Feature Article: Dual Approach Alleviates the Effects of Acid Rain
「Feature Article: Dual Approach Alleviates the Effects of Acid Rain」於資料集「MajorEnvironmentalPolicies」由單位「行政院環境保護署」的陳小姐所提供，聯繫電話是(02)23117722#2753,(02)23117722#2756，最近更新時間為：2023-07-30 01:03:45。 欄位編號的內容是607 ， 欄位標題的內容是Feature Article: Dual Approach Alleviates the Effects of Acid Rain ， 欄位摘要的內容是Collection of the air pollution control fee began in 1995. In conjunction with low sulfur fuel policies aimed at controlling pollution at the source this dual approach has reduced industrial sulfur oxide emissions and gradually lowered airborne concentrations of sulfur dioxide in the Taiwan region. From the 1994 average of 8.1 ppb, sulfur oxide concentration dropped to 4.7 ppb in 1999, a 42% improvement. Average SO2 concentrations in the first half of 2000 further dropped to 4.3 ppb, lower by 22% than the average value for the past three years at the same time.
At an August 8 press conference on implementation of the air pollution control fee, EPA Deputy Administrator, Lin Ta-hsiung, took time to explain recent achievements in controlling sulfur oxides (SOX). Lin pointed out that in 1998 the average sulfur dioxide (SO2) concentration in the Taiwan region was 5 ppb. Taipei City recorded an average concentration of only 4 ppb, significantly lower than many other well known capital cities. For example, London averages 11 ppb, Berlin 9 ppb, Paris 10 ppb, Brussels 8 ppb, New York 9 ppb, Tokyo 9 ppb and Hong Kong 11 ppb.
Director General of the Bureau of Air Quality Protection and Noise Control, Chen Hsiung-wen, further pointed out that reductions in airborne SOX concentrations have brought improvement to the acid rain situation. Acid rain is defined as rain with a pH value below 5.0. Average pH values at the Taipei monitoring station improved from 4.27 in 1991 to 4.54 in 1999. This equal a 50% improvement rate. Kaohsiung station recorded a change in average pH values from 4.49 to 4.73 over the same period of time, a 42% improvement rate. Although metropolitan areas still exhibit some rain acidification, steady progress is being made. Monitoring stations in suburban areas show that places such as Kenting, Taimali, Chiayi, Penghu, and Alishan do not have an acid rain problem.
Airborne sulfur oxides have adverse effects on the human respiratory system, in addition to giving rise to both acid rain and suspended particulates. The major sources of SOX come from combustion of coal, industrial fuel oils and vehicular diesel fuels. Fuel combustion generates SOX and nitrogen oxides (NOX). Chemical reactions in the atmosphere then give rise to sulfuric and nitric acids, which dissolve in water and precipitate as acid rain. Director General Chen noted that the proportion of sulfates found in rain water decreased 27% from 1991 to 1998, a noticeable improvement.
Besides obvious improvements in air quality, the effects of the air pollution control fee are apparent in pollution source emissions as well. The Air Bureau noted that before collection of the air pollution control fee, most factories treated SOX emissions to just within required limits, and did not operate control equipment to attain the greatest removal efficiency. After the air pollution control fee was initiated, factories obtain greater fee exemptions the larger the degree of SOX reduction. The fee also caused enterprises to begin purchasing low sulfur fuels or switching over to natural gases, and accelerated the installation of SOX control equipment. Economic incentive further ensures that prevention equipment is faithfully operated. Since fee collection began, pollution control measures have accounted for SOX reductions of around 126,000 tons annually, and total investment of over NT$100 billion. (see chart). Currently the Taiwan area has 42 sets of exhaust desulfurization equipment, an increase of 12 since collection of the air pollution fee began. Furthermore, their operating efficiency has increased from around 60% to over 90%.
In terms of fuel selection, the push and pull of both incentives and controls have caused industries to begin the switch over to cleaner fuels. Currently, industrial fuel oils with sulfur content below 0.5% make up 2/3 of national consumption. Further, after 1998, it was nationally mandated that sulfur content in diesel fuel must be below 0.05%, comparable with advanced countries. In terms of imported coal, in 1994 average sulfur content for imported fuel coal was 0.73%, but after collection of the air pollution control fee began in 1995 average sulfur content was reduced to 0.55% and subsequently 0.46% by 1998.
The Air Bureau noted that future SOX control strategy will focus mainly on fuel controls, tightening emissions standards for power generation, and total emissions quantity control. For example, gradually implemented fuel controls will eventually lead to comprehensive use of 0.5% sulfur content industrial fuels for Taiwan's west coast. In the Chu-Miao (竹苗) and Yun-Chia-Nan (雲嘉南) air quality control zones, mandatory use of fuels with 0.5% sulfur content will be phased in, and new pollution sources will be encouraged to use low pollution fuels (such as natural gas or liquefied petroleum gas). In addition, SOX emissions from coal-fired power plants will be tightened from 500 ppm to 200 ppm in July 2001.
Measure
Method
Estimated SOX Reductions (1,000 tons/year)
Investment (NT$100 million)
Increase installation of SOX control facilities
Installation of Exhaust Desulfurization Facilities
81
162
Use cleaner fuels
Increase use of natural gas
42
962.5
Other reduction measures
Process improvement reductions or increased removal efficiency
3
0.2
Total
126
1124.7 ， 欄位全文的內容是Collection of the air pollution control fee began in 1995. In conjunction with low sulfur fuel policies aimed at controlling pollution at the source this dual approach has reduced industrial sulfur oxide emissions and gradually lowered airborne concentrations of sulfur dioxide in the Taiwan region. From the 1994 average of 8.1 ppb, sulfur oxide concentration dropped to 4.7 ppb in 1999, a 42% improvement. Average SO2 concentrations in the first half of 2000 further dropped to 4.3 ppb, lower by 22% than the average value for the past three years at the same time.
At an August 8 press conference on implementation of the air pollution control fee, EPA Deputy Administrator, Lin Ta-hsiung, took time to explain recent achievements in controlling sulfur oxides (SOX). Lin pointed out that in 1998 the average sulfur dioxide (SO2) concentration in the Taiwan region was 5 ppb. Taipei City recorded an average concentration of only 4 ppb, significantly lower than many other well known capital cities. For example, London averages 11 ppb, Berlin 9 ppb, Paris 10 ppb, Brussels 8 ppb, New York 9 ppb, Tokyo 9 ppb and Hong Kong 11 ppb.
Director General of the Bureau of Air Quality Protection and Noise Control, Chen Hsiung-wen, further pointed out that reductions in airborne SOX concentrations have brought improvement to the acid rain situation. Acid rain is defined as rain with a pH value below 5.0. Average pH values at the Taipei monitoring station improved from 4.27 in 1991 to 4.54 in 1999. This equal a 50% improvement rate. Kaohsiung station recorded a change in average pH values from 4.49 to 4.73 over the same period of time, a 42% improvement rate. Although metropolitan areas still exhibit some rain acidification, steady progress is being made. Monitoring stations in suburban areas show that places such as Kenting, Taimali, Chiayi, Penghu, and Alishan do not have an acid rain problem.
Airborne sulfur oxides have adverse effects on the human respiratory system, in addition to giving rise to both acid rain and suspended particulates. The major sources of SOX come from combustion of coal, industrial fuel oils and vehicular diesel fuels. Fuel combustion generates SOX and nitrogen oxides (NOX). Chemical reactions in the atmosphere then give rise to sulfuric and nitric acids, which dissolve in water and precipitate as acid rain. Director General Chen noted that the proportion of sulfates found in rain water decreased 27% from 1991 to 1998, a noticeable improvement.
Besides obvious improvements in air quality, the effects of the air pollution control fee are apparent in pollution source emissions as well. The Air Bureau noted that before collection of the air pollution control fee, most factories treated SOX emissions to just within required limits, and did not operate control equipment to attain the greatest removal efficiency. After the air pollution control fee was initiated, factories obtain greater fee exemptions the larger the degree of SOX reduction. The fee also caused enterprises to begin purchasing low sulfur fuels or switching over to natural gases, and accelerated the installation of SOX control equipment. Economic incentive further ensures that prevention equipment is faithfully operated. Since fee collection began, pollution control measures have accounted for SOX reductions of around 126,000 tons annually, and total investment of over NT$100 billion. (see chart). Currently the Taiwan area has 42 sets of exhaust desulfurization equipment, an increase of 12 since collection of the air pollution fee began. Furthermore, their operating efficiency has increased from around 60% to over 90%.
In terms of fuel selection, the push and pull of both incentives and controls have caused industries to begin the switch over to cleaner fuels. Currently, industrial fuel oils with sulfur content below 0.5% make up 2/3 of national consumption. Further, after 1998, it was nationally mandated that sulfur content in diesel fuel must be below 0.05%, comparable with advanced countries. In terms of imported coal, in 1994 average sulfur content for imported fuel coal was 0.73%, but after collection of the air pollution control fee began in 1995 average sulfur content was reduced to 0.55% and subsequently 0.46% by 1998.
The Air Bureau noted that future SOX control strategy will focus mainly on fuel controls, tightening emissions standards for power generation, and total emissions quantity control. For example, gradually implemented fuel controls will eventually lead to comprehensive use of 0.5% sulfur content industrial fuels for Taiwan's west coast. In the Chu-Miao (竹苗) and Yun-Chia-Nan (雲嘉南) air quality control zones, mandatory use of fuels with 0.5% sulfur content will be phased in, and new pollution sources will be encouraged to use low pollution fuels (such as natural gas or liquefied petroleum gas). In addition, SOX emissions from coal-fired power plants will be tightened from 500 ppm to 200 ppm in July 2001.
Measure
Method
Estimated SOX Reductions (1,000 tons/year)
Investment (NT$100 million)
Increase installation of SOX control facilities
Installation of Exhaust Desulfurization Facilities
81
162
Use cleaner fuels
Increase use of natural gas
42
962.5
Other reduction measures
Process improvement reductions or increased removal efficiency
3
0.2
Total
126
1124.7 ， 欄位年度的內容是2000 ， 欄位月份的內容是3 ， 欄位卷的內容是3 ， 欄位期的內容是15 ， 欄位順序的內容是1 ， 欄位倒序的內容是2 ， 欄位分類的內容是air ， 欄位標題2的內容是Dual Approach Alleviates the Effects of Acid Rain ， 欄位檔案位置的內容是V1/V3-15 。
編號
607
標題
Feature Article: Dual Approach Alleviates the Effects of Acid Rain
摘要
Collection of the air pollution control fee began in 1995. In conjunction with low sulfur fuel policies aimed at controlling pollution at the source this dual approach has reduced industrial sulfur oxide emissions and gradually lowered airborne concentrations of sulfur dioxide in the Taiwan region. From the 1994 average of 8.1 ppb, sulfur oxide concentration dropped to 4.7 ppb in 1999, a 42% improvement. Average SO2 concentrations in the first half of 2000 further dropped to 4.3 ppb, lower by 22% than the average value for the past three years at the same time. At an August 8 press conference on implementation of the air pollution control fee, EPA Deputy Administrator, Lin Ta-hsiung, took time to explain recent achievements in controlling sulfur oxides (SOX). Lin pointed out that in 1998 the average sulfur dioxide (SO2) concentration in the Taiwan region was 5 ppb. Taipei City recorded an average concentration of only 4 ppb, significantly lower than many other well known capital cities. For example, London averages 11 ppb, Berlin 9 ppb, Paris 10 ppb, Brussels 8 ppb, New York 9 ppb, Tokyo 9 ppb and Hong Kong 11 ppb. Director General of the Bureau of Air Quality Protection and Noise Control, Chen Hsiung-wen, further pointed out that reductions in airborne SOX concentrations have brought improvement to the acid rain situation. Acid rain is defined as rain with a pH value below 5.0. Average pH values at the Taipei monitoring station improved from 4.27 in 1991 to 4.54 in 1999. This equal a 50% improvement rate. Kaohsiung station recorded a change in average pH values from 4.49 to 4.73 over the same period of time, a 42% improvement rate. Although metropolitan areas still exhibit some rain acidification, steady progress is being made. Monitoring stations in suburban areas show that places such as Kenting, Taimali, Chiayi, Penghu, and Alishan do not have an acid rain problem. Airborne sulfur oxides have adverse effects on the human respiratory system, in addition to giving rise to both acid rain and suspended particulates. The major sources of SOX come from combustion of coal, industrial fuel oils and vehicular diesel fuels. Fuel combustion generates SOX and nitrogen oxides (NOX). Chemical reactions in the atmosphere then give rise to sulfuric and nitric acids, which dissolve in water and precipitate as acid rain. Director General Chen noted that the proportion of sulfates found in rain water decreased 27% from 1991 to 1998, a noticeable improvement. Besides obvious improvements in air quality, the effects of the air pollution control fee are apparent in pollution source emissions as well. The Air Bureau noted that before collection of the air pollution control fee, most factories treated SOX emissions to just within required limits, and did not operate control equipment to attain the greatest removal efficiency. After the air pollution control fee was initiated, factories obtain greater fee exemptions the larger the degree of SOX reduction. The fee also caused enterprises to begin purchasing low sulfur fuels or switching over to natural gases, and accelerated the installation of SOX control equipment. Economic incentive further ensures that prevention equipment is faithfully operated. Since fee collection began, pollution control measures have accounted for SOX reductions of around 126,000 tons annually, and total investment of over NT$100 billion. (see chart). Currently the Taiwan area has 42 sets of exhaust desulfurization equipment, an increase of 12 since collection of the air pollution fee began. Furthermore, their operating efficiency has increased from around 60% to over 90%. In terms of fuel selection, the push and pull of both incentives and controls have caused industries to begin the switch over to cleaner fuels. Currently, industrial fuel oils with sulfur content below 0.5% make up 2/3 of national consumption. Further, after 1998, it was nationally mandated that sulfur content in diesel fuel must be below 0.05%, comparable with advanced countries. In terms of imported coal, in 1994 average sulfur content for imported fuel coal was 0.73%, but after collection of the air pollution control fee began in 1995 average sulfur content was reduced to 0.55% and subsequently 0.46% by 1998. The Air Bureau noted that future SOX control strategy will focus mainly on fuel controls, tightening emissions standards for power generation, and total emissions quantity control. For example, gradually implemented fuel controls will eventually lead to comprehensive use of 0.5% sulfur content industrial fuels for Taiwan's west coast. In the Chu-Miao (竹苗) and Yun-Chia-Nan (雲嘉南) air quality control zones, mandatory use of fuels with 0.5% sulfur content will be phased in, and new pollution sources will be encouraged to use low pollution fuels (such as natural gas or liquefied petroleum gas). In addition, SOX emissions from coal-fired power plants will be tightened from 500 ppm to 200 ppm in July 2001. Measure Method Estimated SOX Reductions (1,000 tons/year) Investment (NT$100 million) Increase installation of SOX control facilities Installation of Exhaust Desulfurization Facilities 81 162 Use cleaner fuels Increase use of natural gas 42 962.5 Other reduction measures Process improvement reductions or increased removal efficiency 3 0.2 Total 126 1124.7
全文
Collection of the air pollution control fee began in 1995. In conjunction with low sulfur fuel policies aimed at controlling pollution at the source this dual approach has reduced industrial sulfur oxide emissions and gradually lowered airborne concentrations of sulfur dioxide in the Taiwan region. From the 1994 average of 8.1 ppb, sulfur oxide concentration dropped to 4.7 ppb in 1999, a 42% improvement. Average SO2 concentrations in the first half of 2000 further dropped to 4.3 ppb, lower by 22% than the average value for the past three years at the same time. At an August 8 press conference on implementation of the air pollution control fee, EPA Deputy Administrator, Lin Ta-hsiung, took time to explain recent achievements in controlling sulfur oxides (SOX). Lin pointed out that in 1998 the average sulfur dioxide (SO2) concentration in the Taiwan region was 5 ppb. Taipei City recorded an average concentration of only 4 ppb, significantly lower than many other well known capital cities. For example, London averages 11 ppb, Berlin 9 ppb, Paris 10 ppb, Brussels 8 ppb, New York 9 ppb, Tokyo 9 ppb and Hong Kong 11 ppb. Director General of the Bureau of Air Quality Protection and Noise Control, Chen Hsiung-wen, further pointed out that reductions in airborne SOX concentrations have brought improvement to the acid rain situation. Acid rain is defined as rain with a pH value below 5.0. Average pH values at the Taipei monitoring station improved from 4.27 in 1991 to 4.54 in 1999. This equal a 50% improvement rate. Kaohsiung station recorded a change in average pH values from 4.49 to 4.73 over the same period of time, a 42% improvement rate. Although metropolitan areas still exhibit some rain acidification, steady progress is being made. Monitoring stations in suburban areas show that places such as Kenting, Taimali, Chiayi, Penghu, and Alishan do not have an acid rain problem. Airborne sulfur oxides have adverse effects on the human respiratory system, in addition to giving rise to both acid rain and suspended particulates. The major sources of SOX come from combustion of coal, industrial fuel oils and vehicular diesel fuels. Fuel combustion generates SOX and nitrogen oxides (NOX). Chemical reactions in the atmosphere then give rise to sulfuric and nitric acids, which dissolve in water and precipitate as acid rain. Director General Chen noted that the proportion of sulfates found in rain water decreased 27% from 1991 to 1998, a noticeable improvement. Besides obvious improvements in air quality, the effects of the air pollution control fee are apparent in pollution source emissions as well. The Air Bureau noted that before collection of the air pollution control fee, most factories treated SOX emissions to just within required limits, and did not operate control equipment to attain the greatest removal efficiency. After the air pollution control fee was initiated, factories obtain greater fee exemptions the larger the degree of SOX reduction. The fee also caused enterprises to begin purchasing low sulfur fuels or switching over to natural gases, and accelerated the installation of SOX control equipment. Economic incentive further ensures that prevention equipment is faithfully operated. Since fee collection began, pollution control measures have accounted for SOX reductions of around 126,000 tons annually, and total investment of over NT$100 billion. (see chart). Currently the Taiwan area has 42 sets of exhaust desulfurization equipment, an increase of 12 since collection of the air pollution fee began. Furthermore, their operating efficiency has increased from around 60% to over 90%. In terms of fuel selection, the push and pull of both incentives and controls have caused industries to begin the switch over to cleaner fuels. Currently, industrial fuel oils with sulfur content below 0.5% make up 2/3 of national consumption. Further, after 1998, it was nationally mandated that sulfur content in diesel fuel must be below 0.05%, comparable with advanced countries. In terms of imported coal, in 1994 average sulfur content for imported fuel coal was 0.73%, but after collection of the air pollution control fee began in 1995 average sulfur content was reduced to 0.55% and subsequently 0.46% by 1998. The Air Bureau noted that future SOX control strategy will focus mainly on fuel controls, tightening emissions standards for power generation, and total emissions quantity control. For example, gradually implemented fuel controls will eventually lead to comprehensive use of 0.5% sulfur content industrial fuels for Taiwan's west coast. In the Chu-Miao (竹苗) and Yun-Chia-Nan (雲嘉南) air quality control zones, mandatory use of fuels with 0.5% sulfur content will be phased in, and new pollution sources will be encouraged to use low pollution fuels (such as natural gas or liquefied petroleum gas). In addition, SOX emissions from coal-fired power plants will be tightened from 500 ppm to 200 ppm in July 2001. Measure Method Estimated SOX Reductions (1,000 tons/year) Investment (NT$100 million) Increase installation of SOX control facilities Installation of Exhaust Desulfurization Facilities 81 162 Use cleaner fuels Increase use of natural gas 42 962.5 Other reduction measures Process improvement reductions or increased removal efficiency 3 0.2 Total 126 1124.7
年度
2000
月份
3
卷
3
期
15
順序
1
倒序
2
分類
air
標題2
Dual Approach Alleviates the Effects of Acid Rain
檔案位置
V1/V3-15
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不定期更新更新,118黃先生 | 02-23117722#2881 | 2023-07-27 01:02:59
行政院環境保護署建檔公廁明細-苗栗縣
不定期更新更新,118賴先生 | 04-2252-1718#53686 | 2023-07-27 01:02:05
行政院環境保護署綠色消費暨環境保護產品審議會設置要點
每季更新更新,35陳先生 | 02-23117722#2936 | 2022-01-15 01:13:12
行政院環境保護署光化測站基本資料
不定期更新更新,51謝小姐 | 02-2311-7722#2386 | 2022-01-14 01:05:01
行政院環境保護署焚化廠營運年報
每1年更新,113莊先生 | 04-22521718#53523 | 2023-08-07 01:02:34
行政院環境保護署
列管毒性化學物質已取得許可業者查核家次
每年更新更新,131謝小姐 | 02-23117722#2103 | 2022-01-14 01:22:54
行政院環境保護署溫室氣體年排放量
每1年更新,153甘先生 | (02)2311-7722#2771 | 2023-08-02 01:02:55
行政院環境保護署環訓所年度年報彙編
每年更新更新,51湯小姐 | 03-4020789#544 | 2022-01-15 01:10:11
行政院環境保護署巡守隊明細資料
不定期更新更新,210謝小姐 | 02-2311-7722#2836 | 2022-01-15 01:12:07
行政院環境保護署重點事業廢棄物-生物醫療廢棄物之處理方式
每月更新更新,155陳先生 | 02-2311-7722#2682 | 2022-01-14 01:24:07
行政院環境保護署
地下水場置性監測井位置圖
每1月更新,47呂小姐 | 02-2383-2389#8110 | 2023-08-09 01:04:52
行政院環境保護署經過地質敏感區之環境影響說明書件
每2月更新,162黃先生 | 02-23117722#2748 | 2023-08-06 01:04:09
行政院環境保護署新化學物質登錄資訊系統工具(Chemist)
不定期更新更新,43蔡小姐 | 23257399#55723 | 2022-01-14 01:23:00
行政院環境保護署空氣品質小時值_新北市_板橋站
每1時更新,124陳先生 | 02-2311-7722#2386 | 2023-08-02 00:58:18
行政院環境保護署空氣污染罰鍰次數
每年更新更新,152謝小姐 | 02-23117722#2103 | 2022-01-14 01:22:39
行政院環境保護署
縣市(新竹市)小時值-每小時
每小時更新更新,173謝小姐 | 02-2311-7722#2386 | 2022-01-14 01:00:48
行政院環境保護署其他環境影響評估書件專案小組審查會議紀錄
每2月更新,53黃先生 | 02-23117722#2748 | 2023-08-06 01:02:13
行政院環境保護署臺中市水量水質自動監測連線傳輸監測紀錄值即時資料集
不定期更新更新,51程先生 | 02-2311-7722#2833 | 2023-08-09 01:04:11
行政院環境保護署廢食用油流向清運資料統計(屬事業廢棄物部分)
每1月更新,146林先生 | 02-2311-7722#2671 | 2023-08-07 01:02:01
行政院環境保護署建檔公廁明細-嘉義市
不定期更新更新,225賴先生 | 04-2252-1718#53686 | 2023-07-27 01:01:59
行政院環境保護署
MajorEnvironmentalPolicies
每3月更新,178陳小姐 | (02)23117722#2753,(02)23117722#2756 | 2023-07-30 01:03:45
行政院環境保護署空氣品質小時值_桃園市_大園站
每1時更新,113陳先生 | 02-2311-7722#2386 | 2023-08-02 00:58:08
行政院環境保護署地方環保局環保稽查次數
每月更新更新,120謝小姐 | 02-23117722#2103 | 2022-01-14 01:21:24
行政院環境保護署毒性化學物質許可及申報資料
每3月更新,282許先生 | 02-23117722#2865 | 2023-07-30 01:03:49
行政院環境保護署環評主管機關受理審查之環境影響差異分析報告
每2月更新,168黃先生 | 02-23117722#2748 | 2023-08-05 01:01:20
行政院環境保護署