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What Forces Dictate the Design of Pollution Monitoring Networks?

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Abstract

The US Environmental Protection Agency maintains networks of pollution monitors for two basic purposes: to check and enforce the attainment of national ambient air quality standards (NAAQS) and to provide useful data for studying pollution and its effects. These purposes imply conflicting criteria for the locations of a limited number of monitors. To check the attainment of standards, monitors are placed where pollution levels are highest. Monitors are not required where standards have always been met and there are no new pollution sources. To provide useful data for studying pollution and its effects, monitors would be placed to observe outcomes under a variety of pollution levels. This study asks the following questions. What factors affect when a monitor is retired from the network? What drives the decision to add a new site? What causes year-to-year changes in the number of monitors? We tackle these questions with a particular focus on the role of regulatory compliance and pollution levels in the context of monitors for tropospheric ozone (O3). Using a panel dataset of monitors in the contiguous US spanning the years 1993 to 2011, we find that the peak O3 readings in the prior period are significantly associated with the regulator’s decision of whether to add or to drop a monitor in the following period. While compliance with the NAAQS for O3 is not consistently associated with network composition, compliance with the PM2.5 NAAQS does appear to affect changes to the network.

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Notes

  1. See http://www.epa.gov/ttn/airs/airsaqs/detaildata/downloadaqsdata.htm.

  2. See http://www.epa.gov/ttnnaaqs/standards/o3/s_o3_history.html.

  3. In its recent Integrated Science Assessment for Ozone and Related Photochemical Oxidants [22], the USEPA investigated the correlation among monitors in the networks of 20 cities (CITE). This investigation, however, sought high correlations in support of health studies based upon aggregate pollution measures.

  4. This process, and guideline for it, is described by the USEPA at http://www.epa.gov/ttn/scram/guidance/guide/final-03-pm-rh-guidance.pdf

  5. Baldauf et al. [4] note that the primary objective of the NAAQS is the protection of human health. Hence, a methodology focusing on, effectively, a ranking of sites by health risks is still motivated by regulatory concerns, rather than purely measurement.

  6. See http://www.epa.gov/ttn/airs/airsaqs/manuals/codedescs.htm.

  7. We computed goodness-of-fit tests for these parametric models using the approach described in Andrews [2]. Despite fitting the data reasonably well, these tests reject the parametric models because the sample sizes are quite large. Given the qualitative agreement among our parametric models, we remain confident that the parameter estimates give an accurate representation of the patterns in the data.

  8. This is how attainment status is coded by the USEPA (see: http://www.epa.gov/oaqps001/greenbk/data_download.html)

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Muller, N.Z., Ruud, P.A. What Forces Dictate the Design of Pollution Monitoring Networks?. Environ Model Assess 23, 1–14 (2018). https://doi.org/10.1007/s10666-017-9553-7

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