環境資源報告成果查詢系統

99年至101年底泥品質管理計畫

中文摘要 近年來國內陸續發現不少水體底泥受到污染,其清除與否,牽涉龐大之清除處理費用與不甚確定之生態環境與健康效益,成為亟待釐清之問題。為了瞭解國內底泥品質現況,並進一步擬定品質基準,管理管制策略及處理技術評估等相關綱要事項,行政院環境保護署乃辦理本計畫。計畫工作成果包括: 研訂配套子法與行政規則,建置底泥品質檢測及評估機制,建立底泥健康及生態風險評估及污染調查機制等。目前於母法管理底泥相關規定之框架下,本工作團隊已協助完成之工作包括協助環保署針對:(一)底泥品質指標之分類管理及用途限制辦法、(二)目的事業主管機關檢測底泥品質備查作業辦法、(三)底泥之環境影響與健康風險、技術及經濟效益評估方法及撰寫指引、(四)底泥整治可行性評估及核可原則及(五)底泥整治計畫撰寫指引等子法及行政指引完成公告或即將公告的相關行工作。此外,鑑於底泥管理法令體制建立初期亟需指導性計畫,為確立短、中、長期底泥污染管制及整治工作執行方向及事涉各部會之權責分工,以有效整合行政資源,訂定底泥管理管制方案以作為相關子法及指引確立前,管理工作之依據。 底泥品質檢測評估為後續管理行動之起動點,未來納入管理之水體包括河川、湖泊水庫及灌溉渠道,為了瞭解國底泥重要水體底泥品質現況,本計畫即針對二仁溪、大肚溪、澄清湖、寶山水庫等不同水體進行底泥調查工作,同時依第一次進度報告會議中決議針對大肚溪進行底泥調查工作。整體而言,在兩次調查中共完成125個採樣點調查分析,其中湖泊水庫底泥濃度除了部份採樣點中鎳超過品質指標下限值外,均無異常現象。至於河川中底泥,則以三爺溪多數測站重金屬濃度超過品質指標上限值,二仁溪下游疑因受三爺溪水流入所致,於匯流口處測站11、13、49亦有濃度超過指標上限值之現象。三爺溪永寧橋在第二次調查戴奧辛超過指標上限值。三爺溪及二仁溪流域近年常見由台南市環保單位查獲不法業者排放廢水,建議仍加強稽查,落實源頭管理。至於大肚溪上游(烏溪)支流旱溪河段於兩次監測中重金屬濃度(汞、鎳)有超過指標上限值之現象,以國光橋濃度最高但往下游濃度有逐漸降低的趨勢。 針對二仁溪部份採樣點位之樣品進行底泥全毒性分析,結果顯示其中14個(56%)樣站為Tier 1(即可能對水體生物或人體健康有害),而三爺溪(SY)流域的樣站底泥毒性試驗結果皆為Tier 1,為污染最為嚴重的區段。因此進一步針對二仁溪及三爺溪下游河段進行底泥生態風險及健康風險評估工作。經由生物調查結果,受體生物考慮以兩次調查中二仁溪中較優勢之魚種斑海鯰(底棲)為主,其經濟價值不高,惟仍具食用之價值。本計畫針對二仁溪及三爺溪下游魚體進行部份關切污染物(品質指標項目:銅、鋅、鉛、鉻、鎘、多氯聯苯及多環芳香烴等)之檢測,其中第一次調查鉛含量檢出值最高者為區段1夏威夷海鰱 (0.968 mg/kg),共四組魚體樣品中鉛含量超過水產動物類衛生標準(可食部分含量限值為0.3 mg/kg)。魚體戴奧辛濃度第二次調查中測得大鱗鯔戴奧辛濃度高達3.087 ng-TEQ/kg 已接近食用限值,而該樣品多氯聯苯亦測出245.5 µg/kg,為所有樣品中濃度最高(食用限值為1000 µg/kg 濕重)。至於第二次調查魚體濃度較高原因可能係因採樣時為冬季(2月),魚體累積較多油脂(約四倍)。 受污染之底泥主要可分為有機污染物(如PCBs、戴奧辛)與重金屬污染物(如銅、鋅、鎘及鉛等)兩大類。由於實際環境介質複雜,在污染處理技術上要同時去除吸附性高且親合性強的有機及無機污染物較不易,因此通常配合底泥移除、處置技術,如環保抽濬,將受污染底泥與當地環境分離,再針對污染物進行處理。本工作團隊簡要說明整治技術使用的時機與運用原則,簡述常見的整治技術包括現地、離場處理技術、底泥移除與暫存、物理、化學、生物處理技術簡介,說明國際間運用底泥整治技術的實際案例,最後說明現階段國際間發展中的底泥污染整治與監測技術。
中文關鍵字 底泥,管理策略,污染調查, 風險評估

基本資訊

專案計畫編號 EPA-99-GA101-03-A205 經費年度 099 計畫經費 35380 千元
專案開始日期 2010/11/29 專案結束日期 2013/01/28 專案主持人 方孟德
主辦單位 土污基管會 承辦人 王禎 執行單位 財團法人工業技術研究院

成果下載

類型 檔名 檔案大小 說明
期末報告 EPA-99-GA101-03-A205(公開版).pdf 52MB

Program for Managing Contaminated Sediments in Taiwan from 2010 to 2012

英文摘要 In the recent years, there were many sediment sites found contaminated in Taiwan. Whether removal or not does involve in the huge amount of cost and the uncertainty of environmental and health issues that need to be clarified. In order to make clear of sediment quality in Taiwan and further establish the quality guidelines, management strategy, and treatment technology evaluation, the Environmental Protection Administration (EPA) of the Executive Yuan offered the opportunity of the this project study. The results of this project include the establishments of the related regulation, sediment quality analysis and evaluation mechanism, health and ecological risk assessment, and contamination investigation mechanism. Under the framework of the current “Soil and Groundwater Protection Act” regarding sediments, the workgroup of this project has assisted EPA in the following: 1. Classification Management and Use Limitation Regulation of Sediment Quality Indicator, 2. Regulation in Sediment Quality Reporting Issued from Industry Competent Authorities of Sediment, 3. Assessment Method and Report Composition Guideline of Environmental Impact, Health Risk, and Technology and Economical Evaluation of Sediment, 4. Feasibility Evaluation and Approval Principle of Sediment Remediation, and 5. Composition Guideline of Sediment Remediation Proposal. Besides, it is necessary to have a guiding project in the early stage of the sediment regulation establishment served as a management basis; thus, a workforce allocation among different governmental departments regarding sediment quality assurance and control in the near, middle, and long run was studied to make sure a better use of administrative resources before the sediment quality control mechanism is up and running. The sediment quality evaluation is the trigger of a series of the later-on management in sediment. The waters of the regulated sediments include rivers, lakes, reservoirs, and irrigation ditches. In order to know the current status of the sediment quality in the most important waters, this project took the chance to investigate the sediments in the Er-jen River, Da-du River, Chengcing Lake Reservoir, and Bao-shan Reservoir. Overall, a total 125 grab samples in the 2 investigations were analyzed. Among the 125 samples, only small amount of lake sediment samples were found concentrations over the lower limit of the nickel quality guideline and others were found normal in quality. With respect to river sediments, most samples from the San-ye River (tributary of the Er-jen River) were found high in heavy metals and over the respective upper limits. The downstream of the Er-jen River at the Sampling Station 11, 13, and 49 was found that some constituents were over the upper limits, possibly due to the convergence of San-ye River into the Er-jen River. Dioxins concentrations found in the San-ye River near the Yun-ning Bridge in the second sampling were over the upper limit. The San-ye River and the Er-jen River watershed were found illegal release of wastewater by the Tainan Environmental Protection Bureau. It is recommended to enhance the patrol so that the pollution source can be controlled. With respect to the tributary (Han River) of the upstream of the Da-du River, heavy metals of mercury and nickel were found over the upper limits in both samplings. For the toxicity tests of some samples from the Er-jen River, the results showed that 14 samples (56%) were found Tier I (possibly harmful to aquatic life and human health). In the San-ye River, all results of toxicity tests showed Tier I level, indicating the most polluted region. Thus, sediment ecological risk and health risk assessments in the Er-jen River and the downstream of the San-ye River were conducted. Biological investigation targets were Arius maculates in the Er-jen River, although its economic values is not high but it serves as food. Sediment quality guideline constituents, such as copper, zinc, lead, chromium, cadmium, PCBs, and PAHs, were tested on the fish samples. Lead concentration was found high in Elops hawaiensis (0.968 mg/kg) in the first sampling attempt, with 4 samples found high in lead over the aquatic livestock limit (edible portion: 0.3 mg/kg). In the second sampling attempt, the dioxins concentration of Liza macrolepis was found 3.087 ng-TEQ/kg, close to the food consumption limit. The same sample also showed high concentration of PCBs of 245.5 µg/kg, the highest concentration of all fish samples (food consumption limit is 1,000 µg/kg wet weight). The reason why the fish in the second sampling attempt were found high in contaminant concentration could be that the fish had more fat (about 4 times as usual) in February (winter). The contaminated sediments can be categorized into organic matters (PCBs and dioxins) and heavy metals (copper, zinc, cadmium, and lead). Because the real environments are of complexity, it is not easy to remove organic and inorganic contaminants of high affinity at the same time. With respect to choose the right methods for removing contaminated sediments in Taiwan, such as environmental dredging, which will help avoiding contaminants resuspended into aquatic environments before treatments. This project summarized the timing and the principles of using remediation actions, including in situ remediation, off-site remediation, environmental dredging and storage, physical, chemical, and biological treatments. A few international examples of sediment remediation were introduced, as well as the most current update of technology development regarding sediment remediation and investigation.
英文關鍵字 sedimen;management strategy;pollution investigation;risk assessment