2006-66-EC电池指令_中文
2006 66 EC电池指令(中文)
2006/66/EC电池指令(中文)2006-66-EC电池指令(中文)欧洲议会和欧盟理事会2006年9月2日第2006/66/EC号关于电池及蓄电池、废弃电池及蓄电池以及废止91/157/EEC的指令欧洲议会和欧盟理事会注意到建立欧洲共同体条约，特别是其中第175（1）条和第95（1）条，注意到欧盟委员会的提案，注意到欧洲经济社会委员会的提案，注意到欧盟地区委员会的意见，按照欧洲共同体条约第251条所制定的程序以及协调委员会2006年6月22日通过的联合文本，鉴于：(1) 协调各国家跟电池及蓄电池、废弃电池及蓄电池有关的措施是有利的。
这个指令的主要目的是将电池及蓄电池、废弃电池及蓄电池对环境的影响减到最少，从而对保护、保存和改善环境指令做出贡献。
立法75（1）条。
然而，采取基于第95（1）条来协调与重金属含量及电池及蓄电池标识有关的措施也是合适的，目的是确保在欧洲共同体内部市场顺利实施，并避免内部的不正当竞争。
(2) 欧盟理事会通讯于1996年7月30公布的关于欧洲共同体废弃物处理策略综述为欧洲共同体未来的废弃物政策确立了指导方针。
通讯强调了减少废弃物中有害物质含量的必要性，指出在整个欧洲共同体范围内在产品及产品制造过程中限制使用这些有害物质规则的潜在好处。
通讯还说明既然废弃物的产生是不能避免的，那么废弃物应该在材料或能源上循环再利用。
(3) 欧洲议会1988年1月25日决议关于欧洲共同体抗击由镉引起的环境污染行动计划强调，为了保护人类健康和环境，镉控制的策略是限制镉的使用场合和收集、回收含镉电池。
(4) 欧洲议会1991年3月18日第91/157/EEC号关于含有某些有害物质的电池及蓄电池指令使一些成员国在这个领域制定了一些法律。
然而，指令的一些目的没有完全达到。
第1600/2002/EC号制定的第六个欧洲共同体环境行动计划决议和第2002/96/EC号关于电子电气设备废弃指令（WEEE）也强调91/157/EEC指令需要修改。
电池指令英文(2006-66-EC)
I(Acts whose publication is obligatory)DIRECTIVE2006/66/EC OF THE EUROPEAN PARLIAMENT AND OF THE COUNCILof6September2006on batteries and accumulators and waste batteries and accumulators and repealing Directive91/157/EEC(Text with EEA relevance)THE EUROPEAN PARLIAMENT AND THE COUNCIL OF THE EURO-PEAN UNION,Having regard to the Treaty establishing the European Com-munity,and in particular Article175(1)thereof and Article95(1)thereof in relation to Articles4,6and21of this Directive,Having regard to the proposal from the Commission(1),Having regard to the opinion of the European Economic and Social Committee(2),Having regard to the opinion of the Committee of Regions(3),Acting in accordance with the procedure laid down in Article251of the Treaty(4),in the light of the joint text approved by the Conciliation Committee on22June2006,Whereas:(1)It is desirable to harmonise national measuresconcerning batteries and accumulators and wastebatteries and accumulators.The primary objective of thisDirective is to minimise the negative impact of batteriesand accumulators and waste batteries and accumulatorson the environment,thus contributing to the protection,preservation and improvement of the quality of theenvironment.The legal base is therefore Article175(1)of the Treaty.However,it is also appropriate to takemeasures at Community level on the basis ofArticle95(1)of the Treaty to harmonise requirementsconcerning the heavy metal content and labelling ofbatteries and accumulators and so to ensure the smoothfunctioning of the internal market and avoid distortionof competition within the Community.(2)The Commission Communication of30July1996onthe Review of the Community Strategy for WasteManagement established guidelines for future Com-munity waste policy.That Communication stresses theneed to reduce the quantities of hazardous substances inwaste and points out the potential benefits of Com-munity-wide rules limiting the presence of suchsubstances in products and in production processes.Itfurther states that,where the generation of waste cannotbe avoided,that waste should be reused or recovered forits material or energy.(3)The Council Resolution of25January1988on a Com-munity action programme to combat environmentalpollution by cadmium(5)stressed the limitation of theuses of cadmium to cases where suitable alternatives donot exist and the collection and recycling of batteriescontaining cadmium as major elements of the strategyfor cadmium control in the interests of the protection ofhuman health and the environment.(4)Council Directive91/157/EEC of18March1991onbatteries and accumulators containing certain dangeroussubstances(6)has brought about an approximation ofMember States'laws in this field.However,the objectivesof that Directive have not been fully attained.DecisionNo1600/2002/EC of the European Parliament and ofthe Council of22July2002laying down the Sixth Com-munity Environment Action Programme(7)and Direc-tive2002/96/EC of the European Parliament and of theCouncil of27January2003on waste electrical and elec-tronic equipment(WEEE)(8)also underlined the need forDirective91/157/EEC to be revised.Directive91/157/EEC should therefore be revised and replaced inthe interests of clarity.(1)OJ C96,21.4.2004,p.29.(2)OJ C117,30.4.2004,p.5.(3)OJ C121,30.4.2004,p.35.(4)Opinion of the European Parliament of20April2004(OJ C104E,30.4.2004,p.354),Council Common Position of18July2005(OJC264E,25.10.2005,p.1)and Position of the European Parliament of13December2005(not yet published in the Official Journal).(5)OJ C30,4.2.1988,p.1.(6)OJ L78,26.3.1991,p.38.Directive as amended by CommissionDirective98/101/EC(OJ L1,5.1.1999,p.1).(7)OJ L242,10.9.2002,p.1.(5)In order to achieve its environmental aims,this Directiveprohibits the placing on the market of certain batteriesand accumulators containing mercury or cadmium.Italso promotes a high level of collection and recycling ofwaste batteries and accumulators and improved environ-mental performance of all operators involved in the lifecycle of batteries and accumulators, e.g.producers,distributors and end-users and,in particular,thoseoperators directly involved in the treatment and recy-cling of waste batteries and accumulators.The specificrules needed to do this are supplementary to existingCommunity legislation on waste,in particular Direc-tive2006/12/EC of the European Parliament and of theCouncil of5April2006on waste(1),Council Direc-tive1999/31/EC of26April1999on the landfill ofwaste(2)and Directive2000/76/EC of theEuropean Parliament and of the Council of4December2000on the incineration of waste(3).(6)In order to prevent waste batteries and accumulatorsfrom being discarded in such a way as to pollute theenvironment,and to avoid end-user confusion about thedifferent waste management requirements for differentbatteries and accumulators,this Directive should applyto all batteries and accumulators placed on the marketwithin the Community.Such a wide scope should alsoensure economies of scale in collection and recycling,aswell as optimal resource saving.(7)Reliable batteries and accumulators are fundamental forthe safety of many products,appliances and services,and are an essential energy source in our society.(8)It is appropriate to distinguish between portable batteriesand accumulators on the one hand and industrial andautomotive batteries and accumulators on the other.Thedisposal of industrial and automotive batteries and accu-mulators in landfill sites or by incineration should beprohibited.(9)Examples of industrial batteries and accumulatorsinclude batteries and accumulators used for emergencyor back-up power supply in hospitals,airports or offices,batteries and accumulators used in trains or aircraft andbatteries and accumulators used on offshore oil rigs orin lighthouses.Examples also include batteries and accu-mulators designed exclusively for hand-held paymentterminals in shops and restaurants,bar code readers inshops,professional video equipment for TV channelsand professional studios,miners'lamps and diving lampsattached to mining and diving helmets for professionals,back up batteries and accumulators for electric doors toprevent them from blocking or crushing people,batteries and accumulators used for instrumentation orin various types of measurement and instrumentationequipment and batteries and accumulators used inconnection with solar panel,photo-voltaic,and otherrenewable energy applications.Industrial batteries andaccumulators also include batteries and accumulatorsused in electrical vehicles,such as electric cars,wheel-chairs,bicycles,airport vehicles and automatic transportvehicles.In addition to this non exhaustive list of exam-ples,any battery or accumulator that is not sealed andnot automotive should be considered industrial.(10)Examples of portable batteries and accumulators,whichare all-sealed batteries and accumulators that an averageperson could carry by hand without difficulty and thatare neither automotive batteries or accumulators norindustrial batteries or accumulators,include single cellbatteries(such as AA and AAA batteries)and batteriesand accumulators used by consumers or professionals inmobile telephones,portable computers,cordless powertools,toys and household appliances such as electrictoothbrushes,razors and hand-held vacuum cleaners(including similar equipment used in schools,shops,restaurants,airports,offices or hospitals)and any batteryor accumulator that consumers may use for normalhousehold applications.(11)The Commission should evaluate the need for adaptationof this Directive,taking account of available technicaland scientific evidence.In particular,the Commissionshould carry out a review of the exemption from thecadmium ban provided for portable batteries and accu-mulators intended for use in cordless power tools.Exam-ples of cordless power tools are tools that consumersand professionals use for turning,milling,sanding,grinding,sawing,cutting,shearing,drilling,makingholes,punching,hammering,riveting,screwing,polishing or similar processing of wood,metal and othermaterials,as well as for mowing,cutting and othergardening activities.(12)The Commission should also monitor,and MemberStates should encourage,technological developmentsthat improve the environmental performance of batteriesand accumulators throughout their entire life cycle,including through participation in a Community eco-management and audit scheme(EMAS).(13)In order to protect the environment,waste batteries andaccumulators should be collected.For portable batteriesand accumulators,collection schemes achieving a highcollection rate should be established.This means settingup collection schemes so that end-users can discard allwaste portable batteries and accumulators conveniently(1)OJ L114,27.4.2006,p.9.(2)OJ L182,16.7.1999,p.1.Directive as amended by Regulation(EC)(14)It is desirable for Member States to achieve a high collec-tion and recycling rate for waste batteries and accumula-tors so as to achieve a high level of environmentalprotection and material recovery throughout the Com-munity.This Directive should therefore set minimumcollection and recycling targets for Member States.It isappropriate to calculate the collection rate on the basisof average annual sales in preceding years,so as to havecomparable targets for all Member States that areproportionate to the national level of battery and accu-mulator consumption.(15)Specific recycling requirements should be established forcadmium and lead batteries and accumulators in orderto attain a high level of material recovery throughoutthe Community and to prevent disparities betweenMember States.(16)All interested parties should be able to participate incollection,treatment and recycling schemes.Thoseschemes should be designed to avoid discriminationagainst imported batteries and accumulators,barriers totrade or distortions of competition.(17)Collection and recycling schemes should be optimised,in particular in order to minimise costs and the negativeenvironmental impact of transport.Treatment and recy-cling schemes should use best available techniques,asdefined in Article2(11)of Council Directive96/61/ECof24September1996concerning integrated pollutionprevention and control(1).The definition of recyclingshould exclude energy recovery.The concept of energyrecovery is defined in other Community instruments.(18)Batteries and accumulators can be collected individually,by way of national battery collection schemes ortogether with waste electrical and electronic equipment,by way of national collection schemes set up on thebasis of Directive2002/96/EC.In the latter case,as anobligatory minimum treatment requirement,batteriesand accumulators should be removed from the collectedwaste electrical and electronic equipment.After theirremoval from the waste electrical and electronic equip-ment,batteries and accumulators are subject to therequirements of this Directive,notably they count forachieving the collection target and are subject to recy-cling requirements.(19)Basic principles for financing the management of wastebatteries and accumulators should be set at Communitylevel.Financing schemes should help to achieve highcollection and recycling rates and to give effect to theprinciple of producer responsibility.All producers asdefined by this Directive should be registered.Producersshould finance the costs of collecting,treating and recy-cling all collected batteries and accumulators minus theprofit made by selling the materials recovered.However,under certain circumstances,the application of deminimis rules to small producers could be justified.(20)The provision of information to end-users on the desir-ability of separate collection,the collection schemesavailable and end-users'role in the management of wastebatteries and accumulators is necessary for successfulcollection.Detailed arrangements should be made for alabelling system,which should provide end-users withtransparent,reliable and clear information on batteriesand accumulators and any heavy metals they contain.(21)If,in order to achieve the objectives of this Directive,and,in particular,to achieve high separate collectionand recycling rates,Member States use economic instru-ments,such as differential tax rates,they should informthe Commission accordingly.(22)Reliable and comparable data on the quantities ofbatteries and accumulators placed on the marketcollected and recycled are necessary for monitoringwhether the objectives of this Directive have beenachieved.(23)Member States should lay down rules on the penaltiesapplicable to infringements of the provisions of thisDirective and ensure that they are implemented.Thosepenalties should be effective,proportionate and dissua-sive.(24)In accordance with paragraph34of the Interinstitutionalagreement on better law-making(2),Member States areencouraged to draw up,for themselves and in the inter-ests of the Community,their own tables,which will,asfar as possible,illustrate the correlation between thisDirective and the transposition measures and to makethem public.(25)The measures necessary for the implementation of thisDirective should be adopted in accordance with CouncilDecision1999/468/EC of28June1999laying downthe procedures for the exercise of implementing powersconferred on the Commission(3).(26)Since the objectives of this Directive namely protectingthe environment and ensuring the proper functioning ofthe internal market cannot be sufficiently achieved bythe Member States and can therefore,by reason of thescale or effects of the action,be better achieved at Com-munity level,the Community may adopt measures,inaccordance with the principle of subsidiarity as set outin Article5of the Treaty.In accordance with the prin-ciple of proportionality,as set out in that Article,thisDirective does not go beyond what is necessary in orderto achieve those objectives.(27)This Directive applies without prejudice to Communitylegislation on safety,quality and health requirements andspecific Community waste management legislation,inparticular Directive2000/53/EC of the European Parlia-ment and of the Council of18September2000on end-of-life vehicles(1)and Directive2002/96/EC.(28)As regards producer responsibility,producers of batteriesand accumulators and producers of other productsincorporating a battery or accumulator are responsiblefor the waste management of batteries and accumulatorsthat they place on the market.A flexible approach isappropriate to enable financing schemes to reflectdiffering national circumstances and to take account ofexisting schemes,particularly those set up to complywith Directives2000/53/EC and2002/96/EC,whileavoiding double charging.(29)Directive2002/95/EC of the European Parliament and ofthe Council of27January2003on the restriction of theuse of certain hazardous substances in electrical andelectronic equipment(2)does not apply to batteries andaccumulators used in electrical and electronic equip-ment.(30)Automotive and industrial batteries and accumulatorsused in vehicles should meet the requirements of Direc-tive2000/53/EC,in particular Article4thereof.There-fore the use of cadmium in industrial batteries and accu-mulators for electrical vehicles should be prohibited,unless they can benefit from an exemption on the basisof Annex II to that Directive,HAVE ADOPTED THIS DIRECTIVE:Article1Subject-matterThis Directive establishes:(1)rules regarding the placing on the market of batteries andaccumulators and,in particular,a prohibition on the placing on the market of batteries and accumulators containing hazardous substances;and(2)specific rules for the collection,treatment,recycling anddisposal of waste batteries and accumulators to supplement relevant Community legislation on waste and to promote a high level of collection and recycling of waste batteries and accumulators.It seeks to improve the environmental performance of batteries and accumulators and of the activities of all economic opera-tors involved in the life cycle of batteries and accumulators,e.g.producers,distributors and end-users and,in particular, those operators directly involved in the treatment and recycling of waste batteries and accumulators.Article2Scope1.This Directive shall apply to all types of batteries and accumulators,regardless of their shape,volume,weight,mate-rial composition or use.It shall apply without prejudice to Directives2000/53/EC and2002/96/EC.2.This Directive shall not apply to batteries and accumula-tors used in:(a)equipment connected with the protection of MemberStates'essential security interests,arms,munitions and war material,with the exclusion of products that are not intended for specifically military purposes;(b)equipment designed to be sent into space.Article3DefinitionsFor the purposes of this Directive,the following definitions shall apply:(1)‘battery’or‘accumulator’means any source of electricalenergy generated by direct conversion of chemical energy and consisting of one or more primary battery cells(non-rechargeable)or consisting of one or more secondary battery cells(rechargeable);(2)‘battery pack’means any set of batteries or accumulatorsthat are connected together and/or encapsulated within an outer casing so as to form a complete unit that the end-user is not intended to split up or open;(3)‘portable battery or accumulator’means any battery,button cell,battery pack or accumulator that:(a)is sealed;and(b)can be hand-carried;and(c)is neither an industrial battery or accumulator nor anautomotive battery or accumulator;(4)‘button cell’means any small round portable battery oraccumulator whose diameter is greater than its height and which is used for special purposes such as hearing aids, watches,small portable equipment and back-up power;(1)OJ L269,21.10.2000,p.34.Directive as last amended by Council(6)‘industrial battery or accumulator’means any battery oraccumulator designed for exclusively industrial or profes-sional uses or used in any type of electric vehicle;(7)‘waste battery or accumulator’means any battery or accu-mulator which is waste within the meaning of Article1(1)(a)of Directive2006/12/EC;(8)‘recycling’means the reprocessing in a production processof waste materials for their original purpose or for other purposes,but excluding energy recovery;(9)‘disposal’means any of the applicable operations providedfor in Annex IIA to Directive2006/12/EC;(10)‘treatment’means any activity carried out on wastebatteries and accumulators after they have been handed over to a facility for sorting,preparation for recycling or preparation for disposal;(11)‘appliance’means any electrical or electronic equipment,as defined by Directive2002/96/EC,which is fully or partly powered by batteries or accumulators or is capable of being so;(12)‘producer’means any person in a Member State that,irre-spective of the selling technique used,including by means of distance communication as defined in Directive97/7/ EC of the European Parliament and of the Council of 20May1997on the protection of consumers in respect of distance contracts(1),places batteries or accumulators, including those incorporated into appliances or vehicles, on the market for the first time within the territory of that Member State on a professional basis;(13)‘distributor’means any person that provides batteries andaccumulators on a professional basis to an end-user;(14)‘placing on the market’means supplying or making avail-able,whether in return for payment or free of charge,to a third party within the Community and includes import into the customs territory of the Community;(15)‘economic operators’means any producer,distributor,collector,recycler or other treatment operator;(16)‘cordless power tool’means any hand held appliancepowered by a battery or accumulator and intended for maintenance,construction or gardening activities;(17)‘collection rate’means,for a given Member State in agiven calendar year,the percentage obtained by dividing the weight of waste portable batteries and accumulators collected in accordance with Article8(1)of this Directive or with Directive2002/96/EC in that calendar year by the average weight of portable batteries and accumulators that producers either sell directly to end-users or deliver to third parties in order to sell them to end-users in that Member State during that calendar year and the preceding two calendar years.Article4Prohibitions1.Without prejudice to Directive2000/53/EC,Member States shall prohibit the placing on the market of:(a)all batteries or accumulators,whether or not incorporatedinto appliances,that contain more than0,0005%of mercury by weight;and(b)portable batteries or accumulators,including those incorpo-rated into appliances,that contain more than0,002%of cadmium by weight.2.The prohibition set out in paragraph1(a)shall not apply to button cells with a mercury content of no more than2%by weight.3.The prohibition set out in paragraph1(b)shall not apply to portable batteries and accumulators intended for use in: (a)emergency and alarm systems,including emergencylighting;(b)medical equipment;or(c)cordless power tools.4.The Commission shall review the exemption referred to in paragraph3(c)and submit a report to the European Parlia-ment and to the Council by26September2010,together,if appropriate,with relevant proposals,with a view to the prohi-bition of cadmium in batteries and accumulators.Article5Increased environmental performanceMember States which have manufacturers established on their territory shall promote research and encourage improvements in the overall environmental performance of batteries and accu-mulators throughout their entire life cycle as well as the devel-opment and marketing of batteries and accumulators which contain smaller quantities of dangerous substances or which contain less polluting substances,in particular as substitutes for mercury,cadmium and lead.Article6Placing on the market1.Member States shall not,on the grounds dealt with in this Directive,impede,prohibit,or restrict the placing on the market in their territory of batteries and accumulators that meet the requirements of this Directive.2.Member States shall take the necessary measures toArticle7Overarching objectiveMember States shall,having regard to the environmental impact of transport,take necessary measures to maximise the separate collection of waste batteries and accumulators and to minimise the disposal of batteries and accumulators as mixed municipal waste in order to achieve a high level of recycling for all waste batteries and accumulators.Article8Collection schemes1.Member States shall ensure that appropriate collection schemes are in place for waste portable batteries and accumula-tors.Such schemes:(a)shall enable end-users to discard waste portable batteries oraccumulators at an accessible collection point in their vici-nity,having regard to population density;(b)shall require distributors to take back waste portablebatteries or accumulators at no charge when supplying portable batteries or accumulators,unless an assessment shows that alternative existing schemes are at least as effec-tive in attaining the environmental aims of this Directive.Member States shall make public such assessments;(c)shall not involve any charge to end-users when discardingwaste portable batteries or accumulators,nor any obliga-tion to buy a new battery or accumulator;(d)may be run in conjunction with the schemes referred to inArticle5(2)of Directive2002/96/EC.Collection points set up to comply with point(a)of this para-graph shall not be subject to the registration or permit require-ments of Directive2006/12/EC or Council Directive91/689/ EEC of12December1991on hazardous waste(1).2.Provided that the schemes meet the criteria listed in para-graph1,Member States may:(a)require producers to set up such schemes;(b)require other economic operators to participate in suchschemes;(c)maintain existing schemes.3.Member States shall ensure that producers of industrial batteries and accumulators,or third parties acting on their behalf,shall not refuse to take back waste industrial batteries and accumulators from end-users,regardless of chemical composition and origin.Independent third parties may also collect industrial batteries and accumulators.4.Member States shall ensure that producers of automotive batteries and accumulators,or third parties,set up schemes for the collection of waste automotive batteries and accumulators from end-users or from an accessible collection point in their vicinity,where collection is not carried out under the schemes referred to in Article5(1)of Directive2000/53/EC.In the case of automotive batteries and accumulators from private,non-commercial vehicles,such schemes shall not involve any charge to end-users when discarding waste batteries or accumulators, nor any obligation to buy a new battery or accumulator.Article9Economic instrumentsMember States may use economic instruments to promote the collection of waste batteries and accumulators or to promote the use of batteries and accumulators containing less polluting substances,for instance by adopting differential tax rates.If they do so,they shall notify the measures related to the imple-mentation of those instruments to the Commission.Article10Collection targets1.Member States shall calculate the collection rate for the first time in respect of the fifth full calendar year following the entry into force of this Directive.Without prejudice to Directive2002/96/EC,annual collection and sales figures shall include batteries and accumulators incor-porated into appliances.2.Member States shall achieve the following minimum collection rates:(a)25%by26September2012;(b)45%by26September2016.3.Member States shall monitor collection rates on a yearly basis according to the scheme set out in Annex I.Without prejudice to Regulation(EC)No2150/2002of the European Parliament and of the Council of25November2002on waste statistics(2),Member States shall transmit reports to the Commission within six months of the end of the calendar year concerned.Reports shall indicate how they obtained the data necessary to calculate the collection rate.4.In accordance with the procedure referred to in Article24(2):(a)transitional arrangements may be laid down to addressdifficulties faced by a Member State in satisfying the requirements of paragraph2as a result of specific national circumstances;。
2006-66-EC
歐盟公告新電池指令: 2006/66/EC歐盟委員會已於2006年9月26日正式公告第2006/66/EC號「電池、蓄電池、廢電池及廢蓄電池」指令，並自2008年9月26日起廢止現行之第91/157/EEC號「含有某些危險物質之電池和蓄電池」指令。
此指令主要目的為調和各會員國關於電池、蓄電池、廢電池及廢蓄電池之措施，減少電池、蓄電池、廢電池及廢蓄電池對環境造成的負面衝擊，因而促進地球環境之維護。
為了達成上述目標，此指令提出禁止銷售某些含有危害物質電池之措施，同時也規定會員國應制定回收體系以達成電池回收目標之最高標準。
另外，此指令也規定生產者有關電池標示以及電池易於拆除之設計…等責任。
歐盟各會員國必須於2008 年9月26日以前將此指令轉化為其國內法令。
此指令的重點如下：一、指令目的根據第一條規定，此指令目的在規範並禁止含有危害物質的電池及蓄電池置於市場銷售，並具體訂定收集、處理、回收及處置廢電池及廢蓄電池之相關規範，進而提高廢電池及蓄電池之回收及再利用率。
二、適用範圍根據第二條規定，此指令適用於所有類型的電池及蓄電池，無論其形狀、體積、重量、材質成分或使用。
三、禁止銷售根據第四條規定自2008 年9月26日起，會員國應禁止下列電池置於市場銷售：鎘含量超過0.002 ﹪的攜帶式電池或蓄電池(使用於緊急警報系統、醫療設備以及無線電動工具者除外)；汞含量超過0.0005 ﹪的所有電池或蓄電池(汞含量小於2﹪的鈕扣電池除外)。
四、回收目標根據第十條規定，會員國應於此指令實施後之第5年首次統計廢電池及廢蓄電池之「回收率(collection rate)。
會員國應達成下列「最小回收率」(minimum collection rates)：應於2012年9月26日之前達成25﹪(按當年度回收量除以電池過去三年之平均銷售量計)。
應於2016年9月26日之前達成45﹪。
五、處理與回收根據第十二條規定，會員國應確保於2009年9月26日之前，生產者或第三者應以保護人類健康及地球環境為前提，建立廢電池及廢蓄電池之「處理與回收」(Treatment and Recycling)體系，關於「處理與回收」的規範須符合此指令附件三之規定。
各国电池指令
电池指令电池指令电池由于含铅、镉、汞、酸、碱等污染物质，当其任意丢弃在环境中，随着时间推移外层金属的锈蚀，有害物质就会慢慢地从电池中溢出，进入环境，并通过生物链作用，直接或间接进入人体，并在人体内长期蓄积难以排出，从而损害神经、造血功能、免疫能力下降、肾脏和骨骼受害等。
因此，对废旧电池的收集与处置非常重要，如果处置不当，可能对生态环境和人类健康造成严重危害。
目前，电池潜在的污染已引起社会各界的广泛关注，世界上各国对电池产品采取的态度，除控制有害物质浓度外，主要以回收为主。
当前，越来越多的国家开始行动起来，制定和实施电池有害物质限制、废旧电池回收处理以及再生利用相关的政策和规定。
欧盟电池指令在欧洲，为达到更高的环保水平，欧洲标准化委员会（EC）引用了数项安全指令，加强控制在不同产品中的化学物质含量。
1991年3月18日，欧盟第91/157/EEC号《含有某些危险物质之电池和蓄电池》指令制定完成。
之后，欧盟委员会又于1999年1月5日公布了第98/101/EC号指令，该指令为第91/157/EEC号指令之修订版。
最近，欧盟委员会于2006年9月26日正式公告第2006/66/EC号《电池、蓄电池、废电池及废蓄电池》指令。
规定欧盟各国于2008年9月26日前将本指令转化为各国法律，并自2008年9月26日开始实施并同时废止原有的电池指令（91/157/EEC）及其修订条文（93/86/EEC和98/101/EEC），由单一项指令取代。
2006/66/EC是欧盟将推行一项与电池及蓄电池有关的新指令。
该指令旨在减少有害电池及蓄电池的产量，提高旧电池及蓄电池的回收、处理及循环再造率，以及向消费者提供资讯，鼓励他们购买较长寿和环保的电池。
电池指令与《报废电子电气设备指令》（WEEE）甚为相似，规定生产商须在有关部门登记，分销商有责任回收旧电池，以及每节电池或蓄电池须达到很高的循环再造率等。
此外，该指令要求电器的设计应能令电池易于拆除，以便消费者随时把旧电池交到回收点。
2006-66-EC出新修改指令2008-12-EC
2006/66/EC出新修改指令2008/12/EC
2008/12/EC指令2008年3月11日公布，修订了2006/66/EC电池和蓄电池及电池和蓄电池废弃物指令。
更新替代了原指令中10.4,15.3,17,21.2和24.3章节;更新修正了原指令中12.6章节。
2008/34/EC指令2008年3月11日公布，修订了2002/96/EC（WEEE）电子电气设备废弃物指令。
更新修正了原指令中13，14.3,6.1,7.3章节和附件2。
2008/35/EC指令2008年3月11日公布，修订了2002/95/EC（RoHS）电子电气设备中限制使用特定有害物质指令。
更新修正了原指令中5.1和7章节。
2008/28/EC指令2008年3月11日公布，修订了2005/32/EC（EUP）用能产品生态设计要求框架指令,同时也修订了被委员会视为EUP制行工具的
92/42/EEC,96/57/EC和2000/55/EC指令。
此次修订EUP指令受权委员会采用措施对特定用能产品制定生态设计要求。
欧盟电池环保指令 EU BattEry DirEctivE 200666Ec
the EU’s 2006/66/Ec, a landmark for eco-friendly batteriesBattery products contain pollutants such as lead, cadmium, mercury, acids and alkali, which can be released into the environment when discarded improperly. considering their widespread use, their eventual disposal poses an eminent threat to the ecosystem and the health of people. to counter this, countries have established and implemented strict measures to limit the amount of hazardous substances found in batteries. Linked to battery recycling and reuse initiatives, these have successfully reduced environmental impacts and pushed manufacturers to reconsider the end of life part of their product cycle.tÜv rheinland’s testing services ensure that the batteries you produce or include in your products comply with the EU’s 2006/66/Ec battery directive – the highest standard in the market. Batteries that meet this norm demonstrate conformity with legally accepted thresholds of hazardous substances and match the precise quantified content targets for collection and recycling. Our experts can help harmonise safety and accountability of your batteries through proper labelling that lists provisions for disposal and demonstrates producer responsibility. We contribute to making uninterrupted power supply cleaner.2006/66/EC，电池环保风向标由于电池产品含铅、镉、汞、酸、碱等污染物质，当其任意丢弃在环境中，有害物质就会慢慢溢出，直接或间接对生态环境和人类健康造成严重危害，因此，越来越多的国家制定和实施相关措施限制电池中的有害物质。
电池标准2006-66-EC(中文版)
本指令通过以下内容： 指令确定：
第 1章 主题
(1) 法规重视在市场上流通的电池和蓄电池，尤其是市场上含某些禁止有害物质的电池和 蓄电池；并且一些有关废电池和蓄电池回收、处置、再循环和丢弃的特殊法规补充了 共同体相关法令并促进了废电池和蓄电池的高回收和再循环率。
(2) 指令寻求改进电池和蓄电池以及相关活动者对环境的影响，相关者包括那些与电池和 蓄电池整个生命周期有关的经济参与者，例如，生产商、分销商和最终使用者，尤其 是那些与电池和蓄电池处置和回收直接有关的操作者。
（27） 本指令并不与共同体安全、质量和健康要求相关的法规和共同体废品管理特殊法 规、特别是欧洲议会和理事会于 2000 年 9 月 8 日通过的关于汽车报废的 2000/53/EC 指令和 2002/96/EC 指令相矛盾。
（28） 考虑到生产者责任、电池和蓄电池生产者及生产电池或蓄电池的相关参与者在市场 上所应有的责任，运用适合且灵活的态度并考虑到已存在的方案，尤其是遵从已提 出的 2000/53/EC 和 2002/96/EC 指令来完成一个反应不同内部环境的经费负担方案 以避免双年 1 月 25 日通过的关于共同体抗击镉对环境污染的行动程序决 议中强调对镉的限制是在没有更好选择、并且电池中所含镉是作为保护人类健康和 环境利益的镉控制政策中收集和循环的主要元素的情况下使用。
（4）
理事会在 1991 年 3 月 18 日通过的关于电池和蓄电池中含有某些危险物质 91/157/EEC 要求各成员国在该领域实施相似的法律。尽管如此，该指令的目的并未 完全达到。欧洲议会和理事会 1600/2002/EC 指令、理事会于 2002 年 7 月 22 日通过 的《第六环境行动指南》、欧洲议会 2002/96/EC 指令、理事会于 2003 年 1 月 27 日 通过的《关于废弃电子电气设备》（WEEE）等指令也是根据需要在 91/157/EEC 基
Battery电池指令检测
Battery 电池指令检测-指令2006/66/EC 检测要求
1. 电池中汞(Hg)、镉(Cd)、铅(Pb)元素的使用受到高度关注：
- 纽扣电池中汞(Hg)的含量不超过2%，其他电池中汞(Hg)不超过0.0005%； - 电池中镉(Cd)的含量不超过0.002%；
- 上述限量要求不适用于以下四类用途的电池：
- 报警或应急系统(含应急灯)中的电池；
- 医疗设备中使用的电池；
- 无绳电动工具中的电池(直到2010年9月再重新评估该豁免项)； - 用于军事、国家安全或将被发射入太空的专用电池； 2. 电池的标识
- 表明电池需分类回收的带叉垃圾桶标志；
- 汞(Hg)的含量超过0.0005%、镉(Cd)的含量超过0.002%以及铅(Pb)的含量超过0.004%的电池需在垃圾桶标志下方注明对应元素符号及其含量
- 电池类型、安全的安装及拆解方法说明
3. 电池回收
- 回收前处理最少包括去掉电池中所含有的任何液体或酸性物质
- 回收率需满足要求：65%--铅酸废电池；75%--镍镉废电池；50%--其他废旧电池；
注：电池类产品如果符合了电池指令，则不需重复符合RoHS 指令(附图：电池垃圾桶标志
)。
最新电池指令解读
欧盟电池回收组织CROs
EPBA Model of compliance organisation
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新电池及蓄电池指令－处理
成员国应确保生产商所设计的设备中废弃电池和蓄电池能够以较容 易的方式拆解； 在2009年9月26日之前确保: A) 生产者或第三方团体应用最佳可行技术处理及循环再用废气电池 及蓄电池； B)所有电池及蓄电池的处理及循环再用都必须符合法律法规对人体 健康、环境安全、废弃物处理的最低要求； 成员国应禁止以填埋或者焚烧方式处理废弃工业及自动式电池和蓄电 池。
贮备电池是为了使电池有较长的贮 存期，贮存时将电池的其它部分与 电解质分别贮存，使用时再注入电 解质活化，通常应用于军事等特殊 场合。如：镁－氯化银电池又称海 水激活电池等。
10
常用电池分类
型号
普 R03
通 锌
R1
锰 R6
电 池 R10
R14
R20
R40
碱 LR03
性
锌 LR6
锰 电
LR14
池 LR20
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新电池及蓄电池指令－回收目标
在不损害2002/96/EC(WEEE)指令前提下,达到以下最 少回收率：achieve the following minimum collection rate收集率： (a) 25% by 26 September 2012； (b) 45% by 26 September 2016； 根据指令附件I，各成员国应监控年回收率； 各国根据本国国情指定合适的回收率； 在2007年9月26日前制定计算年销售电池及蓄电池回 收率通用方法；
25
电池指令限值比较
Battery Directive 91/157/EC
电池指令中文版
欧盟电池指令2006/66/EC欧盟电池指令2006/66/EC欧盟委员会于2006年9月26日发布新的电池和蓄电池指令2006/66/EC ，该指令将取代原电池指令91/157/EEC和98/101/EC。
该指令将于2008年9月26 日执行限制。
指令适用范围包括电池组、便携式电池、汽车电池和工业电池等。
新指令的主要内容：电池及电池组的定义；修改了电池中汞和镉的使用限量；电池的标签要求，对消费者的选购和回收提供帮助；修改了铅、汞和镉含量的标签要求；确定了废弃便携电池的回收率目标；禁止对工业用和汽车用废弃电池进行掩埋或焚化；增加“生产商责任”的规定；电池必须可以从产品上移除(由于安全、性能、医疗或数据完整性原因必须永久连接电池的除外)；从2009年9月26日起，便携和汽车电池应在标签上注明容量。
欧盟委员会正在制定有关容量标签体系的规定；生产商(包括销售带电池和蓄电池的产品的生产商)需要在每个成员国家进行注册。
2006/66/EC对电池、电池组和便携式电池的定义：电池(battery)是指任何由一个或多个初级电池（primary battery cells，不可再充电）组成的将化学能直接转化为电能的装置；蓄电池(accumulator)是指由一个或多个次级电池（secondary battery cells，可再充电）组成的将化学能直接转化为电能的装置。
电池组(battery pack)是指由多个电池或蓄电池互相连接和/或压缩于外壳中形成的完整单元，并且此单元在最终使用时无需分离或打开。
便携式电池或蓄电池(portable battery or accumulator)是指同时符合如下三个条件的任何电池(battery)、钮扣电池(button cell)、电池组(battery pack)和蓄电池(accumulator)：1,被封装的；2,可以用手携带的；3,既不是工业电池或蓄电池，也不是汽车电池或蓄电池。
电池指令(2006_66_EC)
a). 镍镉电池及蓄电池(nickel-cadmium batteries and accumulators)应达成 75﹪(按平均重量计)。 b). 铅酸电池及蓄电池 (lead-acid batteries and accumulators) 应达成 65﹪。 c). 其它废电池及蓄电池 (other waste batteries and accumulators) 应达成 50﹪。
b). 成员国应确保所有电池及蓄电池自 2009 年 9 月 26 日起提供易于辨识的「容量」标示。 c). 镉含量超过 0.002﹪, 铅含量超过 0.004﹪及汞含量超过 0.0005﹪的电池, 蓄电池及钮扣电池应标示重金属的 化学符号：Cd, Pb or Hg。化学符号应印刷于画叉垃圾桶标签下方, 见下图 B。
此指令主要目的为调和各成员国关于电池、蓄电池、废电池及废蓄电池的措施，减少电池、蓄电池、废电池及 废蓄电池对环境造成的负面冲击，因而促进地球环境的维护。为了达成上述目标，此指令提出禁止销售某些含 有危害物质电池的措施，同时也规定成员国应制定回收体系以达成电池回收目标的最高标准。
另外，此指令也规定生产者有关电池标示以及电池易于拆除的设计…等责任。 欧盟各成员国必须于 2008 年 9 月 26 日以前将此指令转化为其国内法令。
2. 生效日期 此指令 2006/66/EC 自刊登于欧盟官方公报(2006 年 9 月 26 日)之日起正式生效。
3. 指令的主要内容 3.1 目的 规范并禁止含有危害物质的电池及蓄电池置于市场销售，并具体订定收集、处理、回收及处置废电池及废蓄电 池的相关规范，进而提高废电池及蓄电池的回收及再利用率。
3.6 处理与回收 成员国应确保于 2009 年 9 月 26 日的前，生产者或第三者应以保护人类健康及地球环境为前提，建立废电池及 废蓄电池的「处理与回收」(Treatment and Recycling)体系。另外，依照电池分类而言，成员国应于 2010 年 9 月 26 日的前达成下列各种类电池的「最小回收率」(minimum recycling efficiencies)：
欧盟电池指令2006-66-EC中英对照
欧盟电池RoHS指令2008年9月26日，欧盟电池指令91/157/EEC被替代，新指令2006/66/EC开始生效。
此后，欧盟市场内的全部电池玩具均需参照新指令。
2006/66/EC指令适用于包括除军用，医用和电力工具外的所有其他类型的电池和蓄电池（AA, AAA, 纽扣型电池，铅酸蓄电池，可充电蓄电池），并制定了电池收集、处理、回收和废弃的条例，旨在限制某些有害物质和改善电池在供应链中所有操作环节的环境表现。
禁止：禁止使用含有下述物质的电池或蓄电池（包括那些已经安装在器具中的）：-纽扣电池汞含量超过２％，其他电池汞含量超过0.0005%（按重量计算）。
-镉含量超过0.002％（按重量计算）。
标签：1.所有电池，蓄电池和电池组上需标有带十字叉的带轮垃圾桶；2.2009年9月26日前所有便携电池、汽车电池和蓄电池均需标示出其容量； .3. 汞含量和镉含量超标或铅含量超过0.004%的电池，蓄电池和纽扣电池必须标有带十字叉的带轮垃圾桶标志以及相关的金属化学符号标志（Hg, Cd, 或Pb）。
重金属标志标示在带轮垃圾桶图案下方，并占据整个图案至少1/4的面积；4.带轮垃圾桶图案应最少占电池，蓄电池或电池组最大面面积的3％，最大不超过5 x 5 cm。
若是圆柱形电池，图案应最少占电池，蓄电池或电池组表面积的1.5％，最大不超过5 x 5 cm 。
5. 若电池，蓄电池或电池组上的标志大小只能小于0.5 x 0.5 cm，则可以不标记，但必须在包装上打印标志，且大小不得小于1 x 1 cm；6. 所有标志必须打印清晰易见且不易磨损。
.说明：所有电池上都必须附有丢弃说明（可以打印在玩具或进口物品的说明书上）和供参考的图例，包括以下要素：ａ对环境和人类健康存在潜在影响的物质；ｂ不得与生活垃圾一同丢弃；ｃ收集和回收计划详情；ｄ消费者在垃圾回收中的责任；e 十字叉带轮垃圾桶标志和化学标志Hg, Cd和Pb的含义。
欧盟ROHS环保标准--关于2006-66-EC号电池指令
欧盟ROHS环保标准--关于2006/66/EC号电池指令关于2006/66/EC号电池指令欧洲在2003年相继出台了RoHS和WEEE指令，令各国特别是国内的电器生产厂商哗然，奔波于两个指令之间。
而同样是“电”字开头的电池则有专门的电池指令——91/157/EEC，93/86/EEC和98/101/EC。
近年来，电池指令的发展迅速。
1991年3月18日，欧盟第91/157/EEC号[含有某些危险物质之电池和蓄电池]指令制定完成。
之后，欧盟委员会又于1999年1月5日公布了第98/101/EC号指令，该指令为第91/157/EEC号指令之修订版。
最近，欧盟委员会于2006年9月26日正式公告第2006/66/EC号[电池、蓄电池、废电池及废蓄电池]指令，并自2008年9月26日起废止现行之第91/157/EEC号[含有某些危险物质之电池和蓄电池]指令。
“回收令”令广大电池企业陷入尴尬1991年3月18日，欧盟发布91/157/EEC号电池指令该指令称，含汞量超过0.0005%、含镉量超过0.002%的电池，将在欧盟境内都将被禁止销售。
此外，欧盟将从2008年开始强制回收废旧电池，回收费用则由生产厂家来负担。
从2009年开始，所有在欧盟境内销售的电池都必须标明具体使用寿命。
2012年之前，欧盟境内1／4的废旧电池须被回收。
到2016年时，这一比例应达到45%。
目前，欧盟此项指令已获欧盟理事会与欧洲议会批准，即将成为欧盟法律。
在成为欧盟法律之后，各欧盟成员国将在两年内通过相关国内法律与之相适应。
欧盟指出，实施该草案的目的是为了保护环境，防止废电池中镉等金属污染。
实际上，早在2002年，欧委会就颁布2002/525/EC号决定，规定自今年1月1日起停止出售含金属镉的电动汽车用电池。
此外，今年7月1日起，欧盟《关于在电子电气设备禁止使用某些有害物质指令》(RoHS)有将开始实施，指令规定投放于市场的新电子和电气设备不得包含铅、汞、镉、六价铬、聚溴二苯醚和聚溴联苯。
2006-66-EC 电池与蓄电池指令
SPARKLE Volume 390 / 28 July 2008Batteries and Accumulators Directive 2006/66/EC電池和蓄電池-2006/66/EC指令The new Batteries and Accumulators Directive 2006/66/EC becomes effective on September 26, 2008, and applies to battery packs, portable batteries , automotive and industrial batteries.針對電池和蓄電池新的指令2006/66/EC自2008/9/26生效，適用於電池組、便攜電池、機動和工業電池。
Highlights of the new Directive:新指令最顯著(重要)部分：1. Revised restrictions on the use of mercury and cadmium in batteries;修正電池使用汞和鎘的限制；2. Labelling requirements for new batteries to aid consumer choice and recycling;電池新的標簽要求：為幫助顧客選擇和循環利用；3. Revised labelling requirements for lead, mercury and cadmium content;修正含鉛、汞、鎘的標簽要求；4. Collection rate targets for waste portable batteries;收集消耗便攜電池的目標比率；5. Prohibition on landfill disposal or incineration of waste industrial and automotive batteries;禁止用垃圾掩埋法處理和焚燒機動和工業電池；6. Introduction of "producer responsibility" obligations;生產商責任義務介紹；7. Battery must be removable from products (except where a permanent connection to the battery is required for safety, performance, medical or data integrity reasons);電池必須可以從產品上取出(除了因電池安全、性能、醫學或數據完整性的要求而需永久連接)；8. From September 26, 2009, portable and automotive batteries shall be labelled with their capacity. The EU Commission is developing the rules for the capacity labelling system.自2009/9/26便攜電池與機動電池要求貼上它們的容量標簽。
2006-66-EC 电池与蓄电池指令
SPARKLE Volume 390 / 28 July 2008Batteries and Accumulators Directive 2006/66/EC電池和蓄電池-2006/66/EC指令The new Batteries and Accumulators Directive 2006/66/EC becomes effective on September 26, 2008, and applies to battery packs, portable batteries , automotive and industrial batteries.針對電池和蓄電池新的指令2006/66/EC自2008/9/26生效，適用於電池組、便攜電池、機動和工業電池。
Highlights of the new Directive:新指令最顯著(重要)部分：1. Revised restrictions on the use of mercury and cadmium in batteries;修正電池使用汞和鎘的限制；2. Labelling requirements for new batteries to aid consumer choice and recycling;電池新的標簽要求：為幫助顧客選擇和循環利用；3. Revised labelling requirements for lead, mercury and cadmium content;修正含鉛、汞、鎘的標簽要求；4. Collection rate targets for waste portable batteries;收集消耗便攜電池的目標比率；5. Prohibition on landfill disposal or incineration of waste industrial and automotive batteries;禁止用垃圾掩埋法處理和焚燒機動和工業電池；6. Introduction of "producer responsibility" obligations;生產商責任義務介紹；7. Battery must be removable from products (except where a permanent connection to the battery is required for safety, performance, medical or data integrity reasons);電池必須可以從產品上取出(除了因電池安全、性能、醫學或數據完整性的要求而需永久連接)；8. From September 26, 2009, portable and automotive batteries shall be labelled with their capacity. The EU Commission is developing the rules for the capacity labelling system.自2009/9/26便攜電池與機動電池要求貼上它們的容量標簽。
电池指令_2006-66-EC
Guidelines to EnvironmentalBattery Marking in the European Union−These guidelines are intended as a tool to aid thebattery industry with certain marking requirements inthe new battery Directive No. 2006/66/EC whichMember States are required to transpose into nationallaw by 26 September 2008.− All batteries are required to be marked, either on thebattery or its packaging depending on size, with theseparate collection symbol.− Batteries containing mercury, cadmium and lead arealso required to be marked with their chemicalsymbol(s).− The producer placing batteries on the market isresponsible for fulfilling the marking requirements inaccordance to the provisions of the Battery Directive.April 2008DisclaimerThis document is intended to provide guidance on the marking requirements as foreseen by art.21 of the Battery Directive. The document is not a legally binding interpretation of the Battery Directive, and should therefore not be relied upon as legal advice. This document can be updated at any time without prior notice.1. LEGAL REQUIREMENTS1.1 IntroductionDirective 2006/66/EC on batteries and accumulators and waste batteries and accumulators requires that all types of waste batteries and accumulators should be separately collected for recycling and that consumers should be informed about the heavy metals they contain.NB: The term battery, or batteries, used in this document means single cells or battery packs used as individual units.1.2 Batteries Covered by the EU Directive1.2.1 SymbolsAll batteries, accumulators and battery packs are required to be marked with the separate collection symbol (crossed-out wheeled bin) either on the battery or its packaging depending on size.In addition batteries, accumulators, battery packs and button cells should include the chemical symbol Hg when containing more than 0,0005% mercury, the chemical symbol Cd when containing more than 0,002% cadmium, the chemical symbol Pb when containing more than 0,004% lead. If the content is higher for more than one of the substances in question, all relevant chemical symbols have to be placed.The symbols can be placed on the existing colour background as long as they are visible, legible and indelible. The symbols can be attached as labels, by durable printing, or as a surface profile, either indented or as relief.1.3 Marking Dimensions – Separate Collection Symbol1.3.1 On BatteriesPrismatic shapes: The symbol; shall cover at least 3% of the area of the largest side of the battery, accumulator or battery pack, up to a maximum size of 5x5 cm. The symbol may be marked on any side.Cylindrical shapes: The symbol shall cover at least 1.5% of the battery surface area to amaximum of 5cm x 5cm.1.3.2 On PackagingWhere the size of the battery, accumulator or battery pack is such that the symbol would be smaller than 0.5cm x 0.5cm, the battery, accumulator or battery pack need not be marked but a symbol measuring 1cm x 1 cm shall be printed on the consumer packaging.1.4 Marking Dimensions – Chemical SymbolIrrespective of whether the separate collection symbol is on the product or on the packaging, the chemical symbol Cd, Hg or Pb must be placed beneath the separate collection symbol and be at least one quarter of the area of that symbol.Detailed dimensions of the symbols are available in the annex.2. INDUSTRY STANDARDS2.1 IntroductionThe following recommendations have been developed by the EPBA in cooperation with RECHARGE and EICTA to promote a standardised approach on marking related issues that are not clearly defined in Directive 2006/66/EC. Use of these standards are therefore entirely voluntary and at the discretion of the “producer”.2.2 Multiple Chemical SymbolsIn those cases where it is necessary to include more than one chemical symbol the format should be as indicated below. Dimensions of the separate collection symbol and the chemical symbols as required by the Directive should be followed.(Not to scale)Cells2.3 ButtonThe dimensions of a very limited number of button cell batteries are such that the separate collection symbol should be marked on the cell according to a strict reading of the Directive’s marking requirements in Art. 21.4.However this is not an effective method for informing consumers about separate collection for the following reasons:a. Button cells do not have a label on which the symbol could be printed sinceboth its ends are designed to act as electrical contacts. Application of anysubstances such as inks, etc could insulate the contact between the batteryand the appliance into which it is placed causing malfunction. As a result thesymbol would have to be engraved into the metal and this would not be easilyvisible to the consumer and be contrary to Art. 21.6 of the Directive.b. According to the IEC standards button cells should display the followinginformation on cell because of safety, performance and product liabilityissues:polarity "+" and "-" symbols (safety),chemistry and voltage (performance/fit for purpose),brand name (product liability).As a result the available space for the separate collection symbol is restricted. Placing the separate collection symbol, measuring 1cm x 1cm, on the packaging of all button cells will provide consumers with information about their proper disposal visibly, legibly and indelibly.Packs2.4 BatteryDirective 2006/66 defines ‘battery pack’ as “any set of batteries or accumulators that are connected together and/or encapsulated within an outer casing so as to form a complete unit that the end user is not intended to split up or open.”Art. 21.1 includes battery packs together with batteries and accumulators that have to be appropriately marked with the separate collection symbol. Since end users are not intended to come into contact with batteries inside a pack it is not necessary to place the separate collection mark upon them but instead to mark the pack according to the Directive’s requirements noted in section 1 above.2.5 Qualification of Separate Collection SymbolThe following recommendations have been developed for those producers wishing to advise non-EU markets that the separate collection symbol is relevant in the EU only.Location of the qualifier should be outside the boundaries of the symbol.Preferably the qualifier should be on top of the symbol. It should not be below because Directive 2006/66 reserves that space for chemical symbols.The qualifier could be used with the symbol either on battery label or on the battery’s packaging.The recommended qualifier is EU as shown in the following illustration:2.6 Batteries Incorporated into AppliancesArt. 11 of Directive 2006/66 requires that “manufacturers design appliances in such a way that waste batteries and accumulators can be readily removed.” However this requirement does not apply where “for safety, performance, medical or data integrity reasons, continuity of power supply is necessary and requires a permanent connection between the appliance and the battery or accumulator.” Finally the Directive requires “appliances into which batteries and accumulators are incorporated shall be accompanied by instructions showing how they can be removed safely.”2.6.1 Applications Exempted from Ready RemovabilityBatteries incorporated into appliances that are exempted from “readily removed” requirement of the Directive for safety, performance, medical or data integrity reasons, need not be marked with the separate collection and chemical symbols since end users are not expected to dispose of the battery separately from the appliance. Such batteries would be separated from the appliance during the treatment phase of the appliance as required under the WEEE Directive. In particular, this exemption should apply to button cells, memory back-up batteries and battery packs when those batteries/packs are supplied embedded (*) in the equipment.(*) where embedded means “not intended for replacement by the end user”.2.6.2 Applications Designed for Ready RemovabilityMarking of the separate collection and chemical symbols for batteries and accumulators that can be “readily removed” shall be as follows:•Where the size of the battery or accumulator is such that following the symbol size conditions noted under 1.3.1 above the symbol would not be smaller than 0.5 cm x0.5 cm, symbol(s) should be placed on the battery or accumulator.•Where the size of the battery or accumulator is such that the symbol would be smaller than 0.5cm x 0.5cm, the battery or accumulator should not be marked but a symbol measuring 1cm x 1 cm shall be printed either: 1) on the packaging of the appliance; 2) inside the instructions/manual.2.6.3 Instructions for Ready RemovabilityThe Directive requires that instructions for safe removal of batteries should be incorporated within its instructions for use. Instructions may be made available to the consumer on a separate leaflet or printed on the packaging.For further general information on marking guidelines, please contact:EPBA204, avenue Marcel Thiry1200 BrusselsBelgiumTel no +32/2 774 96 02Fax no +32/2 774 96 90Email: epba@RECHARGE aisblAve. de Tervueren, 168 B-3.B-1150 Brussels.Belgium.Tel. + 32 2 777 05 60Fax + 32 2 777 05 65E-mail : jpwiaux@ANNEXMARKING DIMENSIONS ACCOR ES FORSPECIFIC BATTERY SIZESThe following table has bee √A a = nominal symbol dimension ry curved surface eparate collection marking without chemical symbolDING TO EN 61429 AND EXAMPL n derived using formula: a ≥ 0.12 A = half batte area (cylindrical) or area of largest side (prismatic)SSeparate collection marking with chemical symbol。
2006-66-EC电池指令
2006-66-EC 電池指令(中文)歐洲議會和歐盟理事會2006 年9 月2 日第2006/66/EC 號關於電池及蓄電池、廢棄電池及蓄電池以及廢止91/157/EEC 的指令歐洲議會和歐盟理事會注意到建立歐洲共同體條約，特別是其中第175（1）條和第95（1）條，注意到歐盟委員會的提案，注意到歐洲經濟社會委員會的提案，注意到歐盟地區委員會的意見，按照歐洲共同體條約第251 條所制定的程式以及協調委員會2006 年6 月22 日通過的聯合文本，鑒於：(1) 協調各國家跟電池及蓄電池、廢棄電池及蓄電池有關的措施是有利的。
這個指令的主要目的是將電池及蓄電池、廢棄電池及蓄電池對環境的影響減到最少，從而對保護、保存和改善環境指令做出貢獻。
立法依據是歐洲共同體條約第175（1）條。
然而，採取基於第95（1）條來協調與重金屬含量及電池及蓄電池標識有關的措施也是合適的，目的是確保在歐洲共同體內部市場順利實施，並避免內部的不正當競爭。
(2) 歐盟理事會通訊於1996 年7 月30 公佈的關於歐洲共同體廢棄物處理策略綜述為歐洲共同體未來的廢棄物政策確立了指導方針。
通訊強調了減少廢棄物中有害物質含量的必要性，指出在整個歐洲共同體範圍內在產品及產品製造過程中限制使用這些有害物質規則的潛在好處。
通訊還說明既然廢棄物的產生是不能避免的，那麼廢棄物應該在材料或能源上迴圈再利用。
(3) 歐洲議會1988 年1 月25 日決議關於歐洲共同體抗擊由鎘引起的環境污染行動計畫強調，為了保護人類健康和環境，鎘控制的策略是限制鎘的使用場合和收集、回收含鎘電池。
(4) 歐洲議會1991 年3 月18 日第91/157/EEC 號關於含有某些有害物質的電池及蓄電池指令使一些成員國在這個領域制定了一些法律。
然而，指令的一些目的沒有完全達到。
第1600/2002/EC 號制定的第六個歐洲共同體環境行動計畫決議和第2002/96/EC 號關於電子電氣設備廢棄指令（WEEE）也強調91/157/EEC 指令需要修改。
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(10) 便携式电池及蓄电池是指密封的、普通人能轻易携带的、既不是自动式也不是工业用的电池及蓄 电池，包括干电池（如 AA 和 AAA 电池），用于移动电话、便携式电脑、无线电动工具、玩具及家用 器具（如电动牙刷、刮胡刀、手持式吸尘器）的电池及蓄电池，以及任何消费者用于一般家用器具的电 池及蓄电池。 (11) 欧盟委员会应根据现有科学技术的发展评估修改本指令的必要。尤其是，欧盟委员会应评议用于 无线电动工具的便携式电池及蓄电池的镉豁免条例。无线电动工具是指用于旋转、研磨、打磨、碾碎、 锯、切、剪、钻、打洞、冲击、锤打、铆接、螺旋、抛光或在木材、金属和其他材料上进行相似的过程 的工具，还有割草、挖掘等其他园艺活动用工具。 (12) 欧盟委员会还应监控提高电池及蓄电池生命周期环境表现的科技发展，包括通过参与欧洲共同体 生态管理及审查计划（EMAS），成员国也应鼓励上述行为。 (13) 为了保护环境，废弃电池及蓄电池应被回收。对于便携式电池及蓄电池应该建立高回收率的回收 计划。这意味着应该制定这样回收计划以至最终用户可以方便、免费的丢弃所有的废旧电池及蓄电池。 不同的回收计划和资金安排适用于不同的电池及蓄电池。 (14) 成员国达到废弃电池及蓄电池的高回收率是有利的，这样可以使整个欧洲共同体达到高水平的环 境保护和材料循环再利用。因此本指令应为成员国设置最低的回收及循环再利用目标。基于前一年的年 度平均销售额来计算回收率是可行的，这样可以在所有成员国之间根据电池及蓄电池消费比例形成可以 比较的目标。 (15) 针对含镉和含铅电池及蓄电池应建立特殊的循环再利用要求，目的是使整个欧洲共同体达到高水 平的材料循环再利用，并防止各成员国之间形成差异。 (16) 所有利益相关方都应能参与回收、处理及循环再利用计划。这些计划在制定时应避免对进口电池 及蓄电池、电池贸易造成歧视或形成不平等竞争。 (17) 回收及循环再利用计划应达到最优化，特别是为了将费用及运输过程对环境造成的负面影响减到 最少。处理及循环再利用计划应使用最佳的技术，如 1996 年 9 月 24 日第 96/61/EC 号关于综合污染防 止和控制指令所述。循环再利用的定义应排除能量回收。能量回收的概念在别的欧洲共同体规则中已经 定义了。 (18) 电池及蓄电池应能通过国家电池回收计划或者与废弃电子电气设备一起通过基于第 2002/96/EC 号 指令建立的国家回收计划被单独回收。对于后种情形，作为一个强制性的最低处理要求，回收时电池及 蓄电池必须跟废弃电子电气设备分开。跟废弃电子电气设备分开后，电池及蓄电池必须满足本指令的要 求，特别是它们要满足回收目标和循环再利用要求。 (19)废弃电池及蓄电池管理资金的基本原则应建立在欧洲共同体水平。资金计划应帮助达到高回收率和 循环再利用率，并应使生产者责任的原则生效。本指令定义的所有的生产者应该注册。生产者应对回收、 处理及循环再利用所有回收的电池及蓄电池这个过程付费，当然还要减去出售再利用材料所得的费用。 然而在某些情况下，应用于小的生产者的上述规则应能被证明是正当的。 (20) 为了成功回收，分别回收的好处、可取的回收计划和最终用户在废弃电池及蓄电池管理中的作用 等信息和规定必须提供给最终用户。应对标识系统进行这样的细节安排，以使之提供给最终用户透明、 可靠、清晰的关于电池及蓄电池的信息，包括它们含有哪些重金属。 (21) 为了要达到本指令的目的，尤其是要达到高的分别回收率及循环再利用率，成员国如果使用了经 济手段，例如采用微分税率，他们应该相应的知会欧盟委员会。 (22) 关于电池及蓄电池投放市场、回收及循环再利用的数量，这些可靠的和可比较的数据必须要监控， 以查明本指令的目的是否达到。 (23) 成员国应设置适用于违反本指令规定的关于处罚的规则，以确保规定被贯彻。这些处罚措施必须
2006-66-EC 电池指令(中文)
欧洲议会和欧盟理事会 2006 年 9 月 2 日第 2006/66/EC 号关于电池及蓄电池、废弃电池及蓄电池以及废 止 91/157/EEC 的指令 欧洲议会和欧盟理事会注意到建立欧洲共同体条约，特别是其中第 175（1）条和第 95（1）条，注意到 欧盟委员会的提案，注意到欧洲经济社会委员会的提案，注意到欧盟地区委员会的意见，按照欧洲共同 体条约第 251 条所制定的程序以及协调委员会 2006 年 6 月 22 日通过的联合文本，鉴于： (1) 协调各国家跟电池及蓄电池、废弃电池及蓄电池有关的措施是有利的。这个指令的主要目的是将电 池及蓄电池、废弃电池及蓄电池对环境的影响减到最少，从而对保护、保存和改善环境指令做出贡献。 立法依据是欧洲共同体条约第 175（1）条。然而，采取基于第 95（1）条来协调与重金属含量及电池及 蓄电池标识有关的措施也是合适的，目的是确保在欧洲共同体内部市场顺利实施，并避免内部的不正当 竞争。 (2) 欧盟理事会通讯于 1996 年 7 月 30 公布的关于欧洲共同体废弃物处理策略综述为欧洲共同体未来的 废弃物政策确立了指导方针。通讯强调了减少废弃物中有害物质含量的必要性，指出在整个欧洲共同体 范围内在产品及产品制造过程中限制使用这些有害物质规则的潜在好处。通讯还说明既然废弃物的产生 是不能避免的，那么废弃物应该在材料或能源上循环再利用。 (3) 欧洲议会 1988 年 1 月 25 日决议关于欧洲共同体抗击由镉引起的环境污染行动计划强调，为了保护 人类健康和环境，镉控制的策略是限制镉的使用场合和收集、回收含镉电池。 (4) 欧洲议会 1991 年 3 月 18 日第 91/157/EEC 号关于含有某些有害物质的电池及蓄电池指令使一些成 员国在这个领域制定了一些法律。然而，指令的一些目的没有完全达到。第 1600/2002/EC 号制定的第 六个欧洲共同体环境行动计划决议和第 2002/96/EC 号关于电子电气设备废弃指令（WEEE）也强调 91/157/EEC 指令需要修改。因此为了指令的清晰性，91/157/EEC 指令需要被修改和替换。 (5) 为了达到环境方面的目标，本指令禁止某些含有汞和镉的电池及蓄电池投放于市场。本指令提高了 废弃电池及蓄电池回收及循环再利用的水平，还提升了涉及电池及蓄电池生命周期各操作者的环境方面 的表现，例如生产者、经销商、使用者，特别是涉及直接处理和循环再利用废弃电池与废弃蓄电池的操 作者。这些特殊规则是对欧洲共同体目前存在的关于废弃物立法的补充，特别是第 2006/12/EC 号指令、 第 1999/31/EC 号指令和第 2000/76/EC 号指令。 (6) 为了制止废弃电池及蓄电池被随意丢弃而导致污染环境，以及避免使用者对不同电池及蓄电池的不 同废弃处理产生混乱，本指令应适用于所有投放于欧洲共同体的电池及蓄电池。如此广泛的范围应能确 保经济的回收及循环再利用，以及最佳的能源节省。 (7) 可靠的电池及蓄电池是许多产品、设备和服务安全的基本要求，还是我们社会的必要能量来源。 (8) 需要分辨便携式电池及蓄电池与工业用、自动式电池及蓄电池之间的区别。要禁止随意丢弃及掩埋 工业用、汽车用电池及蓄电池。 (9) 工业用、自动式电池及蓄电池的例子包括用于医院、机场或办公场所应急或储备的电力供应用电池 及蓄电池，用于火车、飞机上的电池及蓄电池，用于油井钻探和灯塔的电池及蓄电池。还有商店、宾馆 的手持式付帐刷卡机、商店的条形码识别器、电视台和职业摄影场所的专业视频设备、专业采矿和潜水 头盔上的采矿照明灯和潜水灯等专用电池及蓄电池，为防止封闭和夹伤人群的电动门备用电池及蓄电 池，用于仪器使用和不同测量设备和仪器仪表的电池及蓄电池，以及用于连接太阳能、光伏及其他新能 源设备的电池及蓄电池。工业用电池及蓄电池还包括用于用电的交通设备，如电车、电动轮椅、电动自 行车、飞机和自动运输等设备上的电池及蓄电池。除此之外，任何未经密封的和非自动氏的电池及蓄电 池都应被视为工业用电池。
充电的），或包含一个或多个二级电池单元（Байду номын сангаас充电的）； (2) “电池组”是指任何经外包装连接和（或）封装以形成一个完整单元的套装电池或蓄电池，使得最 终用户不会轻易打开或拆开； (3) “便携式电池或蓄电池”是指任何封装好的、能用手携带的、非工业用或自动式的普通电池、钮扣 电池、电池组或蓄电池； (4) “钮扣电池”是指任何小的、圆形的、直径比高度更大，用于助听器、手表、小型便携式设备和备 份电源等特殊用途的便携式电池或蓄电池； (5) “汽车电池或蓄电池”是指任何用于汽车发动器、照明或点火能源的电池或蓄电池； (6) “工业用电池或蓄电池”是指任何专门为工业或专业用途设计的电池或蓄电池，或用于任何电动交 通工具的电池或蓄电池； (7) “废弃电池或蓄电池”是指任何在第 2006/12/EC 号指令第 1 条(a)范围内被废弃的电池或蓄电池； (8) “循环再利用”是指废弃材料处于原来目的或其他目的的产品再生产过程，但不包括能量再生； (9) “处置”是指第 2006/12/EC 号指令附录 IIA 中提供的任何适当的操作； (10) “处理”是指当电池及蓄电池被送往拣选、准备循环再利用或准备处置等机构后，对被废弃物进 行的任何活动； (11) “器具”是指第 2002/96/EC 号指令定义的、由或可以由电池或蓄电池提供能量任何电子或电气设 备； (12) “生产者”是指任何从事在成员国范围内第一次将电池或蓄电池投放于市场的职业人员，不考虑 出售技术者，但包括通过欧洲议会和欧盟理事会 1997 年 5 月 20 日第 97/7/EC 号关于在远距离通讯中保 护消费者契约指令定义的远距离通讯用的电池及蓄电池，包括那些放在器具及交通工具中的电池及蓄电 池； (13) “经销商”是指任何从事提供电池及蓄电池给最终用户的职业人员； (14) “投放市场”是指在共同体范围内包括从共同体海关进口以供给第三方或使之可获得，不管是付 费还是免费的行为； (15) “商业经营者”是指任何生产者、经销商、回收方、循环再利用方或其他处理操作者； (16) “无线电动工具”是指任何由电池或蓄电池提供能量的和为了维修、建筑或园艺行为的手持器具； (17) “回收率”是指某一成员国在一年内通过将根据本指令第 8 条及第 2002/96/EC 号指令回收的废弃 便携式电池及蓄电池重量除以该成员国该年生产者直接销售给最终用户或由第三方销售给最终用户的 便携式电池及蓄电池平均重量（取两年的平均值）获得的百分数。 第4条 禁止 1. 成员国应禁止以下的产品投放于市场： (a) 含汞量超过 0.0005%（重量百分比）所有的电池及蓄电池，不管是否与设备配套使用；还有 (b) 含镉量超过 0.002%（重量百分比）的便携式电池及蓄电池，包括与设备配套使用的产品。 2. 段落 1(a)的禁令不适用于含汞量不超过 2%（重量百分比）的钮扣电池。 3. 段落 1(b)的禁令不适用于用于以下用途的便携式电池及蓄电池： (a) 紧急系统和警报系统，包括紧急照明；或 (b) 医疗设备；或 (c) 无线电动工具。 4. 欧盟委员会应审视段落 3(c)中所指的豁免，并于 2010 年 9 月 26 日提交一份报告给欧洲议会和欧盟 理事会，如果合适，还要提交电池及蓄电池中关于镉禁令的相关提案以及关于的。