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1
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2
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- Needs of Visualization for Tracking
- Mapping Disease Rates
- Failure of mapping in discrete areas
- Density estimation
- Strengths and Weaknesses
- Modeling of Traffic-Exhaust Pollution
- Methods: Cost-Benefit Analysis
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3
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- We need a system that is continuous and ongoing
- We need web-based tools that allow public access and ability to
interface with data
- We need to preserve data confidentiality and privacy
- The system is not complete until those who need information
- Know the information exists
- Know where to find it
- Know what its good for
- Are able to access and interpret it
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4
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- Failure of mapping rates in discrete areas
- Sample size problem: law of
small numbers
- Instability of rates with small denominators
- As areas get smaller, variability increases
- Visualization fails
- Political boundaries change over time (e.g. ZIP codes)
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5
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- Methods of Openshaw,
- Rushton
- Produce continuous surface of rates
- Preserves data confidentiality
- More accurately reflect reality
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6
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- Restricted births to:
- completed birthweight
- geocoded address
- downtown San Diego and nearby areas
- compatible birthweight and gestational age
- 16,385 births 1980
- 24,274 births 1990
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7
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- (1) Generated Uniform Grid 0.5 miles apart (spatial filters)
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8
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9
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- (2) Identified all births within a 0.5 mile spatial filter (min. of 40 births to compute rate)
- 3) Compute LBW rates and made contour maps
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10
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11
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12
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13
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14
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15
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- Assign each birth equal probability of being a LBW birth
- Assign a random number (1-1000) for each birth
- Classify each birth as LBW or non-LBW
- Compute LBW rate at each grid point 1000 times
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16
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- Compute the % of simulated rates
which are less than the observed rate.
- Make map of statistical significance
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17
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18
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- Need for geocoded denominator
- Need for sensitivity analysis:
- size of filter needs to change in relation of density of health
events?
- Spatial autocorrelation an issue in analysis: Spatial regression
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19
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- Proximity Analyses
- Dispersion Models
- Land-Use Regression
- Integrated-Meterological Models
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20
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21
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- Strengths:
- Easy to use (adapt with Gaussian weights)
- Distance of residence to road correlates well with personal and
ambient NO2 monitoring (Rijnders,et al 2001)
- Weaknesses:
- Exposure misclassification likely without wind direction data
- Does not model actual level of pollutants
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22
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23
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- Strengths:
- More accurately measuring dispersal of pollutants
- Model actual pollutant levels
- Weaknesses:
- Is gaussian plume realistic model?
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24
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25
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- Strengths:
- Use land use, met data, DEMs, traffic to predict pollutant
concentrations
- Easily obtained data
- Weaknesses:
- Need enough monitoring locations for callibration/validation
- Need to replicate in new areas; models developed in one geographic
location may not be predictive in other areas.
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26
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- ADMS-Urban: Strengths:
- Incorporates mobile, point, and area sources
- Ability to model gridded emissions and terrain simultaneously
- model 10,050 receptor points
- boundary layer effects and dispersal behaviors over complex terrain
- photochemistry.
- seamlessly integrated with ArcView GIS
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27
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- ADMS-Urban:
- Weaknesses::
- Significant training and expertise necessary
- Cost
- Multiple data inputs
- What is the bang for the buck?
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28
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29
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- Cost/sample size makes these activities prohibitive for tracking
- Subsample analysis?
- Survey data on time activities
- Commuting important exposure time:
- Use of Transportation demand models?
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30
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- Integrating density estimation techniques important for visualization
and analysis of health tracking data increased method development
necessary
- Various approaches for traffic-exhaust modeling for tracking Need to
capture most accurate method over the most population at least cost
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