Upload
loraine-simpson
View
215
Download
0
Tags:
Embed Size (px)
Citation preview
Developing Analytic Forecasting Methodologies for Health Impact Assessment
Rajiv Bhatia, MD, MPHSan Francisco Department of Public Health
ForecastingPage 2
Rajiv BhatiaAlaska Health Impact Assessment Training 2008
Presentation Overview
The Distinction Among Assessment of Existing Conditions vs. Monitoring vs. Forecasting
Three Examples:Existing Forecasting MethodNew Method Based on Existing ResearchNew Method Based on New Research
Implications for Alaska HIA
ForecastingPage 3
Rajiv BhatiaAlaska Health Impact Assessment Training 2008
Example 1: Assessment and Mitigation of Roadway Air Pollution Impacts on Sensitive Uses
State and National air quality standards concern limited pollutants
Regional monitoring does not capture intra-urban variation in exposure
Regulations limit tailpipe emissions per mile but not vehicle intensity
Local agencies do not regulate air quality land use conflicts related to high volume roadways
ForecastingPage 4
Rajiv BhatiaAlaska Health Impact Assessment Training 2008
Available Health Effects Assessment Methods For Air Quality Assessment
Dose response functions can associate area-level air quality exposures with health effects
Air quality dispersion models and other techniques can assess roadway related air quality exposure based on: Vehicle Flow, Speed Emissions Meteorology Relationship between Facilities and Sensitive
Receptors
ForecastingPage 5
Rajiv BhatiaAlaska Health Impact Assessment Training 2008
Estimating Mortality Impacts From Exposure to PM2.5 based on CARB CR Functions
Mortality = R0 • [exp (-*∆PM2.5 -1) ] • P
R0 = Baseline Mortality Rate = Coefficient Derived from Relative Risk P = Affected Population
ForecastingPage 6
Rajiv BhatiaAlaska Health Impact Assessment Training 2008
Spatial Extent of Vehicle PM2.5 All Vehicle Sources using CAL3QHCR—West Oakland, CA
ForecastingPage 7
Rajiv BhatiaAlaska Health Impact Assessment Training 2008
Applications
Location of Sensitive Uses Transportation System Planning Indoor Air Quality Ventilation Standards
ForecastingPage 8
Rajiv BhatiaAlaska Health Impact Assessment Training 2008
Example 2: Quantifying the Health Benefits of a Living Wage
Few analyses health benefits of labor policies Plausible relationship meditated through material needs
Consistent association among high quality epidemiologic studies on income and health looking at multiple health outcomes
ForecastingPage 9
Rajiv BhatiaAlaska Health Impact Assessment Training 2008
Data Required For Impact Analysis
The baseline income of the population targeted by the living wage
The estimated income gains of workers benefiting from the new wage
A dose response function between income and health outcomes
ForecastingPage 10
Rajiv BhatiaAlaska Health Impact Assessment Training 2008
Inclusion Criteria For Studies Providing Dose-Response Relationships
English language peer reviewed literature 1990-1998 Studies of income and mortality, hospitalizations, or
health status indicators Subjects representative of the U.S. general population Income measured at the household, family or individual
level Longitudinal design Statistical adjustment for age and gender year of income
ascertainment provided Income applied as a continuous variable
ForecastingPage 11
Rajiv BhatiaAlaska Health Impact Assessment Training 2008
Estimated Health Effects Due To Living Wage Income Gains For Workers With A Current Family Income of $20,000
Study/Outcome Model Effect Measure Full Time Workers Part Time Workers
Backlund, 1996
Mortality-Male Proportional Hazards Hazard Ratio 0.94 (0.92-0.97) 0.97 (0.96-0.98)
Mortality-Female Proportional Hazards Hazard Ratio 0.96 (0.95-0.98) 0.98 (0.97-0.99)
Ettner, 1996
Health Status Ordered Probit Relative Risk 0.94 (0.93-0.96) 0.97 (0.96-0.98)
ADL Limitations Probit Relative Risk 0.96 (0.95-0.98) 0.98 (0.97-0.99)
Work Limitations Probit Relative Risk 0.94 (0.92-0.96) 0.97 (0.95-0.98)
CES—Depression Scale Two Part Elasticity -1.9% -1.1%
Number of Sick Days Two Part Elasticity -5.8% -3.2%
Alcohol Consumption Two Part Elasticity +2.4% +1.3%
Duncan, 1998
Completed Schooling OLS Regression Years of Schooling 0.25 (0.20-0.30) 0.15 (0.12-0.17)
H.S. Completion Logistic Regression Odds Ratio 1.34 (1.20-1.49) 1.18 (1.11-1.26)
Non-Marital Birth Proportional Hazards Hazard Ratio 0.78 (0.69-0.86) 0.86 (0.81-0.92)
ForecastingPage 12
Rajiv BhatiaAlaska Health Impact Assessment Training 2008
Example 3: Area-level Model of Pedestrian Vehicle Collisions
Transportation Analyses in EIA provides little analysis of Pedestrian Safety Impacts:
Vehicle-pedestrian injuries and fatalities are preventable.
Key area-level environmental determinants of collisions include: Traffic volumes Traffic speed Pedestrian activity
ForecastingPage 13
Rajiv BhatiaAlaska Health Impact Assessment Training 2008
An Environmental Approach:Evident area-level patterns – correlate with the freeway network, concentrations of streets with heavy arterial traffic, pedestrian activity centers (e.g., downtown, Golden Gate Park).
27 - 191
15 - 26
8 - 14
0 - 7
Number of Collisions
Highways/Freeways
Source: California Highway Patrol, Statewide Integrated Traffic Records System
0 3 61.5 Miles
Vehicle-pedestrian injury collisions: San Francisco, California census tracts (2001–2005)
ForecastingPage 14
Rajiv BhatiaAlaska Health Impact Assessment Training 2008
Model development framework
How do transportation, land use, and population factors predict change in pedestrian injury collisions in San Francisco census tracts?
Travel Behaviors:walking, public transit,
private vehicle use
Population Characteristics: number of residents and workers, socio-demographic characteristics
Built Environment: street and land use
characteristics
Vehicle-Pedestrian Collisions (Number):
pedestrian injuryand death
ForecastingPage 15
Rajiv BhatiaAlaska Health Impact Assessment Training 2008
Vehicle-Pedestrian Injury Collision Model
o Publicly available data (SWITRS, U.S. Census, SF Planning,
SF MTA)
o Traffic Volume, Street Characteristics – SF DPH/UC Berkeley
o Continuous, census-tract level variables
o Multivariate, linear regression model – predicts the natural log of vehicle-pedestrian injury collisions:
ln(PIC) = b0 + ∑biXi
ForecastingPage 16
Rajiv BhatiaAlaska Health Impact Assessment Training 2008
Vehicle-Pedestrian Injury Collision Final Model Variables
Traffic volume (+) Arterial streets (+) Neighborhood commercial zoning (+) Employees (+) Residents (+) Land area (-) Below poverty level (+) Age 65 and over (-)
ForecastingPage 17
Rajiv BhatiaAlaska Health Impact Assessment Training 2008
Final Ordinary Least Squares Regression Model Vehicle-Pedestrian Injury Collisions: San Francisco, California, 2001-2005 (n=175 census tracts)
a Excludes grade-separated street segments inaccessible to pedestrians.
Census Tract-Level Variable Coefficient SE p-value95% CI, Lower
limit95% CI, Upper
limitTraffic volume
(n, natural log, aggregated average daily traffic counts )a 0.753 0.115 0.000 0.526 0.981
Arterial streets, without public transit (%, street length) 0.017 0.004 0.000 0.009 0.025Neighborhood commercial (%, land area) 0.029 0.007 0.000 0.016 0.042Residential-neighborhood commercial (%, land area) 0.021 0.006 0.000 0.009 0.032Land area (square miles) -0.704 0.195 0.000 -1.089 -0.319Employee population (n, natural log) 0.228 0.046 0.000 0.136 0.319Resident population (n) 0.00010 0.00003 0.000 0.00005 0.00015Living below the poverty level last year (%, resident population) 0.019 0.006 0.003 0.006 0.031Age 65 and older (%, resident population) -0.016 0.007 0.013 -0.029 -0.003
Constant -9.954 1.283 0.000 -12.488 -7.420Adjusted Pearson R2
0.7154
ForecastingPage 18
Rajiv BhatiaAlaska Health Impact Assessment Training 2008
Comparing the Simple Bivariate Model to Our Multivariate Model Approach
Holding all covariates constant (as above), the model is equivalent to a power function with β=0.753.
0
10
20
30
40
50
60
70
80
0 10 20 30 40 50 60 70 80 90 100
% Increase in Traffic Volume
% In
crea
se in
Ped
estr
ian
Inju
ry C
olli
sio
ns
PF: β = 0.8
FM: β = 0.753
PF: β = 0.5
PF: β = 0.25
ForecastingPage 19
Rajiv BhatiaAlaska Health Impact Assessment Training 2008
Vehicle-Pedestrian Injury Collision Model: Eastern Neighborhoods Plans EIR Analysis
Census Tract Characteristics
Traffic
Volumeb (CT sum)
Population (CT sum)
Traffic
Volumeb (% increase, CT)
Populationd
(% increase, CT)
San Francisco (N=176) 212,238 776,733 na na
Eastern SOMA (N=5)a 20,550 19,954 15%c 25%
Mission (N=13)a 20,307 60,202 15%c 8%
Show Place Square/Potrero
Hill (N=9)a 27,771 20,984 15%c 39%
Central Waterfront (N=3)a 8,682 6,397 15%c 58%
All Eastern Neighborhoods
(N=23)a 52,602 91,109 15%c 16%
Planning Area (N, Census Tracts)
Existing Conditions Estimated Changes
a Areas defined based on SF Planning boundaries, and census tracts used for the Eastern Neighborhoods Rezoning Socioeconomic Impacts analysis.
b Census Tract, Aggregate Traffic Volumes. c Based on the Air Quality Chapter, Eastern Neighborhoods Pre-draft Environmental Impact Report, 2007. d Population increases based on increased population and housing units projected in Rezoning Option B, detailed in the
draft Eastern Neighborhoods Rezoning and Community Plans, Environmental Setting and Impacts, April 2007.
ForecastingPage 20
Rajiv BhatiaAlaska Health Impact Assessment Training 2008
Vehicle-Pedestrian Injury Collision Model: Eastern Neighborhoods Plans EIR Analysis
20%
21%
15%
24%
Predicted % change in pedestrian injury collisions based on estimated changes inresident population and traffic volume.
ForecastingPage 21
Rajiv BhatiaAlaska Health Impact Assessment Training 2008
Vehicle-Pedestrian Injury Collision Model: Application
Land Use Development Transportation Facilities Planning and
Funding Congestion Pricing and other
Transportation Policy
ForecastingPage 22
Rajiv BhatiaAlaska Health Impact Assessment Training 2008
A General Approach to Predicting Health Effects Using Epidemiological Research
1. Develop Clear Analytic Objectives2. Literature Review
A. Develop study criteria and data needsB. Identify SourcesC. Establish Adequacy of Existing ReviewsD. Evaluate studiesE. Formal summary and documentation of review
3. Make qualitative inferences on health effects 4. If appropriate and feasible, quantify effects
A. Select or generate a summary effect measureB. Estimate Baseline and Changes to “Exposure”C. Predict Health Impacts (PAR, Forecasting)
5. Qualify certainty of assessment & predictions
ForecastingPage 23
Rajiv BhatiaAlaska Health Impact Assessment Training 2008
Developing Forecasting Methods for Alaskan HIA
Some environmental - health relationships may be generalizable from general population studies
HIA forecasting methods in Alaska probably requires new research environmental-health relationships
Data collection and monitoring will support long term research efforts