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Mapping the uninsured using secondary data: an environmental justice application in Dallas

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Abstract

Over the last 5 years, environmental justice (EJ) researchers have been calling for incorporation of health outcomes more directly into spatial studies of socio-demographics and environmental hazards. To date, researchers have not incorporated insurance status (an access to health care variable) in their models although access to care likely has an important association with the probability of health effects due to environmental exposures. As such, insurance status represents an important variable within spatial EJ studies focused on health, and the lack of spatially explicit access to care data is a critical limitation in the field. As a solution, we offer a method of using uninsured appendicitis cases, acquired secondarily from state hospital admissions data, to estimate rates of uninsurance at the zip-code level. We apply the technique to explore relationships between cancer risk from hazardous air pollutants and estimated rates of uninsurance, a previously unexplored phenomenon. Then, we compare the uninsurance findings to those related to poverty to illustrate how uninsurance, as a variable, compares to a more traditional socio-economic predictor used in EJ studies. The relationship between cancer risk from hazardous air pollutants and uninsurance is weaker than the relationship between risk and poverty, but both are statistically significant. As such, we conclude with a discussion of the importance of considering insurance status in spatial studies of EJ focused on health.

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Fig. 1

Notes

  1. Only a few EJ researchers have predicted actual heath outcomes, i.e., asthma hospitalizations, using socio-demographics and air pollution (Grineski 2007; Maantay 2007), although several others have used socio-demographic characteristics to predict estimated health risks from hazardous air pollutants (HAPs) based on toxicology (e.g., Chakraborty 2009).

  2. Appendicitis is most common among older children and young adults, with a peak incidence the second and third decades of life. It is quite uncommon in children under five and the elderly (Prystowsky et al. 2005). Therefore, this method undercounts uninsurance for these groups. In addition, the hospitalization counts are suppressed in very rural areas (Texas Health Care Information Council 2000), so this method underestimate uninsurance in rural communities.

  3. As such, we compared the percent of uninsured cases of appendicitis in Texas to estimates of un-insurance published by the Texas Medical Association. In our appendicitis data set (2003–2005), 21.4% of all cases of appendicitis were uninsured; this compares favorably to 24.5% of all Texans being uninsured in 2005 (Texas Medical Association 2009) given the differences in methodology, time frame, and limitations (e.g., missing the very rural patients in the appendicitis data set).

  4. We ran bi-variate spatial lag regression models using GeoDa software due to spatial autocorrelation (i.e., tendency of variable values to relate to neighboring value, see Chakraborty 2009), as opposed to just presenting basic Pearson correlations. We found positive spatial autocorrelation in the residuals (i.e., the Moran's I values were significant at a p value of 0.001) for both models. Then, the Lagrange Multiplier test suggested spatial lag models (as opposed to spatial error models), and the two models reported in Table 3 were run with weights matrix of 14,000 meters because the spatial autocorrelation was removed at that distance (i.e., Moran’s I values became insignificant at p < .05 level).

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Correspondence to Sara E. Grineski.

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Grineski, S.E., McDonald, Y.J. Mapping the uninsured using secondary data: an environmental justice application in Dallas. Popul Environ 32, 376–387 (2011). https://doi.org/10.1007/s11111-010-0129-6

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