環境資源報告成果查詢系統

提升中部及雲嘉南空品區空氣品質改善計畫

中文摘要 本計畫主要工作內容包括研析空品區空品變化趨勢及擬定空品改善目標、協助推動重大開發案或重點污染源熱點(Hot Spot)管制及減量工作、協助推動揮發性有機物空氣污染管制及排放標準法規,並追蹤六輕工業區空氣污染減量工作及改善成效、檢討修訂固定污染源相關管制排放標準,提昇PM2.5等空氣污染物減量成效。主要成果摘要如下: 一、空品區空品變化趨勢及擬定空品改善目標 環保署於101年6月14日修正「直轄市、縣(市)各級空氣污染防制區」,南投縣懸浮微粒劣化為三級防制區可能與莫拉克風災後之河川揚塵、疏濬工程及土石運輸有關。臭氧改善部分則可能與固定污染源、移動污染源改善或天氣型態改變有關。 101年中部及雲嘉南空品區(包含南投縣)空品不良率已有顯著改善,為近十年來最佳狀況。排放因子分析顯示,SOx及NOx於90~100年減幅達29.4、23.2%,VOCs初期仍以排放量掌握為主,成效仍待努力。移動污染源方面,98年相較於76年排放量,PM10排放量降低5%,SOx排放量降低95%,NOx排放量降低22%,NMHC排放量降低69%,CO排放量降低68%,Pb排放量降低98%,顯見所實施的管制措施已具成效。但98年車輛數較88年成長30%,排放減量工作仍須持續加強。氣象因子分析顯示,101年月降雨日數明顯較多,也有助於一次污染物之去除效果,並減少二次污染物之生成機率。 六輕對空氣品質影響分析顯示,台西站乙烯及丙烯濃度佔比相對其它光化測站為高,另台西站在六輕營運後SO2異常日數達每年80日,97年起改善,100年已減為12日。 台西測站乙烯、丙烯及苯濃度最大值發生在特定風向(北北西),該方向上風處為燃燒塔,而濃度依風向別,類似高斯煙流模式型態分布,推測燃燒塔常態排放,在北北西風向,台西測站受到顯著影響。 二、協助推動重大開發案或重點污染源熱點管制及減量工作 空品區減量行動計畫推動方式係邀集各縣市共同提出議題,由中央地方合作解決。 移動污染源議題含淨區管制,探討阿里山空品淨區之處分爭議對類似案之影響;針對業者即時通報,以替代道路規避稽查作業行為,以中部及雲嘉南空品區七縣市合作進行柴油車聯合稽查(台中港區)來突破。 逸散污染源議題含追蹤西濱快速公路(台61線)員林大排至西濱大橋營建工程道路揚塵改善情形;推動濁水溪管制之跨單位合作協商機制;探討減少稻草露天燃燒、稻草再利用平台、以焚化爐處理可行評估。 固定污染源含重大開發案(如台中港區投資案),參考六輕管制經驗,下階段擴大辦理;中小型污染源則探討塊煤鍋爐管制及燃料使用變化趨勢。 針對燃料使用變化趨勢,如燃油改燃塊煤、燃油改燃NG或LPG、燃塊煤改燃生質燃料等,提出改善建議,包含加嚴粒狀物標準、增訂塊煤含硫量檢測方法、研擬以單位輸出熱值之排放量標準、掌握因應燃油鍋爐改燃NG、LPG或生質燃料情形。 三、協助推動揮發性有機物空氣污染管制及排放標準法規,並追蹤六輕工業區空氣污染減量工作及改善成效 法規推動部分:已協助完成VOCs標準申報表單4項,協助環檢所修訂檢測方法完成4項,另有2項檢討中。 追蹤六輕減量部份:100年查核發現燃燒塔廢氣熱值不足問題,101年因業者添加燃料補充熱值已解決,排放總硫問題將於101年底廢氣導入高溫氧化設備後解決,設備元件洩漏問題,業者已導入線上修護技術解決,大於10,000ppm洩漏濃度從97年0.13%降為100年之0.04%,已具初步成效。VOCs標準生效後燃燒塔等VOCs、SOx及CO2分別減量達986、916及1,385,572噸/年。 協助六輕排放量確認部分:101/7/25環評審查會219次會議,決議將燃燒塔(含異常排放)、油漆塗佈、冷卻水塔、儲槽清洗及歲修作業之VOCs排放量,納入六輕計畫排放總量計算,其查核方式納入定稿。100/12/5行政院訴願委員會撤銷環評大會決議。因有先減量後投產及淨減量決議,影響有限。另為完備管制作業,已於101/1/4辦理VOCs公告係數修正草案公聽會。 協助VOCs標準執行困難部分:業界建議減少由地方環保主管機關審查項目。針對業界意見,本計畫亦收集國外管制規定及作法,提供縣市審查之參考。 四、檢討修訂固定污染源相關管制排放標準,提昇PM2.5等空氣污染物減量成效。 針對民國80年間發布標準提出修正草案,提出檢討修正計11項,預估實施後,粒狀污染物減量效益為3,823公噸/年,硫氧化物減量效益為12,733噸/年及氮氧化物減量效益為37,089公噸/年,其中以電力設施修正草案減量最高,國內燃煤汽電共生鍋爐需投資46.2億增設SCR以符合NOx排放限值。 考量排放量高及節能減碳等因素,建議其中5項優先實施。鋼鐵業燒結工場已於6/14修正發布,固定污染源及煉鋼業電爐已完成預告修正,電力設施及玻璃業標準亦與業界完成研商。
中文關鍵字 空氣品質;空污減量;六輕離島工業區;固定污染源;排放標準

基本資訊

專案計畫編號 EPA-101-FA12-03-A083 經費年度 101 計畫經費 9600 千元
專案開始日期 2012/04/05 專案結束日期 2012/12/31 專案主持人 郭子豪
主辦單位 空保處 承辦人 戴忠良 執行單位 中興工程顧問股份有限公司

成果下載

類型 檔名 檔案大小 說明
期末報告 EPA-101-FA12-03-A083.pdf 43MB

The Plan to Improve the Air Quality in the Central and South Taiwan

英文摘要 The scope of work for this project includes analyzing air quality trend and develop air quality improvement goals of air quality zone, promoting the control strategy and pollution reduction of major development projects or main pollutant source hotspot, promoting the air pollution control and emission standards of volatile organic compounds(VOCs), tracing the air pollution reduction and improvement effects of the No.6 Naphtha Cracking Plant, reviewing the amendments to the stationary source emission standards, improving the reduction effect of fine suspended particles(PM2.5). The critical results are abstracted as followed: 1.Analyzing air quality trend and develop air quality improvement goals of air quality area. EPA has announced the modified air quality control region for each class of special municipality, county and city on 2012/6/14, and the amendment will be in effect on 2013/1/1. In which, Nantou country PM2.5 deteriorated to Class 3 control region. It may relate to river bank fugitive dust, river channel dredging work, and transportation of earth and gravel caused by Typhoon Morakot. The improvement of ozone control region may relate to improvement of stationary source and mobile sources or climate change. The poor air quality rate of Central Taiwan and Yun-Chia-Nan Air Quality Zone (including Nantou County) had improved significantly in 2012, which is the best condition for the past decade. Emission factor analysis shows that in 2011 the SOx and NOx emissions reduction is 29.4% and 23.2% comparing to 2001. The main strategy of VOCs control in the early stage is to identify major emissions sources. The VOCs reduction will be done in the future. Between 1987 and 2009, mobile sources showed 5% reduction in PM10 emissions, 95% reduction in SOx emissions, 22% reduction in NOx emissions, 69% reduction in NMHC emissions, 68% reduction in CO emissions, and 98% reduction in Pb emissions. It shows that the implementation of control measures have been effective. However, the amount of vehicles has grown by 30% between 1999 and 2009; the emissions reduction of mobile sources has reached a bottleneck. The meteorological factor analysis shows that the monthly raining days in 2012 were significantly higher than past few years. It contributed to the removal of primary pollutants and reduced the generation rate of secondary pollutants. According to the analysis of the air quality impact from the No.6 Naphtha Cracking Plant, the concentration of ethylene and propylene at Taisi monitoring site is higher than other sites. The SOx abnormal days reached 80 days per year since the operation of the plant. However, it has started to improve in 2008, and decreased to 12 days per year in 2011. Maximum concentrations of ethylene, propylene and benzene detected at the Taisi monitoring site occurred in a specific wind direction(north-northwest). It may be caused by the constant emissions from flares in the north-northwest wind direction. 2. Promoting the control strategy and pollution reduction of major development projects or main pollutant source hotspot. The emission reduction strategies in air quality zones were proposed by local governments and coordinated by the central government. Issues of controlling mobile sources in designated “Clean Air Zones” include dispute of sanctions in Alishan, and joint investigation of diesel cars in 7 counties and cities to prevent cars from escaping inspections by taking detours. Fugitive source air pollution issues include tracking the improvement of fugitive dust from construction of West Coast Expressway(Route 61), promoting the cooperation and consultation mechanisms of ChoShui River fugitive dust control, and feasibility of reducing the straw open burning, straw reuse platform and incineration. Stationary sources issues including major development projects (ex. Taichung Harbor) will be implement in the next phase according to the air pollution control experience of the No.6 Naphtha Cracking Plant. Small and medium-sized pollution sources issues include lump coal boiler control and the study of change of fuel consumption. For the change of pollution source fuel consumption trends, such as oil changed to lump coal, oil changed to NG or LPG, lump coal changed to biomass etc., we proposed the improvements including strengthen the particle emission standards, proposed the sulfur content detection method of lump coal, proposed the specific heating value emission standard, and analyzed the feasibility of the oil fuel boiler changed to NG, LPG or biomass fuel. 3. Promoting the air pollution control and emission standards of volatile organic compounds (VOCs) and tracing the effect of air pollution reduction of the No.6 Naphtha Cracking Plant. For the promoting of VOCs air pollution control and emission standards, we helped developing four VOCs standards reporting forms and assisted Environmental Analysis Laboratory in the completion of four test methods. There are still two test methods amendments in progress. For the tracking of No.6 Naphtha Cracking Plant air pollution reduction results, the audit found out that the heating value of exhaust gas was too low in 2011. It had been solved by adding fuel gas. The total sulfur emissions of the Naphtha Cracking Plant will be reduced after the completion of high-temperature oxidation equipment in 2011. The leakage problem of equipment components had been solved by using the online repair technique. The chance of leak concentration greater than 10,000ppm was decreased from 0.13% in 1997 to 0.04% in 2011. It has gotten preliminary results. After the VOCs standards take effect, the VOCs, SOx and CO2 emissions reduction from flare and other equipments were 986, 916 and 1,385,572 tons per year, respectively. For confirming air pollutant emissions from the No.6 Naphtha Cracking Plant, in the 219th EIA meeting(2012/7/25), EIA adopted that emission estimating item should include flare(including abnormal emission), painting ,cooling tower, tank washing and yearly repair. The confirming method was into the final draft. Our project helped EPA and Yunlin County EPD jointly to resolve the No.6 Naphtha Cracking Plant air pollution emission dispute. For the implement difficulties of VOCs standards, the industry suggested to cut down the investigating item of local competent authorities. According to the suggestion, our project also collected the international control regulations and methods providing references to local competent authorities. 4. Review of the amendments to the stationary source emission standards, and improve the reduction effect of fine suspended particles(PM2.5) Our project proposed eleven revision drafts for the emission standards announced in 80s. If these standards were coming into effect, the estimating pollution reductions of particle would be 3,823 tons per year, sulfur oxides reduction would be 12,733 tons per year, and nitrogen oxides reduction would be 37,089 tons per year. Among them, the revision draft for power generation facilities has the highest emission reduction. The coal-fired cogeneration boilers in our country need to invest 4.62 billion NT dollars in adding SCR to comply with NOx emission limits. Considering emissions, energy conservation and carbon reduction and etc., it is recommended that five drafts should be implemented first. Steel Industry Sintering Plant Dioxin Control and Emission Standards had been announced on 2012/6/14. Notification for amendment of Stationary Pollution Source and steelmaking industry electric arc furnace emission standards were also announced. Power generation facilities and glass industry emission standards had been discussed with the industry sufficiently.
英文關鍵字 air quality;air pollution reduction;the No.6 Naphtha Cracker off-shore island industrial zone;Stationary Source;Emission Standard