China Policy Journal Volume 1, Number 1, Fall 2018 | Page 12

Water-Pollutant Discharge-Fee System in China ucts are listed in the 2011 Industrial Structure Adjustment Guide. If the pollutant’s discharge behavior falls under one of these situations, the penalty fee is charged once; while if it falls under two situations, the penalty is doubled; or meets all situations, the penalty go up to thrice. Moreover, to strengthen water-pollution control, the penalty fare is defined in terms 73 and 74 of the water pollution prevention law (2008): the irregular use of wastewater-treatment facilities and the demolition and idling of pollutant-treatment equipment should be charged by the upper level of the executive authority with a penalty fare of one to three times the water-pollutant discharge fee, while the national or regional standard-exceeding discharge over the total quantity-control indicators are charged with a fare of two to five times the discharge fee. The flexible fee structure not only affects the industrial structure, but also guides the spacial distribution of enterprises avoiding environmental sensitive areas and gives preference to water-resource abundant and low development-difficulty areas, which has further practical implications from the perspective of development and management. 1.2.3. Pollutant Factors With industrial development, the water-pollutant discharge-fee system was broadened by expanding the range of pollutant factors. The Temporary Regulation of Pollutant Discharge Fee set the standard for wastewater, waste gasses and solids, among which 20 types of water pollutants are clearly defined. In 1991, the list was extended to 29 types due to an increase in known facts about pollution. With further promotion of the water-pollutant discharge-fee system till 1993, the water-pollution fee was deepened from the content and the range. In 2003, the pollutant types were redefined and extended to 65, covering most of the water contaminants, of which 36 types were newly added, including heavy metals, radioactive materials, biochemical pollutants, etc. The fee standard changed from being single-factor dominant to being multi-factor based. 1.2.4. The Fee Collection Range Environmental deterioration had been exacerbated since the 10 th five-year plan, for prioritized achieving economic growth. Increasing transferrable or illegal point-source and nonpoint-source pollution resulted in compromised sanitation condition. In 1982, the fee system was limited to private and collective firms and units. However, supplydriven and conventional exploitation stretched the gap between water demand and the supply. It deviated from the original objective to control all wastewater discharged into water bodies, to cover and regulate any newly added pollution source within the system. Thus, the pollution fee was redefined in the Pollutant Discharge Fee Collection and Management Regulation of 2003, which was extended to include to all polluters, including plants, units, individuals from the industrial field, and commercial householders. 9