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Need for Coordination between Greenhouse Gas and Pollution Abatement Regulations: China’s Case and Its Implications for Korea

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Book cover Quantitative Regional Economic and Environmental Analysis for Sustainability in Korea

Part of the book series: New Frontiers in Regional Science: Asian Perspectives ((NFRSASIPER,volume 25))

Abstract

In this chapter, I briefly introduce my previous research on the carbon co-benefits of pollution abatement in China and then discuss what key lessons Korea can learn from it. A main finding is that strong cross effects exist between air pollution and carbon mitigation in China. In particular, China could even overachieve its official CO2 intensity targets, in terms of carbon reductions, by simply meeting the existing SO2 and NOx reduction goals. Accordingly, the CO2 intensity targets are not binding and generate unnecessary compliance costs. This result conveys several policy implications for Korea. First, local pollution abatement, given its strong cross effects, may be considered as a carbon mitigation strategy. However, taking full advantage of the cross effects—meeting emission reduction targets at minimal costs—requires a close coordination between air pollution and carbon regulations. Finally, clear and consistent long-term reduction goals and associated policy incentives are necessary to promote economy-wide, forward-looking technology adoption and thus to avoid the potential lock-in effect in energy supply.

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Notes

  1. 1.

    At present, the TMS targets firms exceeding 50 ktCO2e, in terms of annual GHG emissions, or 200 TJ, in terms of annual energy consumption, and the installations exceeding 15 ktCO2e or 80 TJ (Government of Korea, 2014).

  2. 2.

    These 526 ETS participants either emitted an annual average of ≥125 ktCO2e of GHGs between 2011 and 2013 or operated an installation emitting ≥25 ktCO2e during the same period (Government of Korea, 2014).

  3. 3.

    The Capital Region includes the following three province-level municipalities: Seoul, Incheon, and Gyeonggi.

  4. 4.

    Energy efficiency is defined as value added per unit energy use, and the numbers given here are computed from the WDI database.

  5. 5.

    For further details on the method introduced in this section, refer to Nam et al. (2013) and (2014).

  6. 6.

    All monetary results displayed in this section are measured in constant 2004 US dollars, unless otherwise specified.

  7. 7.

    In EPPA, the EINT sector includes industries engaged in production of paper products, chemical products, ferrous and nonferrous metal products, metal products, and mineral products.

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Nam, KM. (2016). Need for Coordination between Greenhouse Gas and Pollution Abatement Regulations: China’s Case and Its Implications for Korea. In: Kim, E., Kim, B. (eds) Quantitative Regional Economic and Environmental Analysis for Sustainability in Korea. New Frontiers in Regional Science: Asian Perspectives, vol 25. Springer, Singapore. https://doi.org/10.1007/978-981-10-0300-4_11

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  • DOI: https://doi.org/10.1007/978-981-10-0300-4_11

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