings were lower further north in Southampton at 22.9 Bq/L. South
of Bruce Power, in Kincardine, the average level was below the level of
detection. Overall, the tritium concentration decreases exponentially with
distance north of Bruce Power.
Accurately determining the amount of tritium released into Lake Huron from
Bruce Power is not a straightforward exercise. Two measurements of the
tritium released at each of the two outfalls at Bruce Power were available:
weekly composite tritium levels and calculated tritium levels. No data is
available for the combined effects of tritium releases from Bruce A.
However, a strong relationship was found between the calculated tritium
levels and the nearby sampling points; for example, 81% of the variation in
the tritium levels at Scott Point may be accounted for by knowing the
calculated tritium levels at Bruce A.
Ontario Hydro uses a dilution ratio of 1:14 to calculate probable tritium
concentration at Port Elgin Water Treatment Plant as compared to Bruce
Power. For example, a weekly average tritium concentration discharge of 1400
Bq/L from Bruce Power would result in 100 Bq/L at Port Elgin Water Treatment
Plant using the ratio. For the time period from April 1 to August 31, 1996,
the dilution factor at the Port Elgin Water Treatment Plant approximated
1:14.5. The limitation of using this dilution factor is that it only applies
to the Port Elgin Water Treatment Plant and does not give us any information
for sites closer to Bruce Power.
What future recommendations came from this study?
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Ontario Hydro should extend its
environmental monitoring program north of the Bruce A outfall channel to
at least include Baie du Dore, Scott Point and Brucedale Conservation
Area. Shoreline lake samples and shallow wells in the area should be
routinely monitored for tritium concentrations. Samples should be taken
during each of the four seasons.
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Following an abnormally high tritium
release to the lake, samples should be taken at least daily at multiply
sites north of Bruce Power. This information would enable the Health
Unit to better inform the public of any risk from the release.
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Following an abnormally high tritium
release to the lake, samples taken at the Port Elgin Water Treatment
Plant should be analysed daily.
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Shallow wells surrounding Bruce Power
should be monitored for tritium to establish airborne contamination.
Wells should be chosen at varying distances from Bruce Power to the
north, east and south of the plant.
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The composite sampler system at the
Bruce A outfall needs repair or replacement. The tritium concentrations
recorded by this system do not accurately reflect tritium concentrations
in the outfall stream.
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A model should be developed to show
tritium concentrations that result from liquid tritium emissions from
Bruce Power. The model should include depth, distance and dilution
offshore and along the Lake Huron shoreline, north and south of the
Bruce A and the Bruce B outfall channels.
What did we not find out?
The study was limited in scope and of a
relatively short duration. The return rate of the survey of shoreline
property owners was 51%. Therefore, many of the water supplies in the area
may still need to be identified.
During the study period, consistently low and even releases of tritium were
observed from Bruce Power. A controlled, elevated release would have better
simulated an emergency and provided the study with some peak data, which
would have been more easily tracked through the water supply.
The data reported from each of the two plants was presented in a different
manner and detail, making it difficult to compare or combine the tritium
levels entering the lake from the two plants.
This study reflects only the summer of 1996. It may be possible that, within
different time periods and seasons, the movement of tritium through the
water supply would be substantially different.
For a copy of the report contact the Grey Bruce Health Unit.
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