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The following section provides a more detailed overview of the scientific methods that will be used to conduct the HHRA. This material is excerpted from the Terms of Reference for the study. To read the complete document, please click here.
The HHRA for the town of Flin Flon, Manitoba and Creighton, Saskatchewan, will be conducted
according to widely accepted HHRA methodologies and guidance published and endorsed by
such agencies as the Health Canada Guidance on Human Health Preliminary Quantitative Risk
Assessment (Health Canada, 2004), and the United States Environmental Protection Agency
Risk Assessment Guidance for Superfund (U.S. EPA, 1989) in addition to various HHRA
guidance updates published by U.S. EPA from the early 1990s to the present.
Given that there is evidence to warrant further assessment of risks to humans as a result of the
presence of certain metals in soil above CCME guidelines, and there is uncertainty regarding
the potential risks associated with other metals found to be elevated in soils, the objectives of
the HHRA are as follows:
Objective 1: To assess risks to human receptors residing in Flin Flon, Manitoba and
Creighton, Saskatchewan as a result of exposure to metals in soil and other environmental
media impacted by the activities of the HBMS complex. The HHRA will estimate the
contribution from individual exposure pathways and environmental media to assist in the
development of risk management objectives; and
Objective 2: Develop risk management objectives and/or mitigation plans if unacceptable
risk levels are identified in the HHRA. These risk management plans will be based on
scientific approaches in consultation with the Technical Advisory Committee and the community.
HHRA framework
The HHRA framework to be applied at this site will follow the standard HHRA framework that is
composed of the following steps:
i) Problem formulation
ii) Exposure assessment
iii) Hazard assessment
iv) Risk characterization
Problem Formulation Stage
This first step in the HHRA process is an information gathering and interpretation stage that
plans and focuses the study on critical areas of concern for the site or area being evaluated.
Problem Formulation defines the nature and scope of the work to be conducted, permits
practical boundaries to be placed on the overall scope of work and ensures that the assessment
is directed at the key areas and issues of concern.
The key tasks requiring evaluation within the problem formulation step include the following:
• Site Characterization – delineation of study area, and review of available site data to
identify factors affecting the availability of contaminants to potential receptors, such as
location and medium of contamination.
• Identification of Chemicals of Potential Concern (COPCs) - identification of the
chemicals of potential concern based on site environmental monitoring data.
• Receptor Characterization - identification of “receptors of concern”, which in this study
include those persons with the greatest probability of exposure to chemicals from the
site and those that have the greatest sensitivity to these chemicals.
• Identification of Exposure Pathways – consideration of various factors that influence the
means by which receptors come into contact with COPCs in environmental media
including: chemical-specific parameters, such as solubility and volatility; characteristics
of the site, such as physical geography, geology, and hydrogeology; as well as the
physiology and behaviour patterns of receptors.
Exposure Assessment
The exposure assessment evaluates data related to all chemicals, receptors and exposure
pathways identified during the problem formulation phase of the HHRA. The primary objective
of the exposure assessment is to predict, using site-specific data and a series of conservative
assumptions, the rate of exposure (i.e., the quantity of chemical and the rate at which that
quantity is received) of the selected receptors to the COPCs via the various exposure scenarios
and pathways identified in the problem formulation step.
Relevant environmental media include:
• Surface soil;
• Indoor dust;
• Outdoor/Indoor air
• Home grown produce (i.e., fruits, leafy vegetables, root crops);
• Market basket foods (from non-local sources);
• Locally caught fish;
• Locally harvested wild berries;
• Drinking water; and
• Surface water.
Hazard Assessment Stage
Toxicity is the potential for a chemical to produce any type of damage, permanent or temporary,
to the structure or functioning of any part of the body. The toxicity of a chemical depends on the
amount of chemical taken into the body (referred to as the “dose”) and the duration of exposure
(i.e., the length of time the person is exposed to the chemical). For every chemical, there is a
specific dose and duration of exposure necessary to produce a toxic effect in humans (this is
referred to as the “dose-response relationship” of a chemical). The toxic potency of a chemical
(i.e., its ability to produce any type of damage to the structure or function of any part of the
body), is dependent on the inherent properties of the chemical itself (i.e., its ability to cause a
biochemical or physiological response at the site of action), as well as the ability of the chemical
to reach the site of action (i.e., bioavailability). The dose-response principle is central to the
HHRA methodology.
Exposure limits for this project will be selected from reputable regulatory agencies, with
recognized experience and expertise in the derivation of exposure limits to protect human health
(e.g., Health Canada, U.S. EPA, ATSDR, WHO, Cal EPA OEHHA, OMOE, etc). The exposure
limits selected for this HHRA will be scientifically defensible and those routinely accepted and
used by government departments on HHRAs conducted in Canada and elsewhere. In selecting
the limits, the scientific basis and date of last major review will be among the considerations.
Risk Characterization Stage Calculation of Risk Levels
The risk characterization step integrates the exposure and hazard assessments to provide a
conservative estimate of human health risk for the receptors assessed in the various exposure
scenarios. Potential risk will be characterized through a comparison of the estimated or
predicted exposures from all pathways (from the Exposure Assessment) with the identified
exposure limits (from the Hazard Assessment) for all chemicals of potential concern.
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