廢乾電池回收貯存清除處理方法及設施標準
- Jurisdiction:
- Taiwan
- Type:
- EPR · Disposal Ban
- Last action:
- Oct 16, 2002
Review this measure’s obligations and confirm whether they reach your products
Applies toNot specified in this measure; this standard governs collection, storage, transport, and processing methods/facilities rather than defining producers.
- ·Vehicles used for transport must have rain-protection measures and prevent spillage, leakage, scattering, or falling of waste batteries.
- ·Transport vehicles must carry emergency response equipment/materials, emergency fire-extinguishing equipment, and first-aid kits.
- ·Storage locations, containers, and facilities must be kept clean and intact; no waste falling, spillage, leakage, odor, ground contamination, water accumulation, or harmful gas diffusion is permitted.
No designated program action is recorded for this measure yet — treat the above as the general obligation and verify against the source text.
- ·Waste dry batteries (廢乾電池) as announced under Article 15, Paragraph 2 of the Waste Disposal Act, including primary batteries and secondary (rechargeable) batteries such as nickel-cadmium batteries, button-type batteries, alkaline manganese batteries, manganese-zinc batteries, lithium batteries, mercury oxide batteries, silver oxide batteries
- ·Vehicles used for transport must have rain-protection measures and prevent spillage, leakage, scattering, or falling of waste batteries.
- ·Transport vehicles must carry emergency response equipment/materials, emergency fire-extinguishing equipment, and first-aid kits.
- ·Storage locations, containers, and facilities must be kept clean and intact; no waste falling, spillage, leakage, odor, ground contamination, water accumulation, or harmful gas diffusion is permitted.
- ·Storage containers and facilities must be compatible with the waste dry batteries stored and sufficient to prevent electrolyte leakage or corrosion.
- ·Collection and storage sites must have building structures preventing rainwater ingress and impermeable flooring.
- ·Waste liquids, gases, and odors from storage facilities must be collected or prevented from contaminating ground/groundwater, air, and soil.
- ·Storage site perimeters must be fenced.
- ·Classified waste dry batteries, recyclables, and waste must be stored in separate zones and labeled in both Chinese and English with type and name at conspicuous locations.
- ·Waste dry batteries must not be disassembled, deformed, or have electrolyte leaked during collection, storage, or transport.
- ·Secondary (rechargeable) batteries must be discharged before storage.
- ·Fire-fighting equipment and emergency shower/safety equipment must be installed at storage sites.
- ·Before processing, waste dry batteries must be sorted by battery type; mixed processing is not permitted without approval from the central competent authority.
- ·Secondary batteries must be discharged before processing.
- ·Processing must comply with soil and groundwater pollution remediation regulations and prevent pollutants from entering soil or groundwater.
- ·Waste dry batteries with mercury and its compounds content ≥260 mg/kg must be processed using thermal treatment to recover mercury; those below 260 mg/kg may use other methods.
- ·Processing of button-type waste dry batteries: leaching test results for mercury in materials produced for reuse and waste must be below 0.025 mg/L.
- ·Thermal treatment facilities must operate under negative pressure with sealed equipment, explosion-proof devices, metal recovery equipment, and exhaust gas collection/treatment systems.
- ·Thermal treatment facilities must conduct flue gas testing and report cadmium and compounds, lead and compounds, and mercury and compounds results during periodic inspection filings under the Air Pollution Control Act.
- ·Smelting (熔煉法) as thermal treatment: feed types must be manganese-zinc batteries, cylindrical alkaline manganese batteries, or batteries with mercury content below 1 ppm, and feed weight must not exceed 3% of the total raw material batch input.
- ·Thermal treatment of button-type batteries must include mercury condensation recovery equipment for mercury pollution control, except for button-type lithium batteries.
- ·Wet processing facilities must have dissolution, metal recovery, and wastewater treatment equipment.
- ·Wet processing facilities must conduct wastewater discharge testing and report cadmium and compounds, lead and compounds, and mercury and compounds results during periodic inspection filings under the Water Pollution Prevention Act.
- ·Processing facilities must have solid foundation structures.
- ·Facilities must have equipment or measures to prevent surface water, rainwater, and groundwater from entering or seeping in.
- ·Facilities must have measures to prevent waste battery falling, odor emission, ground contamination, and impact on surrounding environmental quality.
- ·Waste liquids, gases, and odors from processing facilities must have collection equipment or anti-corrosion measures.
- ·Pollution control equipment for mercury, cadmium, and lead must be installed.
- ·Emergency response measures and pollution prevention/control plans must be prepared.
- ·Export of waste dry batteries for overseas processing requires approval from the central competent authority and is limited to OECD member countries with processing facilities.
- ·Certain categories of waste dry batteries (internationally regulated mixed batteries, mercury oxide, silver oxide, nickel-cadmium, or other internationally regulated materials, batteries recognized as hazardous by receiving/transit countries, or others designated by the central authority) must follow hazardous waste export regulations under the Industrial Waste Import/Export Management Regulations.
- ·Waste generated after collection, storage, transport, and processing must comply with this standard; industrial waste must also comply with Industrial Waste Storage, Transport, and Processing Methods and Facilities Standards and Article 28 of the Waste Disposal Act.
- ·Export of waste generated from processing must comply with Article 38 of the Waste Disposal Act.
- ·To apply for subsidies from the Resource Recycling Management Fund: overseas processing must follow Article 5; domestic processing resource recovery and reuse ratio must meet thresholds (nickel-cadmium batteries ≥75%; other battery types ≥50%; smelting or melting methods are exempt from these ratios); cadmium recovered from processing must be properly recycled and not arbitrarily discarded; a sorting efficiency and equipment trial-run report must be submitted.
- ·Button-type lithium batteries are exempt from the requirement to install mercury condensation recovery equipment when processed by thermal treatment.
- ·Processors using smelting (熔煉法) or melting (熔融法) methods are exempt from the resource recovery and reuse ratio thresholds (75% for nickel-cadmium; 50% for others) when applying for subsidies.
- ·Waste dry batteries meeting certain conditions (internationally regulated mixed batteries, mercury oxide, silver oxide, nickel-cadmium, or other internationally regulated materials, batteries recognized as hazardous by receiving/transit countries) are excluded from the standard overseas export route and must follow hazardous waste export regulations.
“一、回收之廢乾電池於處理前,應依電池種類完成分類;非經中央主管機關認可,不得混合處理。 (三)採用熔煉法作為處理方式者,廢乾電池進料種類應為錳鋅電池、筒型鹼錳電池或汞含量低於一ppm之電池,且進料重量不超過該批原料投料量百分之三。 廢乾電池輸出國外處理者,應經中央主管機關核准,並以輸出至經濟合作暨發展組織(OrganizationforEconomicCooperationandDevelopme-nt,OECD)會員國且具有處理設施者為限。 九、廢乾電池於回收、貯存、清除過程中,不得拆解、破壞原形及造成電解液外漏情事。”
“八、經完成分類之廢乾電池及其再生料、廢棄物應分區貯存,並於明顯處,以中英文標示其種類及名稱。”
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Full bill text
第 1 條 本標準依廢棄物清理法(以下簡稱本法)第十八條第一項規定訂定之。 廢乾電池回收貯存清除處理方法及設施依本標準之規定,本標準未規定者,適用其他法令之規定。 第 2 條 本標準用詞,定義如下: 一、廢乾電池:指依本法第十五條第二項公告應回收之廢乾電池。 二、回收:指將廢乾電池收集、分類之行為。 三、貯存:指廢乾電池於回收、清除、處理前,放置於特定地點或貯存容器、設施內之行為。 四、清除:指廢乾電池收集、運輸之行為。 五、處理:指廢乾電池於再利用前,以物理、化學或其他處理方法,改變其物理、化學特性,達到純化、精煉、分離、無害化及資源化之行為。 六、再利用:指已回收之廢乾電池經處理後,供作材料、原料或其他經中央目的事業主管機關認定之用途行為。 七、相容性:指廢乾電池與其貯存容器、棧板、處理設施材質或其他物質接觸後,不發生下列效應者: (一)產生熱。 (二)產生激烈反應、火災或爆炸。 (三)產生可燃性流體或有害流體。 (四)造成容器材料劣化,致降低污染防治之效果。 八、熱處理法: (一)焚化法:指利用高溫燃燒,將廢乾電池轉變成安定之氣體或物質之處理方法。 (二)熱解法:指將廢乾電池置於無氧或少量氧之狀態下,利用熱能裂解使其分離成為氣體、液體或殘渣之處理方法。 (三)熔融法:指將廢乾電池加熱至熔流點以上,使其中所含有害有機物質進一步氧化或重金屬揮發,其餘有害物質則存留於熔渣中產生穩定化固化作用之處理方法。 (四)熔煉法:指將廢乾電池併入金屬高溫冶煉製程中,合併進行高溫減量處理或金屬資源回收之處理方法。 (五)其他熱處理方法。 九、濕式處理法:指以處理液(如無機酸溶液等)將廢電池中之各項成分進行萃取後,再予以純化回收之處理方法。 十、二次電池:指可透過充電過程,使電池內之活性物質回復至原來狀態,以再度提供電力,並重複使用之電池。 十一、資源回收再利用比率:指廢乾電池經處理後,再生料之總和重量占其總處理量之比率。 第 3 條 廢乾電池回收、貯存、清除方法及設施,應符合下列規定: 一、運送時,車輛機具應設置防雨措施,並避免發生溢出、洩漏、飛散、掉落等造成污染環境或危害人體健康之情事。 二、運送之車輛機具應具備緊急應變處理設備或材料、緊急滅火設備及急救箱等。 三、貯存之地點、容器、設施應經常保持清潔完整,不得有廢棄物掉落、溢散、洩漏、散發惡臭、污染地面、積水或有害氣體擴散及洩漏等情事。 四、貯存容器、設施應與所貯存之廢乾電池具有相容性,並足以防止電解液滲漏或造成腐蝕。 五、回收貯存場地應採防止雨水進入之建築結構,其地面應為不透水鋪面。 六、由貯存設施產生之廢液、廢氣、惡臭等,應有收集或防止其污染地面或地下水體、空氣、土壤之設備或措施。 七、貯存場(廠)區四周應設置圍籬。 八、經完成分類之廢乾電池及其再生料、廢棄物應分區貯存,並於明顯處,以中英文標示其種類及名稱。 九、廢乾電池於回收、貯存、清除過程中,不得拆解、破壞原形及造成電解液外漏情事。 十、二次電池應進行放電後再行貯存。 十一、應設置消防設備及緊急沖淋安全設備。 十二、其他經中央主管機關指定者。 第 4 條 廢乾電池於國內處理,其處理方法及設施應符合下列規定: 一、回收之廢乾電池於處理前,應依電池種類完成分類;非經中央主管機關認可,不得混合處理。 二、二次電池應進行放電後再行處理。 三、處理過程中應依土壤及地下水污染整治法規規定,並避免污染物質進入土壤或地下水。 四、廢乾電池中汞及其化合物含量,每公斤濃度達二百六十毫克以上者,應以熱處理法回收汞,低於二百六十毫克者,得採其他方式處理;處理鈕扣型廢乾電池所產出供作再利用之物質及廢棄物溶出試驗結果,其汞溶出量應低於每公升零點零二五毫克。 五、以熱處理法處理廢乾電池者,應符合下列規定: (一)於負壓環境操作,並具備密閉設備、防爆裝置、金屬回收設備及廢氣收集處理系統。 (二)應進行煙道檢測,並依空氣污染防制法規定,於定期檢測申報時,一併申報鎘及其化合物、鉛及其化合物、汞及其化合物之檢測結果。 (三)採用熔煉法作為處理方式者,廢乾電池進料種類應為錳鋅電池、筒型鹼錳電池或汞含量低於一ppm之電池,且進料重量不超過該批原料投料量百分之三。 (四)採熱處理法處理鈕扣型電池者,其汞污染防制設備應設置汞冷凝回收設備。但處理鈕扣型鋰電池者,不在此限。 六、以濕式處理法處理乾電池者,應符合下列規定: (一)應具備溶解、金屬回收及廢水處理設備。 (二)應進行廢水排放檢測,並依水污染防治法規定,於定期檢測申報時,一併申報鎘及其化合物、鉛及其化合物、汞及其化合物之檢測結果。 七、具備堅固之基礎結構。 八、設施周圍應有防止地面水、雨水及地下水流入、滲透之設備或措施。 九、具備防止廢乾電池掉落、散發惡臭、污染地面及影響四周環境品質之必要措施。 十、處理設施產生之廢液、廢氣、惡臭等,應有收集設備或防蝕措施。 十一、應設置汞、鎘、鉛之污染防制設備。 十二、備有緊急應變措施及污染防制(治)計畫書。 十三、其他經中央主管機關指定者。 廢乾電池之處理方法及設施,本標準未規定者,準用事業廢棄物貯存清除處理方法及設施標準規定。 第 5 條 廢乾電池輸出國外處理者,應經中央主管機關核准,並以輸出至經濟合作暨發展組織(OrganizationforEconomicCooperationandDevelopme-nt,OECD)會員國且具有處理設施者為限。廢乾電池申請輸出處理應檢具之文件,由中央主管機關公告並刊登政府公報。 廢乾電池有下列情形之一者,不適用第一項規定,應依事業廢棄物輸入輸出管理辦法之有害廢棄物輸出規定辦理: 一、屬國際公約列管之混雜廢乾電池。 二、廢乾電池種類為氧化汞、氧化銀、鎳鎘或其他國際公約列管之材質。 三、經其他接受國或過境國之國內法認定為有害之廢乾電池。 四、其他經中央主管機關指定者。 第 6 條 廢乾電池經回收、貯存、清除及處理後之廢棄物,應依本標準規定辦理,其屬事業廢棄物者,除應依事業廢棄物貯存清除處理方法及設施標準規定貯存、清除及處理外,並應符合本法第二十八條規定之清理方式。 前項廢棄物之輸出,應符合本法第三十八條規定。 第 7 條 依本法第十八條第五項規定向資源回收管理基金申請廢乾電池回收清除處理補貼者,應符合下列規定: 一、輸出國外處理,依第五條規定辦理。 二、於國內處理廢乾電池,其資源回收再利用比率應符合下列規定: (一)屬鎳鎘電池,應達百分之七十五。 (二)屬其他種類電池,應達百分之五十。 (三)以熔煉法或熔融法處理廢乾電池,不受前二目規定限制。 三、廢乾電池回收處理後之鎘應妥善回收,不得任意棄置。 四、國內處理廢乾電池,應提送分類效能及處理設備試運轉報告。 五、其他經中央主管機關指定者。 第 8 條 本標準自發布日施行。
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