Transcript Slide 1

AFCEE, 2002
Human Health Risk
Assessment and
Chemical Safety
Stephanie Simstad
The Ohio State University Extension
Clermont County
Acknowledgements
• U.S. EPA risk assessment documents
including:
– Risk Assessment Guidance for Superfund
– Presenter’s Manual for “Superfund Risk
Assessment and How You Can Help”
What if . .
Ohio EPA
• Your private water well has been sampled
and results show that a commonly used
pesticide is present in your drinking water.
• How would you determine whether this
contaminant could be a health problem for
your family?
Overview
• Description of risk assessment and how it is
•
•
•
used
Use of human health risk assessment process to
evaluate a contaminated family well
Group exercise to identify source and pathways
of pesticide into well
Consideration of exposure pathway analysis to
identify Best Management Practices for
protection of drinking water sources
Human Health Risk Assessment
• A formalized process to evaluate risk
posed to humans from exposure to an
identified hazard
– Evaluation of both cancer and noncancer
effects
– Evaluation of risk to adult, child, or even
prenatal populations
Hazard versus Risk
• Hazard
(OEPA)
– Potential to do harm
• tornado
• hazardous chemical
• Risk
– Likelihood of defined harm to
occur from specific hazard
• 1 additional cancer per 10,000
people exposed
(NOAA)
Individual
Lifetime Risk of
Developing
Melanoma is
1 in 75.
(NIH)
How is Risk Assessment Used?
• To set drinking water standards for public
water supplies
• Licensing and regulation of pesticides
• Identification and clean-up of hazardous
waste sites
• Identification of special handling
requirements for chemicals
Back to the Well . . .
• You’ve found that the family well is
contaminated and you use this water for
drinking, cooking, and bathing.
• How would the risk to those who use
water from the well be evaluated?
Risk Assessment is a 4-Part Process
• Hazard Identification
– What chemicals are present and are they likely to be
toxic?
• Exposure Assessment
– Who is exposed, at what concentration, how often,
and for how long?
• Toxicity Assessment
– How is it toxic and at what exposure levels?
• Risk Characterization
– What does the risk assessment tell us about this
situation?
Risk Assessment Process
(U.S. EPA)
Hazard
Identification
Exposure
Assessment
Toxicity
Assessment
Risk Characterization
Step 1:Hazard Identification
• Collect data on presence of
chemical
– Sampling
– Modeling
– Chemical fate and transport
• Determine if chemical may be toxic
• Develop model of how chemical
AFCEE, 2002
may move through environment
– Conceptual Site Model is used to
organize information regarding
chemicals and potential transport to
people
© Vermont DPS, 2000
Input for Conceptual Site Model
Modified from Oak Ridge (2002)
How are
chemicals transported
to receptors?
Who may be
exposed?
How may
they be
exposed?
How does
exposure change
through time?
Conceptual
Site Model
What information
is missing?
Modeling of Chemicals in the
Environment
• Chemical characteristics
– More or less soluble in water?
• Soil and connections to surface and ground
water
– Type of soil
– Likely paths to and through water sources
• General Concept
– Based on knowledge of the chemical, the soils, and
local water sources; predictions can be made about
how that chemical will move through the
environment.
Conceptual Site Model
(Oak Ridge National Lab, 2002)
Step #2: Exposure
Assessment
• Who is Exposed?
– Adult, Child, Special Populations
• How Are They Exposed?
– Ingestion, Inhalation, Skin Contact
• What is the Concentration of Chemical to
Which They are Exposed?
– ppm in Water or Soil
• How Often Are They Exposed?
– Days per year, Number of years
Exposure Pathway
• Definition: The steps that a chemical takes from
the source to an exposed individual
– Exposure is contact with a chemical through either
swallowing, breathing, or direct contact on skin
Spilled
Container
Soil
Groundwater
Well
Path Traveled by Chemical
SOURCE
Individual
Using Well
Exposed
Individual
Exposure Pathway Diagram
(ATSDR, 2002)
Complete Exposure Pathways
• Key to Risk Assessment is Identifying
Complete Exposure Pathways
– Individual must have contact with
chemical for it to cause a health effect
Chemical
Contact
Receptor
Complete Exposure Pathway
• Steps in Complete Exposure Pathway
– Source
– Chemical Transport and Transformation
– Exposure Point
– Receptor and Exposure Route
Spilled
Container
SOURCE
Soil
Groundwater
CHEMICAL TRANSPORT
Well
EXPOSURE
POINT
Individual
Drinks
Water
RECEPTOR
AND
EXPOSURE
ROUTE
Exposure Point and Exposure
Route
• Exposure Point defines the place that an
individual comes into contact with the
chemical
– Home with lead-contaminated paint
• Exposure Route describes the way a
chemical enters the body
– Ingestion (Eating and Drinking)
– Inhalation (Breathing)
– Dermal (Skin Contact)
Exposure Pathways
• All exposure pathways are not obvious
– Ingestion of contaminated soil
• Children during play (200 mg soil /day)
• Children who deliberately ingest soil (1 gram
soil/day)
• Incidental ingestion by adults (100 mg soil/day)
– Inhalation of chemical vapors
• During showering with contaminated water
– Volatile chemicals will vaporize into the air from
the shower water, they can then be inhaled by
person showering
• Vapor migration into homes from contaminated
ground water or soil under homes
Identify Source and Potential
Exposure Pathways
(Oak Ridge National Lab, 2002)
Back To Contaminated Well
Example. . .
• Who is exposed when family farm well is
contaminated?
• What are their routes of exposure?
Drinking Water
Well
?
Receptors
?
Routes of
Exposure
Exposure Assessment
• Purpose is to calculate dose that individual
receives
– Dose represents a daily average intake per unit of
body weight
• Use information from conceptual site model and
•
•
sampling to identify complete exposure
pathways
Calculate dose for each exposure pathway by
using exposure assumptions
Sum goes across all pathways to get total dose
Exposure Assumptions
• Answer “how much” and “how often” people
•
may be exposed to chemical in air, water, soil or
dust
Examples
– How much water does an adult drink in one day?
– How many days per year is someone at their home?
– How many years does someone live in the same
house?
Why Calculate Dose?
• Paracelsus
(15th
century scientist)
Courtesy of the National
Library of Medicine
– “Dose makes the poison”
• For most chemicals, there is a threshold below
which health effects are unlikely to occur
– HOWEVER for some cancer-causing chemicals, a
threshold is not assumed to exist
• Toxicity data can then be compared with dose to
determine if health effect likely to occur
Dose-Response Curve
Dose – Chemical concentration per unit body weight
Response – Level of measured adverse effect
Putting it all together. . .
C  CR  EF  ED
Intake Dose (mg/kg  day ) 
BW  AT
• Intake Equation for Drinking Water Example
C= Chemical Concentration (Obtain from sampling)
CR= Contact Rate (2 liters water/day)
EF= Exposure Frequency (350 days/year)
ED= Exposure Duration (30 years)
BW=Body Weight (70 kg.)
AT= Averaging Time (10,950 days)
Special Concerns During
Exposure Assessment
• Children
– Children will often have a higher dose than
adults when exposed to the same chemical
concentration in the environment
• Differences in children’s activities
– Playing in dirt, infant mouthing of toys, formuladominated diet of young infants
• Water, food, and air intake per pound of body
weight can be higher for children than adults
Step #3: Toxicity Assessment
• What toxicity data are available?
– Acute or chronic effect? Or both?
– Cancer or noncancer effect? Or both?
• Consider effects of multiple chemicals
– Similar to “Mode of Action” concept in pesticides but
broader since multiple nonlethal effects can still have
an adverse impact on human health
• Consider route of exposure
– Effects can be route of exposure specific
Sensitive Subpopulations
• Children
– Rapid development and differing physiologies
of young children can result in potentially
greater sensitivity to contaminants
• Lead exposure and the developing brain
– Exposure to lead during prenatal or early childhood can
cause irreversible intelligence losses
– What are potential sources on the farm for lead exposure
to children?
Sensitive Subpopulations
• Children or adults with health problems
– Compromised immune systems
• Undergoing chemotherapy
• Organ transplant patients
• Diseases affecting immune system
– Other diseases that affect body system that chemical
exposure may target
• Children or adults with “hidden” sensitivities
– Genes can increase or decrease susceptibility to
environmental factors and can therefore modify risk
Distinction between Cancer and
Noncancer Effects
• Calculation of dose and some exposure
assumptions differ
• Large number of carcinogenic contaminants are
assumed to have no threshold
What would doseresponse curve
look like if we did
not assume a
threshold existed?
Hint: An effect
would be seen at
any dose level.
Step #4: Risk Characterization
The risk
characterization
combines the
information
obtained on
toxicity with the
calculated
exposure to
provide an
estimate of risk.
Purdue, 1997
Risk Characterization Answers
• What is the likelihood of harm
following exposure to this chemical
in this specific situation?
– Provides a numerical estimate of risk
– Identifies key uncertainties in this estimate
– Compares numerical estimate of risk with a
previously determined risk goal
Risk Goal
• Most environmental programs have a specified
•
risk goal which has gone through review
Risk goal is a policy determination
– Risk goal is numerical estimate of acceptable risk for
cancer or noncancer effects.
• 1 in 1,000,000 for cancer or the level of reference dose
(threshold + uncertainty factor) for noncancer effect.
• Compare numerical estimate of risk with risk
•
goal
If risk goal is exceeded, risk management
decision necessary
Risk Assessment is One Part of
Decisionmaking Process to Manage
Hazards
• Science
•
determines
likelihood of
effect but risk
management
determines
whether and
how the risk
should be
addressed
Policy decision
What Does Risk Assessment Not
Tell Us?
• Whether risk is “acceptable”
• Whether risk is equitably distributed
across population
• Predictions regarding personal or
individual risk
Summary
• Risk assessment is a 4-part process to evaluate risk from
suspected hazards.
–
–
–
–
Hazard Identification
Exposure Assessment
Toxicity Assessment
Risk Characterization
• For a hazard to have an adverse impact on health, there
•
must be contact between the receptor and the hazard.
Exposure must occur.
Children and other sensitive subpopulations can have
greater exposure and toxicity to the same environmental
conditions than other adults.
Summary contd.
• Risk goals are used as a comparison point
with calculated risk values. These are
policy, or nonscientific, determinations.
• Risk characterization
– defines the risk relative to the risk goal,
– identifies uncertainties, and
– identifies receptors and exposure pathways of
most concern.
Summary contd.
• Risk management is the decisionmaking
process to determine whether to take
action for an identified risk.
Case Study Scenario
• Smith family well was found to have
“herbex” contamination
• Both neighboring farms have used or stored
herbex
• Handouts
–
–
–
–
Risk Assessment Case Study Map
Pesticide Application Worksheet
Participant worksheet to complete
Herbex label
Case Study Map
Pictures of Storage Sheds
Mr. Ulright’s Shed
Mr. Sorong’s Shed
Hints
• Examine map closely
• Environmental information from herbex
label
• Review Pesticide Application Worksheets
• Complete participant worksheet to aid in
identifying all parts of exposure pathway
Case Study Answers
• Working back from the contaminated well
– What are some possible sources and
associated pathways?
– Which source and pathway do you believe to
be the most likely cause? Why?
BMP’s to Prevent Potential Well
Contamination?
• Pesticide Selection?
• Pesticide Storage?
• Pesticide Application Practices?
• Well Placement?
• Well Maintenance?
• Well Abandonment?
And How Can You Use Your New
Risk Assessment Knowledge?
• Think about the possible ways that
chemicals stored or used at your farm
could reach receptors, especially through
drinking water pathways.
X
Consider Drinking
Water Sources
• Be aware of drinking water sources
that could be affected by your use of
agricultural chemicals
– Private family wells? Public Water Supply wells?
– Nearby reservoirs used as public water
sources?
– Drinking water intakes in rivers or streams?
• Take necessary steps to protect them
Consider Local Conditions When
Selecting Pesticides
• Be aware of geologic and hydrologic
conditions when selecting pesticides
– Type of soils
• Sand versus clay?
– Location of surface water bodies and runoff
pattern of surface water
– Location and depth of ground water
Think:
If you have shallow groundwater and sand/gravel soils,
what should you be concerned about if you choose to apply a
highly water soluble pesticide?
Consider Local Surface
Water Quality
Conditions
• Be aware of local water quality conditions
when selecting pesticides
– Are there any identified problems with pesticides in
water, sediment or fish in local streams or rivers?
• See Ohio EPA’s web site and associated reports
– Join your local watershed group!
• Most watersheds in the state have a watershed
coordinator and group working to improve water quality
OEPA
Consider and Use
Appropriate BMPs
University of Arizona
• Be aware of BMPs when
storing and applying pesticides
– Store properly and be prepared
for spills
– Read and follow the label!
• Drinking and surface water
U.S. EPA
advisories (e.g., Atrazine)
– Use buffer strips and maintain
streamside areas in natural state
NRCS