Air quality impacts of projections of natural gas-fired distributed generation. (November 2017)

• Record Type: Journal Article
• Authors: Horne, Jeremy R.; Carreras-Sospedra, Marc; Dabdub, Donald; Lemar, Paul; Nopmongcol, Uarporn; Shah, Tejas; Yarwood, Greg; Young, David; Shaw, Stephanie L.; Knipping, Eladio M.
• Is Part Of: Atmospheric environment. Volume 168(2017)
• Page Start: 8
• Page End: 22
• Publication Date: 2017-11
• Subjects: Distributed generation -- Air quality modeling -- Ozone -- Particulate matter; Air -- Pollution -- Periodicals; Air -- Pollution -- Meteorological aspects -- Periodicals; 551.51
• DOI: 10.1016/j.atmosenv.2017.08.046
• Languages: English
• ISSNs: 1352-2310

Abstract

Abstract: This study assesses the potential impacts on emissions and air quality from the increased adoption of natural gas-fired distributed generation of electricity (DG), including displacement of power from central power generation, in the contiguous United States. The study includes four major tasks: (1) modeling of distributed generation market penetration; (2) modeling of central power generation systems; (3) modeling of spatially and temporally resolved emissions; and (4) photochemical grid modeling to evaluate the potential air quality impacts of increased DG penetration, which includes both power-only DG and combined heat and power (CHP) units, for 2030. Low and high DG penetration scenarios estimate the largest penetration of future DG units in three regions – New England, New York, and California. Projections of DG penetration in the contiguous United States estimate 6.3 GW and 24 GW of market adoption in 2030 for the low DG penetration and high DG penetration scenarios, respectively. High DG penetration (all of which is natural gas-fired) serves to offset 8 GW of new natural gas combined cycle (NGCC) units, and 19 GW of solar photovoltaic (PV) installations by 2030. In all scenarios, air quality in the central United States and the northwest remains unaffected as there is little to no DG penetration in those states. California and several states in the northeast are the most impacted by emissions from DG units. Peak increases in maximum daily 8-h average ozone concentrations exceed 5 ppb, which may impede attainment of ambient air quality standards. Overall, air quality impacts from DG vary greatly based on meteorological conditions, proximity to emissions sources, the number and type of DG installations, and the emissions factors used for DG units. Highlights: 6–24 GW of natural gas-fired DG penetration is estimated for 2030. Ozone levels may increase up to 6 ppb due to increased NG-fired DG penetration. Largest air quality impacts from NG-fired DG occur in New England and California. The greatest projected DG penetration occurs New England, New York, and California. Stricter emission limits for NG-fired DG greatly reduce air quality impacts of DG.