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Scenario

 Exposure Assessment

The exposure assessment estimates the dose of contaminant that people coming into contact with the contaminated site will receive while engaged in specific activities.  Doses are quantified using algebraic equations.  Investigators can estimate the external dose (amount of contaminant that a person comes into contact with), absorbed dose (amount of contaminant that makes it into the body) or biologically effective dose (the amount of the contaminant that actually causes harm to the affected organ or tissue system), depending upon the scientific understanding of the contaminant and the resources available to study it. Site-specific information should be incorporated into the exposure assessment in order to provide meaningful estimates of dose. The site conceptual model is used as a guide to decide which exposure pathways should be evaluated in the exposure assessment.

    Hazard Identification Risk Characterization Uncertainty Analysis Dose-Response Assessment


Exposure scenarios need to be constructed based on:

  • Current and potential future use of contaminated areas
  • The potential for the hazardous substance to cause adverse effects.
  • The audience of the risk assessment and the questions that you ultimately need to answer. For example, community members will be interested in how much exposure their children will receive, and risk managers want to know the worst case scenario for the maximum exposure possible.

Then, for each exposure scenario one must collect data and calculate estimated doses

  • Potential dose (e.g. the amount of contaminant in the air)
  • Applied dose, i.e., the intake or administered dose or the amount actually taken in (e.g. inhaled)
  • Absorbed dose i.e., the uptake or internal dose or delivered dose(e.g., the amount absorbed by the lung into the blood stream)
  • Biologically effective dose, i.e. the dose at the target tissue.

For each scenario calculations must take into account not only the receptors (who might be exposed) and their activities, but also the dimensions of :

  • Intensity: concentration of exposure
  • Frequency: number of times exposed
  • Duration: length of exposure. Was it acute (hours to days) or chronic (many years). For example, the response to 30 cups of coffee consumed during a 24 hour period would certainly be different from 1 cup per day over a period of 30 day.

The Average Daily Dose:

The final step of the exposure assessment is to calculate the average daily dose (ADD) for each contaminant of concern and each exposure route. Each ADD reflects exposure to a single COC by a specific exposure route.   If multiple exposure routes exist for the same COC, then the sum of the ADDs for each route serves as a measure of total dose.  If there are multiple COCs, then multiple ADDs must be calculated. 

For example, an average daily dose for ingestion of residential drinking water could be calculated from:

Average Daily Dose (mg/kg body weight/day) =   (CW x IR x EF x ED)/ (BW x AT)

 where:

CW = Chemical concentration in water (mg/liter)
IR    = Ingestion rate (liters/day)
EF  = Exposure frequency (days/year)
ED  = Exposure duration (years)
BW = Body weight  (kg)
AT  = Averaging time (days)

The values for each of these variables is not always known. Consequently, one frequently utilizes widely accepted assumptions or typical values.

CW: May be measured at the site or modeled values may be used (e.g., estimated based on information about a chemical spill adjacent to the site of interest)

IR        = 2 liter/day - adult, 90th percentile value or
            = 1.4 liters/day - adult, average value or
            = x liter/day based on age-specific values

EF        = 365 days/year for residential scenario

ED       = 30 years - 90th percentile value for time in one residence or
             = 9 years - 50th percentile value for time in one residence

BW      = 70 kg - adult, average value or 
             =x kg based on age-specific values

AT       = ED x 365 days/year for non-carcinogenic effects or 
            = 70 year lifetime x 365 days/year for carcinogenic effects

Some chemicals are quickly excreted from the body naturally, while others accumulate within the tissue.  Sampling these tissues or bodily fluids allows for the measurement of absorbed dose. 

Biomarkers are biochemical, physiological, and histological changes ithat can be used to estimate either exposure to chemicals or the effects of exposure to chemicals. Some examples of biomarkers include blood, urine, hair, and fatty tissue.  Because of the invasive nature of biomarker collection, it is often difficult to use them for exposure assessment.

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