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COMPARATIVE RISK ASSESSMENT:
SETTING PRIORITIES FOR URBAN ENVIRONMENTAL MANAGEMENT IN
DEVELOPING COUNTRIES
Presentation by Barbara Britton
January 18, 2000
OUTLINE OF PRESENTATIONPart I Introduction and Background
Part II International Experience with CRA
Part III Methodology
PART I: INTRODUCTION AND BACKGROUND
HISTORY OF COMPARATIVE RISK ASSESSMENT
First used in the U.S. in 1987– “Unfinished Business” evaluated 31 problems and
changed USEPA priorities
– Many projects completed for regions, states, and cities
Used outside the U.S. by USAID and USEPA– First assessment was in Bangkok, 1990
– Assessments completed for about 10 cities and regions
What DID EPA Learn From Comparative Risk Efforts?
Chemical-Specific, Media-Specific, Technology-Based Approaches have Limitations
Policies Based on Comparative Risk Assessments Could Lead to More Efficient Use of Resources and Greater Protection of Public Health and the Environment
ENVIRONMENTAL MANAGEMENT
Comparative Health Risk Assessment is used to set priorities for environmental management.
Risk Assessment
Risk Management
Identify and evaluate risks, set prioritiesamong problems.
Develop andimplement solutions forhigh priority problems
ENVIRONMENTAL RISKS
Environmental damage may have three types of negative effects.
Public Health--illness, injuries, deaths
Ecological--loss of species and habitat
Quality of Life--economic and social costs
TYPES OF “RISK ASSESSMENT”
Health Risk Assessment:evaluates the potential public health impacts of an environmental condition
Comparative Health Risk Assessment:evaluates and compares the potential healthimpacts of several environmental conditions
Comparative Risk Assessment:evaluates and compares the potential health,ecological, and quality-of-life impacts ofseveral environmental conditions
PART II: INTERNATIONAL EXPERIENCE WITH
COMPARATIVE RISK ASSESSMENT
International Experience WithComparative Risk Assessment
Bangkok: Accelerated plans for banning lead in gasoline
Cairo: USAID projects to reduce air pollution and lead contamination
Ahmedabad: Municipal program to reduce air pollution from transport
Lima: USAID environmental health project under design
Silesia: USAID technical assistance to high risk industrial facilities
“HIGH RISK” PROBLEMS FROM FIVE CRAs
Environmental Problem Categories Bangkok Quito Cairo Ahmedabad Lima
Water, Sanitation, orMicrobial Diseases
Ambient PM
Indoor Air
Lead
Air Pollution from Transport
Solid Waste
CRA RESULTS: BANGKOK
Bangkok, Thailand (1990)
Airborne Particulate MatterLead ContaminationMicrobiological Diseases
Carbon Monoxide (CO)Other Metals
Toxic Air Pollutants
Surface Water ContaminationGround Water ContaminationPesticides & Metals in FoodSolid & Hazardous Wastes
High
Moderate
Low
Other Gaseous Air Pollutants (SO2, NO2, O3)
CRA RESULTS: CAIROCairo, Egypt (1994)
High
Moderate
Moderate/Low
Low
Airborne Particulate MatterLead (all media)Microbiological Diseases
Microbiological Contamination of FoodOzone
Other Gaseous Air Pollutants (SO2, CO)
Indoor Air PollutionDrinking Water (microbes, chemicals)Solid and Hazardous Wastes
Toxic Air PollutantsOther Water Pathways (e.g. fish, irrigation)
CRA RESULTS: AHMEDABAD
Ahmedabad, India (1995)
High
Moderate
Low
Air Pollution from Mobile SourcesAmbient Air Pollution (all sources)Indoor Air Pollution
Drinking WaterWastewater
Occupational HazardsTraffic HazardsFood Contamination
CRA RESULTS: LIMA
Lima, Peru (1997)
High
Moderate
Low
Inadequate Water SupplyInadequate SanitationSolid Waste
Surface and Groundwater ContaminationFood ContaminationAir PollutionWater Pollution (marine)
Hazardous WasteToxic SubstancesIndoor Air PollutionLoss of Landscaped Areas & Farm Land
PART III: COMPARATIVE RISK ASSESSMENT
METHODOLOGY
STEPS IN RISK ASSESSMENT
Health risk assessment is quantitative, based on experimental and observational data.
Hazard Identification--identify health risks associated with exposure
Dose-Response Assessment--model the relationship between dose and effects
Exposure Assessment--estimate a group’s exposure (amount, duration)
Risk Characterization--estimate the probability and severity of effects
CONCEPTUAL MODEL LINKING ENVIRONMENTAL CONDITIONS AND
HEALTHSource
Discharge
Transport and Fate in the Environment
Transport and Fate in the Body
Dose Target Organs
Exposure
IntakeDamage, Disease, or Death
EXAMPLE:HEALTH RISK ASSESSMENT
Health Risk Assessment in Bangkok:
Population: 5.9 million
Airborne particulates: 90 - 200 g/m3
Health effects (per year): 9 - 51 million restricted activity days 300 - 1400 deaths
EXAMPLE:HEALTH RISK ASSESSMENT
Health Risk Assessment in Quito, Ecuador:
Population: 1.1 million
Pesticides in food:44.3 g/day intake of heptachlor11.0 g/day intake of aldrin
Health Effects:0.3 to 9.1 x 10-3 lifetime cancer riskUp to 150 excess cancer cases/year
EXAMPLE: COMPARATIVEHEALTH RISK ASSESSMENT
Quito, Ecuador (1993)
Risk Metropolitan Area
High Microbiological Diseases (Food)Airborne Particulate Matter
ModerateTraffic InjuriesDrinking Water and WastewaterIndoor Air QualityOccupational Disease and Injuries
LowSolid & Hazardous Waste DisposalPesticides in Food
Asentamientos Populares
Microbiological Diseases (Food)Airborne Particulate MatterIndoor Air QualityOccupational Disease and InjuriesDrinking Water and Wastewater
Traffic InjuriesSolid & Hazardous Waste Disposal
Pesticides in Food
CRA METHODOLOGY
¶ Planning Determine scope of the study Select and organize the team Identify data types and sources
Data Collection and Analysis Identify and gather data Analyze data to estimate risks
Priority Setting Interpret and compare risks Debate and agree on priorities
Reporting Prepare report as input to risk management planning
Four Phases of Comparative Risk Assessment
FUNCTIONS AND RESPONSIBILITIESFunction Typical Unit
Project Management and oversight
Policy direction and project mandate
Public participation
Final risk ranking
Technical analysis--data collection, risk assessment, preliminary ranking
Project Manager
Steering Committee
Public Advisory Committee
Steering Committee or Public Advisory CommitteeTechnical Committees
The organization of a CRA must address five necessary functions:
PARTICIPATORY ASPECTS OF CRAs
Broad participation is critical because:
•Analysis is multi-disciplinary and highly complex•Setting priorities are ultimately based on values of the community•Broad participation is linked to acceptance of CRA results and implementation of actions to reduce risks
TECHNICAL ANALYSIS
Identify and evaluate health impacts of many environmental conditions– water and food
– sanitation, drainage, and wastewater
– ambient and indoor air, gases and particles
– solid and hazardous wastes
– occupational injuries and exposures
– infectious, vector-borne, and pollutant-related diseases
ADAPTING TECHNICAL ANALYSIS FOR CRA IN DEVELOPING COUNTRIES
ISSUE RESPONSE
Scope includes infectious diseases, outside traditional risk assessment methods
Limited information and many data gaps.
Use health data from clinics and local survey to estimate disease rates.
Use environmental, health, and qualitative data
Data are not computerized and are aggregated at inappropriate geographic levels.
Reorganize information; use assumptions and extrapolation where necessary.
Some standard exposure assumptions are inappropriate due to culture or conditions.
Adjust assumptions; conduct special studies if possible.
PRIORITY SETTING Categorize each health impact by magnitude and
severity magnitude -- number of people affected
severity -- of effect, and importance of group affected Combine magnitude and severity scores Compare and categorize environmental problems
high, medium, and low risk
CRA Risk Ranking
Risk ranking requires judgments based on values
Comparing health effects:acute vs. chronic disease vs accidents
Comparing effects among groups:children vs. working adults vs. elderlypoor vs. middle incomevoluntarily exposed vs. involuntary exposedwomen vs. men
Conclusion
CRA’s can form an effective basis for urban environmental management planning
Allow cities to address worst environmental problems first
Broad-based participation is crucial to ensure risk ranking reflects views of entire community
Stakeholder involvement is pivotal to ensuring risk assessment results translate into management action