Original Investigation
Transplantation
Ambient Air Pollutants and Risk of Fatal Coronary Heart Disease Among Kidney Transplant Recipients

https://doi.org/10.1053/j.ajkd.2011.05.017Get rights and content

Background

There is increasing evidence that specific ambient air pollutants are associated with coronary heart disease (CHD) morbidity and mortality. Because kidney transplant recipients have prevalent traditional and nontraditional risk factors, they may constitute a sensitive subgroup.

Study Design

Retrospective cohort.

Setting & Participants

This study includes 32,239 nonsmoking adult kidney transplant recipients who underwent transplant in 1997-2003, identified through the US Renal Data System and living in the United States within 50 km of an air pollution monitoring station.

Predictor

Long-term ambient pollutant ozone and particulate matter ≤10 μm (PM10), assessed from monthly concentrations of ozone and PM10 calculated from ambient monitoring data by the US Environmental Protection Agency Air Quality System and interpolated to zip code centroids according to patients' residence.

Outcomes

Outcomes of interest were death from CHD and natural-cause mortality.

Results

For the entire transplant cohort, average pollutant levels for ozone and PM10 were 25.5 ± 4.4 parts per billion (ppb) and 25.3 ± 6.4 μg/m3, respectively. Correlation between ozone and PM10 values was low, but statistically significant (P < 0.001). There were deaths from CHD (n = 267) and natural causes (n = 2,076) during the 7-year study period. For each 10-ppb increase in ozone, the risk of fatal CHD increased by 35% (RR, 1.35; 95% CI, 1.04-1.77) in the single-pollutant model and 34% (RR, 1.34; 95% CI, 1.03-1.76) in the 2-pollutant model. No independent association was found between CHD and PM10. No significant association was identified for PM10 or ozone level and natural-cause mortality (RR, 1.09; 95% CI, 0.99-1.21).

Limitations

Exposure assignment based on only residential location.

Conclusions

For kidney transplant recipients, ambient ozone levels potentially are associated with higher risk of fatal CHD. These findings may have implications for regulations governing air pollution and the development of individual CHD risk-reduction strategies.

Section snippets

Study Population

Study participants were identified through the US Renal Data System (USRDS), a national data repository containing extensive demographic (including updated residential information), diagnostic, hospital information, and mortality data for persons living with end-stage renal disease (ESRD). Our study population included first-time kidney transplant recipients 18 years and older who underwent transplant in 1997-2003, with at least 1 year of transplant survival, residing within 50 km of an air

Study Population

The transplant population for this study consisted of individuals from across the entire continental United States (Fig 1). A total of 267 CHD deaths and 2,076 natural-cause deaths occurred in the 32,239 individuals studied (230.2 CHD deaths/100,000 person-years) during the 7-year study period. A combined total of 115,983.5 person-years was contributed by cohort participants during the follow-up period. Deaths from CHD accounted for 12.9% of the total 2,076 natural-cause deaths. For those with

Discussion

To our knowledge, no other study has assessed the impact of ambient air pollution on organ transplant recipients. Findings from this cohort study provide support for the hypothesis that air pollution exacerbates the atherosclerotic process and increases the risk of fatal CHD in kidney transplant recipients. Most studies of the effect of ambient air pollution on risk of CHD have found a clear and harmful effect of particulate matter, especially PM2.5 (particulate matter ≤2.5 μm), but usually

Acknowledgements

The authors thank Rebekah Spencer, DMD (Oregon Health and Science University), for valuable comments with drafting of the manuscript.

The data reported here have been supplied by the USRDS. The interpretation and reporting of these data are the responsibility of the authors and in no way should be seen as an official policy or interpretation of the US government.

Support: This study was in part funded by Environmental Protection Agency grant CR–83054701–0.

Financial Disclosure: The authors declare

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