欧盟食品污染物限量标准(中文版)-翻译了(EC)18812006 欧盟食品污染物限量

合集下载

EC1881-2006中文版食品中特定污染物的最大限量

EC1881-2006中文版食品中特定污染物的最大限量
2000
1.3
新鲜生菜(萬苣)(有防护和室外生长的萬苣)不 包括1.4中列出的萬苣
10.1-3.31收获
覆膜生菜
4500
露天生长的生菜
4000
4. 1-9.30收获
覆膜萬苣
3500
潺天生长的萬苣
2500
1.4
冰型生菜
覆膜生菜
2500
露天生长的生菜
2000
1.5
为婴儿和儿童加工的谷物制品和婴幼儿食品(3)(4)
用于人类直接食用或作为食品配料的落花生、坚果 和其他加工制品
2 (5)
4 (5)
2.1.4
在食用干制水果或将其作为食品配料之前应对其进 行挑选,或者进行其他的物理处理
5
10
-
2.1.5
用于人类直接食用或作为食品配料的干制水果和其 他加工制品
2
4
2. 1.6
所有谷物及其制品,包括经加工的谷物制品(2.1.7、
20 (20)
2. 5.8
加工玉米食品,专供婴幼儿及儿童食用(3、7)
20 (20)
2.6
伏马菌素
B1和B2的总和
2.6・1
未加工的玉米(18)
2000 (23)
2. 6.2
玉米淀粉、脱胚玉米粉、粗玉米粉、玉米胚芽油及 精制玉米油
1000 (23)
2. 6.3
供人类直接食用的玉米制品,不包括2.6.2、2.6.4列出的食品
1250
2.4.2
未加工硬质小麦、燕麦(18、19)
1750
2.4.3
未加工玉米(18)
1750 (20)
2.4.4
人类直接食用的谷物、谷物淀粉(包括玉米淀粉、 玉米粉、和粗玉米粉(21))

欧盟食品污染物限量标准(中文版)-翻译了(EC)18812006 欧盟食品污染物限量

欧盟食品污染物限量标准(中文版)-翻译了(EC)18812006 欧盟食品污染物限量

最大限量(mg NO3/kg)
10.1-3.31收获 4.1-9.30收获 3000 2500 2000
1.3
பைடு நூலகம்
新鲜生菜(莴苣)(有防护和室外生长的莴 苣)不包括1.4中列出的莴苣
4500 4000 3500 2500 2500 2000 200
1.4 1.5
冰型生菜 为婴儿和儿童加工的谷物制品和婴幼儿食品 (3)(4)
2
4
2 5 —
4 10 —
2.1.9 2.1.10 2.1.11 2.1.12 2.2 2.2.1
2.2.2 2.2.3 2.2.4 2.2.5 2.2.6
以下调味料种类:辣椒粉(干制水果和其他, 包括辣椒、辣椒粉);胡椒粉(其他水果、包 括白胡椒和黑胡椒)肉豆蔻(肉豆蔻的种 子);姜提取物(姜);姜黄(姜黄粉) 为婴儿和儿童加工的谷物制品和婴幼儿食品 (3)(7) 婴幼儿奶粉和较大婴幼儿奶粉、包括婴幼儿牛 奶和较大婴幼儿奶(4、8) 专用于婴幼儿的有特殊医疗目的(9、10)的 食疗食品 赭曲霉素A 未加工的谷物 所有经未加工谷物制成的产品,包括加工谷物 制品和直接供人类食用的谷物(2.2.9、 2.2.10中列出的除外) 干燥藤本科植物水果(黑醋栗、葡萄干、无子 葡萄干) 炒咖啡豆、炒咖啡粉不包括速溶咖啡 速溶咖啡 葡萄酒(包括汽酒、不包括烈酒和酒精度不小 于15%的酒)和果酒(11)
鳝鱼(鳗类)肌肉及其他制品 生乳(6)及奶制品,包括乳脂 鸡蛋及蛋制品(6) 下列动物脂肪: 牛、羊 禽类 猪
第六部分:多环芳香族碳氢化合物
食品(1) 苯并[a]芘 专供人类直接食用或作为食品配料的油及脂 6.1.1 (可可油除外) 6.1.2 熏肉及熏肉制品 6.1.3 6.1.4 鱼肉(24、24),其他熏制鱼

欧盟添加剂限量标准[整理版]

欧盟添加剂限量标准[整理版]

欧盟添加剂限量标准[整理版]No L61/1?欧盟议会和理事会指令95/2/EC1995年2月20除了色素和甜味剂的食品添加剂欧盟议会和理事会考虑到欧盟缔结的条约,尤其是第100a条,考虑到委员会的提议,考虑到经济和社会委员会的提议,根据条约第189b制定的程序进行,考虑到1998年12月21理事会指令89/107/EEC,成员国关于为人类消费而在食品中授权使用的食品添加剂的近似法律,尤其是第3(2)条,鉴于国家之间关于防腐剂、抗氧化剂和其它添加剂和它们的使用条件的不同,鉴于这可能造成不公平的竞争。

鉴于主要考虑这些食品添加剂和它们的使用条件应当必须保护消费者的规定,鉴于普遍公认未加工的食品和某些其它食品应当远离食品添加剂,鉴于考虑到最近关于这些物质的科学和毒理学信息,一些仅允许用于某些食品和在某些条件下使用,鉴于必须制定严格的制度在婴儿配方、成长配方及断奶食品中使用食品添加剂,象在1989年3月3日理事会指令89/398/EEC中提到的,有关成员国用于特殊营养使用的食品的相近法律,尤其是第4(1)(e),鉴于本指令不影响涉及甜味剂和色素的规定,鉴于依据1991年7月15日理事会指令91/414/EEC涉及的植物保护产品投放市场,依据1990年11月27日理事会指令90/642/EEC附的在某些植物原始产品中农药残留的最高标准,包括水果和蔬菜,属于此种类的物质暂时包括在本指令中,鉴于向食品科学委员会咨询有关那些物质不是联盟规定的科目,鉴于当决定一个特殊的食品属于食物的某个种类,最好跟随向食品标准委员会咨询的程序,鉴于除色素和甜味剂外的食品添加剂的现存纯标准和那些没有纯标准存在的的新规范的修改将采纳指令89/107/EEC第11条规定的相应程序,鉴于食品科学委员会还没有提出关于面粉处理剂的的建议,鉴于那些试剂将在一个单独的指令中规定,鉴于本指令取代指令64/54/EEC、70/357/EEC、74/329/EEC和83/463/EEC,鉴于那些指令特此废除,兹采纳如下指令:第1条1( 本指令是一个构成综合指令的特定的指令,在89/107/EEC指令的第3条的内涵之内,适用于除色素和甜味剂和面粉处理剂外的添加剂。

EC 1881-2006 欧盟关于食品污染物最高限量的新法规

EC 1881-2006 欧盟关于食品污染物最高限量的新法规

COMMISSION REGULATION(EC)No1881/2006of19December2006setting maximum levels for certain contaminants in foodstuffs(Text with EEA relevance)THE COMMISSION OF THE EUROPEAN COMMUNITIES,Having regard to the Treaty establishing the European Community,Having regard to Council Regulation(EEC)No315/93of8 February1993laying down Community procedures for contaminants in food(1),and in particular Article2(3)thereof,Whereas:(1)Commission Regulation(EC)No466/2001of8March2001setting maximum levels for certain contaminants infoodstuffs(2)has been amended substantially manytimes.It is necessary to amend again maximum levelsfor certain contaminants to take into account new infor-mation and developments in Codex Alimentarius.At thesame time,the text should,where appropriate,beclarified.Regulation(EC)No466/2001should thereforebe replaced.(2)It is essential,in order to protect public health,to keepcontaminants at levels which are toxicologicallyacceptable.(3)In view of disparities between the laws of Member Statesand the consequent risk of distortion of competition,forsome contaminants Community measures are necessaryin order to ensure market unity while abiding by theprinciple of proportionality.(4)Maximum levels should be set at a strict level which isreasonably achievable by following good agricultural,fishery and manufacturing practices and taking intoaccount the risk related to the consumption of thefood.In the case of contaminants which are consideredto be genotoxic carcinogens or in cases where currentexposure of the population or of vulnerable groups inthe population is close to or exceeds the tolerable intake,maximum levels should be set at a level which is as lowas reasonably achievable(ALARA).Such approachesensure that food business operators apply measures toprevent and reduce the contamination as far as possiblein order to protect public health.It is furthermore appro-priate for the health protection of infants and youngchildren,a vulnerable group,to establish the lowestmaximum levels,which are achievable through a strictselection of the raw materials used for the manufacturingof foods for infants and young children.This strictselection of the raw materials is also appropriate forthe production of some specific foodstuffs such as branfor direct human consumption.(5)To allow maximum levels to be applied to dried,diluted,processed and compound foodstuffs,where no specificCommunity maximum levels have been established,foodbusiness operators should provide the specific concen-tration and dilution factors accompanied by the appro-priate experimental data justifying the factor proposed.(6)To ensure an efficient protection of public health,products containing contaminants exceeding themaximum levels should not be placed on the marketeither as such,after mixture with other foodstuffs orused as an ingredient in other foods.(7)It is recognised that sorting or other physical treatmentsmake it possible to reduce the aflatoxin content ofconsignments of groundnuts,nuts,dried fruit andmaize.In order to minimise the effects on trade,it isappropriate to allow higher aflatoxin contents for thoseproducts which are not intended for direct humanconsumption or as an ingredient in foodstuffs.In thesecases,the maximum levels for aflatoxins should be fixedtaking into consideration the effectiveness of the above-mentioned treatments to reduce the aflatoxin content ingroundnuts,nuts,dried fruit and maize to levels belowthe maximum limits fixed for those products intendedfor direct human consumption or use as an ingredient infoodstuffs.(8)To enable effective enforcement of the maximum levelsfor certain contaminants in certain foodstuffs,it is appro-priate to provide for suitable labelling provisions forthese cases.(1)OJ L37,13.2.1993,p.1.Regulation as amended by Regulation(EC)No1882/2003of the European Parliament and of the Council(OJ L284,31.10.2003,p.1).(2)OJ L77,16.3.2001,p.1.Regulation as last amended by Regulation(EC)No199/2006(OJ L32,4.2.2006,p.32).(9)Because of the climatic conditions in some MemberStates,it is difficult to ensure that the maximum levelsare not exceeded for fresh lettuce and fresh spinach.These Member States should be allowed for atemporary period to continue to authorise themarketing of fresh lettuce and fresh spinach grown andintended for consumption in their territory with nitratecontents exceeding the maximum levels.Lettuce andspinach producers established in the Member Stateswhich have given the aforementioned authorisationsshould progressively modify their farming methods byapplying the good agricultural practices recommendedat national level.(10)Certain fish species originating from the Baltic regionmay contain high levels of dioxins and dioxin-likePCBs.A significant proportion of these fish speciesfrom the Baltic region will not comply with themaximum levels and would therefore be excluded fromthe diet.There are indications that the exclusion of fishfrom the diet may have a negative health impact in theBaltic region.(11)Sweden and Finland have a system in place which hasthe capacity to ensure that consumers are fully informedof the dietary recommendations concerning restrictionson consumption of fish from the Baltic region by ident-ified vulnerable groups of the population in order toavoid potential health risks.Therefore,it is appropriateto grant a derogation to Finland and Sweden to place onthe market for a temporary period certain fish speciesoriginating in the Baltic region and intended forconsumption in their territory with levels of dioxinsand dioxin-like PCBs higher than those set in this Regu-lation.The necessary measures must be implemented toensure that fish and fish products not complying withthe maximum levels are not marketed in other MemberStates.Finland and Sweden report every year to theCommission the results of their monitoring of thelevels of dioxins and dioxin-like PCBs in fish from theBaltic region and the measures to reduce humanexposure to dioxins and dioxin-like PCBs from theBaltic region.(12)To ensure that the maximum levels are enforced in auniform way,the same sampling criteria and the sameanalysis performance criteria should be applied by thecompetent authorities throughout the Community.It isfurthermore important that analytical results are reportedand interpreted in a uniform way.The measures asregards sampling and analysis specified in this Regulationprovide for uniform rules on reporting and interpret-ation.(13)For certain contaminants,Member States and interestedparties should monitor and report levels,as well reporton the progress with regard to application of pre-ventative measures,to allow the Commission to assessthe need to modify existing measures or to adopt addi-tional measures.(14)Any maximum level adopted at Community level can besubject to a review to take account of the advance ofscientific and technical knowledge and improvements ingood agricultural,fishery and manufacturing practices.(15)Bran and germ can be marketed for direct humanconsumption and it is therefore appropriate to establisha maximum level for deoxynivalenol and zearalenone inthese commodities.(16)Codex Alimentarius has recently set a maximum level forlead in fish which the Community accepted.It istherefore appropriate to modify the current provisionfor lead in fish accordingly.(17)Regulation(EC)No853/2004of the EuropeanParliament and Council of29April2004laying downspecific hygiene rules for food of animal origin(3)definesfoodstuffs of animal origin,and consequently the entriesas regards foodstuffs of animal origin should be amendedin some cases according to the terminology used in thatRegulation.(18)It is necessary to provide that the maximum levels forcontaminants do not apply to the foodstuffs which havebeen lawfully placed on the Community market beforethe date of application of these maximum levels.(19)As regards nitrate,vegetables are the major source for thehuman intake of nitrate.The Scientific Committee onFood(SCF)stated in its opinion of22September1995(4)that the total intake of nitrate is normally wellbelow the acceptable daily intake(ADI)of3,65mg/kgbody weight(bw).It recommended,however,con-tinuation of efforts to reduce exposure to nitrate viafood and water.(20)Since climatic conditions have a major influence on thelevels of nitrate in certain vegetables such as lettuce andspinach,different maximum nitrate levels shouldtherefore be fixed depending on the season.(3)OJ L139,30.4.2004,p.55,as corrected by OJ L226,25.6.2004,p.22.Regulation as last amended by Regulation(EC)No 1662/2006(OJ L320,18.11.2006,p.1).(4)Reports of the Scientific Committee for Food,38th series,Opinionof the Scientific Committee for Food on nitrates and nitrite,p.1, http://ec.europa.eu/food/fs/sc/scf/reports/scf_reports_38.pdf(21)As regards aflatoxins,the SCF expressed in its opinion of23September1994that aflatoxins are genotoxic car-cinogens(5).Based on that opinion,it is appropriate tolimit the total aflatoxin content of food(sum of afla-toxins B1,B2,G1and G2)as well as the aflatoxin B1content alone,aflatoxin B1being by far the most toxiccompound.For aflatoxin M1in foods for infants andyoung children,a possible reduction of the currentmaximum level should be considered in the light ofdevelopments in analytical procedures.(22)As regards ochratoxin A(OTA),the SCF adopted ascientific opinion on17September1998(6).Anassessment of the dietary intake of OTA by the popu-lation of the Community has been performed(7)in theframework of Council Directive93/5/EEC of25February1993on assistance to the Commission and cooperationby the Member States in the scientific examination ofquestions relating to food(8)(SCOOP).The EuropeanFood Safety Authority(EFSA)has,on a request fromthe Commission,adopted an updated scientific opinionrelating to ochratoxin A in food on4April2006(9),taking into account new scientific information andderived a tolerable weekly intake(TWI)of120ng/kg bw.(23)Based on these opinions,it is appropriate to setmaximum levels for cereals,cereal products,dried vinefruit,roasted coffee,wine,grape juice and foods forinfants and young children,all of which contributesignificantly to general human exposure to OTA or tothe exposure of vulnerable groups of consumers such aschildren.(24)The appropriateness of setting a maximum level for OTAin foodstuffs such as dried fruit other than dried vinefruit,cocoa and cocoa products,spices,meat products,green coffee,beer and liquorice,as well as a review of theexisting maximum levels,in particular for OTA in driedvine fruit and grape juice,will be considered in the lightof the recent EFSA scientific opinion.(25)As regards patulin,the SCF endorsed in its meeting on8March2000the provisional maximum tolerable dailyintake(PMTDI)of0,4μg/kg bw for patulin(10).(26)In2001,a SCOOP-task‘Assessment of the dietary intakeof patulin by the population of EU Member States’in theframework of Directive93/5/EEC was performed(11).(27)Based on that assessment and taking into account thePMTDI,maximum levels should be set for patulin incertain foodstuffs to protect consumers from un-acceptable contamination.These maximum levelsshould be reviewed and,if necessary,reduced takinginto account the progress in scientific and technologicalknowledge and the implementation of CommissionRecommendation2003/598/EC of11August2003onthe prevention and reduction of patulin contamination inapple juice and apple juice ingredients in otherbeverages(12).(28)As regards Fusarium toxins,the SCF has adopted severalopinions evaluating deoxynivalenol in December1999(13)establishing a tolerable daily intake(TDI)of1μg/kg bw,zearalenone in June2000(14)establishing atemporary TDI of0,2μg/kg bw,fumonisins in October2000(15)(updated in April2003)(16)establishing a TDIof2μg/kg bw,nivalenol in October2000(17)estab-lishing a temporary TDI of0,7μg/kg bw,T-2andHT-2toxin in May2001(18)establishing a combinedtemporary TDI of0,06μg/kg bw and the trichothecenesas group in February2002(19).(5)Reports of the Scientific Committee for Food,35th series,Opinionof the Scientific Committee for Food on aflatoxins,ochratoxin A and patulin,p.45,http://ec.europa.eu/food/fs/sc/scf/reports/scf_reports_35.pdf(6)Opinion of the Scientific Committee on Food on Ochratoxin A(expressed on17September1998)http://ec.europa.eu/food/fs/sc/scf/out14_en.html(7)Reports on tasks for scientific cooperation,Task3.2.7‘Assessmentof dietary intake of Ochratoxin A by the population of EU Member States’.http://ec.europa.eu/food/food/chemicalsafety/contaminants/task_3-2-7_en.pdf(8)OJ L52,4.3.1993,p.18.(9)Opinion of the Scientific Panel on contaminants in the Food Chainof the EFSA on a request from the Commission related to ochratoxin A in food.http://www.efsa.europa.eu/etc/medialib/efsa/ science/contam/contam_opinions/1521.Par.0001.File.dat/contam_op _ej365_ochratoxin_a_food_en1.pdf (10)Minutes of the120th Meeting of the Scientific Committee on Foodheld on8and9March2000in Brussels,Minute statement on patulin.http://ec.europa.eu/food/fs/sc/scf/out55_en.pdf(11)Reports on tasks for scientific cooperation,Task3.2.8,‘Assessmentof dietary intake of Patulin by the population of EU Member States’.http://ec.europa.eu/food/food/chemicalsafety/contaminants/3.2.8_en.pdf(12)OJ L203,12.8.2003,p.34.(13)Opinion of the Scientific Committee on Food on Fusarium-toxinsPart1:Deoxynivalenol(DON),(expressed on2December1999) http://ec.europa.eu/food/fs/sc/scf/out44_en.pdf(14)Opinion of the Scientific Committee on Food on Fusarium-toxinsPart2:Zearalenone(ZEA),(expressed on22June2000)http://ec.europa.eu/food/fs/sc/scf/out65_en.pdf(15)Opinion of the Scientific Committee on Food on Fusarium-toxinsPart3:Fumonisin B1(FB1)(expressed on17October2000) http://ec.europa.eu/food/fs/sc/scf/out73_en.pdf(16)Updated opinion of the Scientific Committee on Food onFumonisin B1,B2and B3(expressed on4April2003)http://ec.europa.eu/food/fs/sc/scf/out185_en.pdf(17)Opinion of the Scientific Committee on Food on Fusarium-toxinsPart4:Nivalenol(expressed on19October2000)http://ec.europa.eu/food/fs/sc/scf/out74_en.pdf(18)Opinion of the Scientific Committee on Food on Fusarium-toxinsPart5:T-2toxin and HT-2toxin(adopted on30May2001) http://ec.europa.eu/food/fs/sc/scf/out88_en.pdf(19)Opinion of the Scientific Committee on Food on Fusarium-toxinsPart6:Group evaluation of T-2toxin,HT-2toxin,nivalenol and deoxynivalenol.(adopted on26February2002)http://ec.europa.eu/food/fs/sc/scf/out123_en.pdf(29)In the framework of Directive93/5/EEC the SCOOP-task‘Collection of occurrence data on Fusarium toxins in foodand assessment of dietary intake by the population of EUMember States’was performed and finalised inSeptember2003(20).(30)Based on the scientific opinions and the assessment ofthe dietary intake,it is appropriate to set maximum levelsfor deoxynivalenol,zearalenone and fumonisins.Asregards fumonisins,monitoring control results of therecent harvests indicate that maize and maize productscan be very highly contaminated by fumonisins and it isappropriate that measures are taken to avoid such unac-ceptably highly contaminated maize and maize productscan enter the food chain.(31)Intake estimates indicate that the presence of T-2andHT-2toxin can be of concern for public health.Therefore,the development of a reliable and sensitivemethod,collection of more occurrence data and moreinvestigations/research in the factors involved in thepresence of T-2and HT-2toxin in cereals and cerealproducts,in particular in oats and oat products,isnecessary and of high priority.(32)It is not necessary due to co-occurrence to considerspecific measures for3-acetyl deoxynivalenol,15-acetyldeoxynivalenol and fumonisin B3,as measures withregard to in particular deoxynivalenol and fumonisin B1and B2would also protect the human population froman unacceptable exposure from3-acetyl deoxynivalenol,15-acetyl deoxynivalenol and fumonisin B3.The sameapplies to nivalenol for which to a certain degree co-occurrence with deoxynivalenol can be observed.Furthermore,human exposure to nivalenol is estimatedto be significantly below the t-TDI.As regards othertrichothecenes considered in the abovementionedSCOOP-task,such as3-acetyldeoxynivalenol,15-acetyl-deoxynivalenol,fusarenon-X,T2-triol,diacetoxyscirpenol,neosolaniol,monoacetoxyscirpenol and verrucol,thelimited information available indicates that they do notoccur widely and the levels found are generally low.(33)Climatic conditions during the growth,in particular atflowering,have a major influence on the Fusarium toxincontent.However,good agricultural practices,wherebythe risk factors are reduced to a minimum,can preventto a certain degree the contamination by Fusarium fungi.Commission Recommendation2006/583/EC of17August2006on the prevention and reduction ofFusarium toxins in cereals and cereal products(21)contains general principles for the prevention andreduction of Fusarium toxin contamination(zearalenone,fumonisins and trichothecenes)in cereals to be im-plemented by the development of national codes ofpractice based on these principles.(34)Maximum levels of Fusarium toxins should be set forunprocessed cereals placed on the market for first-stageprocessing.Cleaning,sorting and drying procedures arenot considered as first-stage processing insofar as nophysical action is exerted on the grain kernel itself.Scouring is to be considered as first-stage processing.(35)Since the degree to which Fusarium toxins in unpro-cessed cereals are removed by cleaning and processingmay vary,it is appropriate to set maximum levels forfinal consumer cereal products as well as for major foodingredients derived from cereals to have enforceable legis-lation in the interest of ensuring public health protection.(36)For maize,not all factors involved in the formation ofFusarium toxins,in particular zearalenone and fumo-nisins B1and B2,are yet precisely known.Therefore,atime period is granted to enable food business operatorsin the cereal chain to perform investigations on thesources of the formation of these mycotoxins and onthe identification of the management measures to betaken to prevent their presence as far as reasonablypossible.Maximum levels based on currently availableoccurrence data are proposed to apply from2007incase no specific maximum levels based on new infor-mation on occurrence and formation are set beforethat time.(37)Given the low contamination levels of Fusarium toxinsfound in rice,no maximum levels are proposed for riceor rice products.(38)A review of the maximum levels for deoxynivalenol,zearalenone,fumonisin B1and B2as well as the appro-priateness of setting a maximum level for T-2and HT-2toxin in cereals and cereal products should be consideredby1July2008,taking into account the progress inscientific and technological knowledge on these toxinsin food.(39)As regards lead,the SCF adopted an opinion on19June1992(22)endorsing the provisional tolerable weeklyintake(PTWI)of25μg/kg bw proposed by the WHOin1986.The SCF concluded in its opinion that the meanlevel in foodstuffs does not seem to be a cause ofimmediate concern.(20)Reports on tasks for scientific cooperation,Task3.2.10‘Collectionof occurrence data of Fusarium toxins in food and assessment of dietary intake by the population of EU Member States’.http://ec.europa.eu/food/fs/scoop/task3210.pdf(21)OJ L234,29.8.2006,p.35.(22)Reports of the Scientific Committee for Food,32nd series,Opinionof the Scientific Committee for Food on‘The potential risk to health presented by lead in food and drink’,p.7,http://ec.europa.eu/food/fs/sc/scf/reports/scf_reports_32.pdf(40)In the framework of Directive93/5/EEC2004theSCOOP-task3.2.11‘Assessment of the dietary exposureto arsenic,cadmium,lead and mercury of the populationof the EU Member States’was performed in2004(23).Inview of this assessment and the opinion delivered by theSCF,it is appropriate to take measures to reduce thepresence of lead in food as much as possible(41)As regards cadmium,the SCF endorsed in its opinion of2June1995(24)the PTWI of7μg/kg bw and rec-ommended greater efforts to reduce dietary exposure tocadmium since foodstuffs are the main source of humanintake of cadmium.A dietary exposure assessment wasperformed in the SCOOP-task3.2.11.In view of thisassessment and the opinion delivered by the SCF,it isappropriate to take measures to reduce the presence ofcadmium in food as much as possible.(42)As regards mercury EFSA adopted on24February2004an opinion related to mercury and methylmercury infood(25)and endorsed the provisional tolerable weeklyintake of1,6μg/kg bw.Methylmercury is the chemicalform of most concern and can make up more than90%of the total mercury in fish and seafood.Taking intoaccount the outcome of the SCOOP-task3.2.11,EFSAconcluded that the levels of mercury found in foods,other than fish and seafood,were of lower concern.The forms of mercury present in these other foods aremainly not methylmercury and they are thereforeconsidered to be of lower risk.(43)In addition to the setting of maximum levels,targetedconsumer advice is an appropriate approach in the caseof methylmercury for protecting vulnerable groups of thepopulation.An information note on methylmercury infish and fishery products responding to this need hastherefore been made available on the website of theHealth and Consumer Protection Directorate-General ofthe European Commission(26).Several Member Stateshave also issued advice on this issue that is relevant totheir population.(44)As regards inorganic tin,the SCF concluded in itsopinion of12December2001(27)that levels ofinorganic tin of150mg/kg in canned beverages and250mg/kg in other canned foods may cause gastricirritation in some individuals.(45)To protect public health from this health risk it isnecessary to set maximum levels for inorganic tin incanned foods and canned beverages.Until databecomes available on the sensitivity of infants andyoung children to inorganic tin in foods,it is necessaryon a precautionary basis to protect the health of thisvulnerable population group and to establish lowermaximum levels.(46)As regards3-monochloropropane-1,2-diol(3-MCPD)theSCF adopted on30May2001a scientific opinion asregards3-MCPD in food(28),updating its opinion of16December1994(29)on the basis of new scientificinformation and established a tolerable daily intake(TDI)of2μg/kg bw for3-MCPD.(47)In the framework of Directive93/5/EEC the SCOOP-task‘Collection and collation of data on levels of3-MCPDand related substances in foodstuffs’was performed andfinalised in June2004(30).The main contributors of3-MCPD to dietary intake were soy sauce and soy-saucebased products.Some other foods eaten in large quan-tities,such as bread and noodles,also contributed sig-nificantly to intake in some countries because of highconsumption rather than high levels of3-MCPDpresent in these foods.(48)Accordingly maximum levels should be set for3-MCPDin hydrolysed vegetable protein(HVP)and soy saucetaking into account the risk related to the consumptionof these foods.Member States are requested to examineother foodstuffs for the occurrence of3-MCPD in orderto consider the need to set maximum levels for ad-ditional foodstuffs.(23)Reports on tasks for scientific co-operation,Task 3.2.11‘Assessment of dietary exposure to arsenic,cadmium,lead and mercury of the population of the EU Member States’.http://ec.europa.eu/food/food/chemicalsafety/contaminants/scoop_ 3-2-11_heavy_metals_report_en.pdf(24)Reports of the Scientific Committee for Food,36th series,Opinionof the Scientific Committee for Food on cadmium,p.67,http://ec.europa.eu/food/fs/sc/scf/reports/scf_reports_36.pdf (25)Opinion of the Scientific Panel on contaminants in the Food Chainof the European Food Safety Authority(EFSA)on a request from the Commission related to mercury and methylmercury in food (adopted on24February2004)http://www.efsa.eu.int/science/contam/contam_opinions/259/opinion_contam_01_en1.pdf(26)http://ec.europa.eu/food/food/chemicalsafety/contaminants/information_note_mercury-fish_12-05-04.pdf (27)Opinion of the Scientific Committee on Food on acute risks posedby tin in canned foods(adopted on12December2001)http://ec.europa.eu/food/fs/sc/scf/out110_en.pdf(28)Opinion of the Scientific Committee on Food on3-monochloro-propane-1,2-diol(3-MCPD)updating the SCF opinion of1994 (adopted on30May2001)http://ec.europa.eu/food/fs/sc/scf/out91_en.pdf(29)Reports of the Scientific Committee for Food,36th series,Opinionof the Scientific Committee for Food on3-monochloro-propane-1,2-diol3-MCPD),p.31,http://ec.europa.eu/food/fs/sc/scf/reports/scf_reports_36.pdf (30)Reports on tasks for scientific cooperation,Task3.2.9‘Collectionand collation of data on levels of3-monochloropropanediol(3-MCPD)and related substances in foodstuffs’.http://ec.europa.eu/ food/food/chemicalsafety/contaminants/scoop_3-2-9_final_report_ chloropropanols_en.pdf(49)As regards dioxins and PCBs,the SCF adopted on30May2001an opinion on dioxins and dioxin-like PCBsin food(31),updating its opinion of22November2000(32)fixing a tolerable weekly intake(TWI)of14pg World Health Organisation toxic equivalent(WHO-TEQ)/kg bw for dioxins and dioxin-like PCBs.(50)Dioxins as referred to in this Regulation cover a group of75polychlorinated dibenzo-p-dioxin(PCDD)congenersand135polychlorinated dibenzofuran(PCDF)congeners,of which17are of toxicological concern.Polychlorinated biphenyls(PCBs)are a group of209different congeners which can be divided into twogroups according to their toxicological properties:12congeners exhibit toxicological properties similar todioxins and are therefore often termed dioxin-likePCBs.The other PCBs do not exhibit dioxin-liketoxicity but have a different toxicological profile.(51)Each congener of dioxins or dioxin-like PCBs exhibits adifferent level of toxicity.In order to be able to sum upthe toxicity of these different congeners,the concept oftoxic equivalency factors(TEFs)has been introduced tofacilitate risk assessment and regulatory control.Thismeans that the analytical results relating to all the indi-vidual dioxin and dioxin-like PCB congeners of toxico-logical concern are expressed in terms of a quantifiableunit,namely the TCDD toxic equivalent(TEQ).(52)Exposure estimates taking into account the SCOOP-task‘Assessment of dietary intake of dioxins and related PCBsby the population of EU Member States’finalised in June2000(33)indicate that a considerable proportion of theCommunity population has a dietary intake in excess ofthe TWI.(53)From a toxicological point of view,any level set shouldapply to both dioxins and dioxin-like PCBs,but in2001maximum levels were set on Community level only fordioxins and not for dioxin-like PCBs,given the verylimited data available at that time on the prevalence ofdioxin-like PCBs.Since2001,however,more data on thepresence of dioxin-like PCBs have become available,therefore,maximum levels for the sum of dioxins anddioxin-like PCBs have been set in2006as this is themost appropriate approach from a toxicological pointof view.In order to ensure a smooth transition,thelevels for dioxins should continue to apply for a transi-tional period in addition to the levels for the sum ofdioxins and dioxin-like PCBs.Foodstuffs must complyduring that transitional period with the maximumlevels for dioxins and with the maximum levels for thesum of dioxins and dioxin-like PCBs.Consideration willbe given by31December2008to dispensing with theseparate maximum levels for dioxins.(54)In order to encourage a proactive approach to reducingthe dioxins and dioxin-like PCBs present in food andfeed,action levels were set by Commission Recommen-dation2006/88/EC of6February2006on the reductionof the presence of dioxins,furans and PCBs in feeding-stuffs and foodstuffs(34).These action levels are a tool forcompetent authorities and operators to highlight thosecases where it is appropriate to identify a source ofcontamination and to take measures to reduce oreliminate it.Since the sources of dioxins and dioxin-like PCBs are different,separate action levels aredetermined for dioxins on the one hand and fordioxin-like PCBs on the other hand.This proactiveapproach to actively reduce the dioxins and dioxin-likePCBs in feed and food and consequently,the maximumlevels applicable should be reviewed within a definedperiod of time with the objective to set lower levels.Therefore,consideration will be given by31December2008to significantly reducing the maximum levels forthe sum of dioxins and dioxin-like PCBs.(55)Operators need to make efforts to step up their capacityto remove dioxins,furans and dioxin-like PCBs frommarine oil.The significant lower level,to which con-sideration shall be given by31December2008,shallbe based on the technical possibilities of the mosteffective decontamination procedure.(56)As regards the establishment of maximum levels forother foodstuffs by31December2008,particularattention shall be paid to the need to set specific lowermaximum levels for dioxins and dioxin-like PCBs infoods for infants and young children in the light of themonitoring data obtained through the2005,2006and2007programmes for monitoring dioxins and dioxin-like PCBs in foods for infants and young children.(31)Opinion of the Scientific Committee on Food on the riskassessment of dioxins and dioxin-like PCBs in food.Update basedon new scientific information available since the adoption of theSCF opinion of22nd November2000(adopted on30May2001)http://ec.europa.eu/food/fs/sc/scf/out90_en.pdf(32)Opinion of the Scientific Committee on Food on the riskassessment of dioxins and dioxin-like PCBs in food.(adopted on22November2000)http://ec.europa.eu/food/fs/sc/scf/out78_en.pdf(33)Reports on tasks for scientific cooperation,Task3.2.5‘Assessmentof dietary intake of dioxins and related PCBs by the population ofEU Member States’.http://ec.europa.eu/dgs/health_consumer/library/pub/pub08_en.pdf(34)OJ L42,14.2.2006,p.26.。

Regulation 1881-2006-EC 食品中特定污染物的最大限量-中文版

Regulation 1881-2006-EC 食品中特定污染物的最大限量-中文版

第二部分 毒枝菌素
食品(1) 2.1 黄曲霉毒素 B1 8(5) 5(5) 2(5) 5 最大限量(μ g/kg) B1、B2、G1、G2 的总和 15(5) 10(5) 4(5) 10
在食用落花生或将其作为食品配料之前应对其 2.1.1 进行挑选,或者进行其他的物理处理 在食用坚果或将其作为食品配料之前应对其进 2.1.2 行挑选,或者进行其他的物理处理 用于人类直接食用或作为食品配料的落花生、 2.1.3 坚果和其他加工制品 在食用干制水果或将其作为食品配料之前应对 2.1.4 其进行挑选,或者进行其他的物理处理 用于人类直接食用或作为食品配料的干制水果 2.1.5 和其他加工制品 所有谷物及其制品,包括经加工的谷物制品 2.1.6 (2.1.7、2.1.10、2.1.12列出的食品除外) 在食用玉米或将其作为食品配料之前应对其进 2.1.7 行挑选,或者进行其他的物理处理 2.1.8 生乳(6)、热处理牛奶和用于制造奶制品的奶
2(12) 2(12)
0.5 0.5
—— 50 50 25
10 10
1250 1750 1750(20) 750 750 500
婴幼儿及儿童食用加工谷物食品及婴幼儿食品 2.4.7 (3、7) 2.5 玉米烯酮(霉菌毒素) 2.5.1 非玉米未加工谷物(18、19) 2.5.2 未加工玉米(18) 直接供人类食用的谷物、谷物淀粉、在市场上 销售的供人类直接食用的糠(作为终产品)及 胚芽不包括在2.5.4、2.5.7及2.5.8中列出的 2.5.3 产品 直接供人类食用的玉米、玉米淀粉、玉米粉、 2.5.4 粗玉米淀粉、玉米胚芽及精制玉米油(21) 面包(包括小的面包制品)、糕点、饼干、谷 2.5.5 物点心、和早餐用麦片 2.5.6 玉米点心及以玉米为主料的早餐麦片粥 加工谷物食品(不包括加工玉米食品)及专供 2.5.7 婴幼儿及儿童食用的婴儿食品 2.5.8 加工玉米食品,专供婴幼儿及儿童食用(3、7) 2.6 伏马菌素 2.6.1 未加工的玉米(18) 玉米淀粉、脱胚玉米粉、粗玉米粉、玉米胚芽 2.6.2 油及精制玉米油 供人类直接食用的玉米制品,不包括2.6.2、 2.6.3 2.6.4列出的食品 加工的玉米制品及婴儿食品,专供婴幼儿及儿 2.6.4 童食用 2.7 T-2毒素及HT-2毒素 2.7.1 未经加工的谷物及谷物制品

(EU)No 1881-2006 欧盟食品污染物限量标准(中文版)

(EU)No 1881-2006 欧盟食品污染物限量标准(中文版)

6.1.5 6.1.6 双壳贝类(26) 6.1.7 专供婴幼儿及儿童食用的经加工的谷物制品 婴幼儿奶粉和较大婴幼儿奶粉、包括婴幼儿牛 6.1.8 奶和较大婴幼儿奶(8、29) 6.1.9 专供婴幼儿食用的以医疗为目的的食疗食品
委员会法规(EC)No 1881/2006 2006年12月19日发布 规定食品中特定污染物的最大限量 附录
第一部分 硝酸盐 食品(1)
1.1 1.2 新鲜菠菜(2) 保存、深低温冷冻或冷冻菠菜 10.1-3.31收获 覆膜生菜 露天生长的生菜 4.1-9.30收获 覆膜莴苣 露天生长的莴苣 覆膜生菜 露天生长的生菜
3.3.1
0.5
3.3.2
1 200 100 50
3.4
3.4.1 3.4.2 3.4.3

非饮料类罐装食品 罐装饮料,包括水果汁及蔬菜汁 专供婴幼儿食用的罐装婴儿食品及经加工的谷物食 品,不包括干燥粉末状制品(3、29) 罐装婴幼儿奶粉及较大婴幼儿罐装奶粉(包括也婴 幼儿牛奶及较大婴幼儿牛奶),不包括干燥精粉制 品(8、29) 专供婴幼儿的特殊医疗用罐装食品不包括干燥精粉 制品(8、29)
谷物、豆类蔬菜及豆类 蔬菜,不包括芸薹属蔬菜、叶类蔬菜、新鲜草本植 物及真菌(27).马铃薯的限量按照去皮马铃薯计 3.1.10 算 3.1.11 芸薹蔬菜、叶类蔬菜及养殖真菌 3.1.12 水果,不包括草莓及小水果(27) 3.1.13 草莓及小水果(27) 3.1.14 脂肪和油,不包括乳脂 3.1.15 水果汁、浓缩果汁及水果花蜜(14) 葡萄酒(包括汽酒、不包括烈酒)、苹果酒、梨酒 3.1.16 及果酒(11) 3.1.17 加香葡萄酒、加香葡萄酒饮料及加香鸡尾酒(13)
2(12) 2(12)
0.5 0.5

欧盟食品中多环芳烃最大限量要求

欧盟食品中多环芳烃最大限量要求

欧盟食品中多环芳烃最大限量要求(3) Foodstuffs listed in this category as defined in Commission Directive 96/5/EC of 16 February 1996 on processed cereal-based foods and baby foods for infants and young children (OJ L 49, 28.2.1996, p. 17) as last amended by Directive 2003/13/EC (OJ L 41, 14.2.2003, p. 33).(8) Foodstuffs listed in this category as defined in Commission Directive 91/321/EEC of 14 May 1991 on infant formulae and follow-on formulae (OJ L 175, 4.7.1991, p. 35) as last amended by Directive 2003/14/EC (OJ L 41, 14.2.2003, p. 37).(9) Foodstuffs listed in this category as defined in Commission Directive 1999/21/EC of 25 March 1999 on dietary foods for special medical purposes (OJ L 91, 7.4.1999, p.29).(24) Fish listed in this category as defined in category (a), with the exclusion of fish liver falling under code CN 0302 70 00, of the list in Article 1 of Council Regulation (EC) No 104/2000 (OJ L 17, 21.1.2000, p. 22) as last amended by the Act concerning the conditions of accession of the Czech Republic, the Republic of Estonia, the Republic of Cyprus, the Republic of Latvia, the Republic of Lithuania, the Republic of Hungary, the Republic of Malta, the Republic of Poland, the Republic of Slovenia and the Slovak Republic and the adjustments to the Treaties on which the European Union is founded (OJ L 236, 23.9.2003, p. 33). In case of dried, diluted, processed and/or compound foodstuffs Article 2(1) and 2(2) apply.(25) Where fish are intended to be eaten whole, the maximum level shall apply to the whole fish.(26) Foodstuffs falling within category (c) and (f) of the list in Article 1 of Regulation (EC) No 104/2000, as appropriate (species as listed in the relevant entry). In case of dried, diluted, processed and/or compound foodstuffs Article 2(1) and 2(2) apply.(29) The maximum level refers to the product as sold.(35) Benzo(a)pyrene, for which maximum levels are listed, is used as a marker for the occurrence and effect of carcinogenic polycyclic aromatic hydrocarbons. These measures therefore provide full harmonisation on polycyclic aromatic hydrocarbons in the listed foods across the Member States.(36) Foodstuffs listed in this category as defined in categories (b), (c), and (f) of the list in Article 1 of Regulation (EC) No 104/2000。

2021年欧盟食品中重金属限量标准(中文)

2021年欧盟食品中重金属限量标准(中文)

*欧阳光明*创编 2021.03.07欧盟重金属限量标准欧阳光明(2021.03.07)(中国SPS通报咨询中心提供)一、铅1铅Lead未加工的牛奶*, 热处理的牛奶和以牛奶为原料加工的奶制品Raw milk *, heat-treated milk and milk for theman0.020欧盟*Foodstuffs listed in thiscategory as defined in2铅Lead婴儿食品和后续食品Infant formulae and follow-on formulae0.020欧盟The maximum level refers tothe products ready to3铅Lead牛、羊、猪和家禽肉,不包括下Meat (excluding offal) of bovine animals, sheep,p0.10欧盟Foodstuffs listed in thiscategory as defined in R4铅Lead牛、羊、猪和家禽的下水Offal of bovine animals, sheep, pig and poultry0.50欧盟Foodstuffs listed in thiscategory as defined in R5铅Lead鱼的肌肉Muscle meat of fish0.30欧盟Fish listed in this category asdefined in categor6铅Lead甲壳类, 不包括螃蟹的褐色肉、龙虾和大小相当的甲壳类(Nephropidae and PalinurCrustaceans, excluding brown meat of crab andexcl0.50欧盟Foodstuffs falling withincategory © and (f) of th7铅Lead双壳类动物Bivalve molluscs1.5欧盟Foodstuffs falling withincategory © and (f) of th8铅Lead头足类动物Cephalopods (without viscera)1.0欧盟Foodstuffs falling withincategory © and (f) of th9铅Lead谷类、豆荚和豆科植物Cereals, legumes and pulses0.20欧盟10铅Lead蔬菜,不包括芸苔蔬菜、叶类蔬菜、新鲜草药和菌类,土豆的最大限量适用于去皮土豆Vegetables, excluding brassica vegetables, leaf ve0.10欧盟The maximum level appliesafter washing of the fru11铅Lead芸苔蔬菜、叶类蔬菜和食用菌Brassica vegetables, leaf vegetables and cultivate0.30欧盟The maximum level appliesafter washing of the fru12铅Lead果实,不包括浆果和小果实Fruit, excluding berries and small fruit0.10欧盟The maximum level appliesafter washing of the fru13铅Lead浆果和小果Berries and small fruit0.20欧盟The maximum level appliesafter washing of the fru14铅Lead脂肪和油,包括奶油Fats and oils, including milk fat0.10欧盟15铅Lead果汁,作为重新制造的浓缩果汁和果蜜Fruit juices, concentrated fruit juices as reconst0.050欧盟Foodstuffs listed in thiscategory as defined in C16 铅酒(包括汽酒,不包括利口酒),苹果酒,梨酒和果0.20#欧*Foodstuffs listed in this*欧阳光明*创编 2021.03.07Lead酒*Wine (including sparkling wine, excludingliqueur盟category as defined in17铅Lead香酒、加酒芬香的饮料和加酒芬香的鸡尾酒*Aromatized wine, aromatized wine-based drinksand0.20#欧盟*Foodstuffs listed in thiscategory as defined in二、镉1镉Cadmium牛、羊、猪和家禽肉,不包括下水Meat (excluding offal) of bovine animals,sheep, p0.050欧盟Foodstuffs listed in thiscategory as defined in R2镉Cadmium马肉,不包括下水Horsemeat, excluding offal (6)0.20欧盟Foodstuffs listed in thiscategory as defined in R3镉Cadmium牛、羊、猪、家禽、马肝脏Liver of bovine animals, sheep, pig, poultryand h0.50欧盟Foodstuffs listed in thiscategory as defined in R4镉Cadmium牛、羊、猪、家禽、马肾脏Kidney of bovine animals, sheep, pig, poultryand1.0欧盟Foodstuffs listed in thiscategory as defined in R5镉Cadmium鱼肉,不包括3.2.6和3.2.7中列出的那些鱼肉Muscle meat of fish , excluding species listedin0.050欧盟Fish listed in this categoryas defined in categor6镉Cadmium3.2.6 下列鱼的肉:凤尾鱼 (Engraulis 种)、鲣(Sarda sarda)、常见的Muscle meat of the following fish :anchovy(Engrau0.10欧盟Fish listed in this categoryas defined in categor7镉Cadmium3.2.7旗鱼的肉(Xiphias gladius)3.2.7 Muscle meat of swordfish (Xiphiasgladius)0.30欧盟Fish listed in this categoryas defined in categor8镉Cadmium甲壳类, 不包括螃蟹的褐色肉、龙虾和大小相当的甲壳类(Nephropidae and PalinurCrustaceans, excluding brown meat of craband excl0.50欧盟Foodstuffs falling withincategory © and (f) of th9镉Cadmium双壳类软体动物Bivalve molluscs1.0欧盟Foodstuffs falling withincategory © and (f) of th10镉Cadmium头足类软体动物(没有内脏)Cephalopods (without viscera)1.0欧盟Foodstuffs falling withincategory © and (f) of th11镉Cadmium谷物不包括麸、酵母、小麦和大米Cereals excluding bran, germ, wheat and rice0.10欧盟12镉Cadmium麸、酵母、小麦和大米Bran, germ, wheat and rice0.20欧盟13镉Cadmium大豆Soybeans0.20欧盟14镉Cadmium蔬菜和水果,叶类蔬菜除外,茎类蔬菜,松子,根类蔬菜和马铃薯Vegetables and fruit, excluding leafvegetables, f0.050欧盟The maximum level appliesafter washing of the fru15 镉叶类蔬菜,新鲜中草药,食用菌和块根芹0.20欧The maximum level applies after washing of the fru*欧阳光明*创编 2021.03.07 Cadmium Leaf vegetables, fresh herbs, cultivated fungiand盟16镉Cadmium茎类蔬菜,根类蔬菜和番茄,块根芹。

  1. 1、下载文档前请自行甄别文档内容的完整性,平台不提供额外的编辑、内容补充、找答案等附加服务。
  2. 2、"仅部分预览"的文档,不可在线预览部分如存在完整性等问题,可反馈申请退款(可完整预览的文档不适用该条件!)。
  3. 3、如文档侵犯您的权益,请联系客服反馈,我们会尽快为您处理(人工客服工作时间:9:00-18:30)。

2(12) 2(12)
0.5 0.5
—— 50 50 25
10 10
1250 1750 1750(20) 750 750 500
婴幼儿及儿童食用加工谷物食品及婴幼儿食品 2.4.7 (3、7) 2.5 玉米烯酮(霉菌毒素) 2.5.1 非玉米未加工谷物(18、19) 2.5.2 未加工玉米(18) 直接供人类食用的谷物、谷物淀粉、在市场上 销售的供人类直接食用的糠(作为终产品)及 胚芽不包括在2.5.4、2.5.7及2.5.8中列出的 2.5.3 产品 直接供人类食用的玉米、玉米淀粉、玉米粉、 2.5.4 粗玉米淀粉、玉米胚芽及精制玉米油(21) 面包(包括小的面包制品)、糕点、饼干、谷 2.5.5 物点心、和早餐用麦片 2.5.6 玉米点心及以玉米为主料的早餐麦片粥 加工谷物食品(不包括加工玉米食品)及专供 2.5.7 婴幼儿及儿童食用的婴儿食品 2.5.8 加工玉米食品,专供婴幼儿及儿童食用(3、7) 2.6 伏马菌素 2.6.1 未加工的玉米(18) 玉米淀粉、脱胚玉米粉、粗玉米粉、玉米胚芽 2.6.2 油及精制玉米油 供人类直接食用的玉米制品,不包括2.6.2、 2.6.3 2.6.4列出的食品 加工的玉米制品及婴儿食品,专供婴幼儿及儿 2.6.4 童食用 2.7 T-2毒素及HT-2毒素 2.7.1 未经加工的谷物及谷物制品
鳝鱼(鳗类)肌肉及其他制品 生乳(6)及奶制品,包括乳脂 鸡蛋及蛋制品(6) 下列动物脂肪: 牛、羊 禽类 猪
第六部分:多环芳香族碳氢化合物
食品(1) 苯并[a]芘 专供人类直接食用或作为食品配料的油及脂 6.1.1 (可可油除外) 6.1.2 熏肉及熏肉制品 6.1.3 6.1.4 鱼肉(24、24),其他熏制鱼
最大限量(mg NO3/kg)
10.1-3.31收获 4.1-9.30收获 3000 2500 2000
1.3
新鲜生菜(莴苣)(有防护和室外生长的莴 苣)不包括1.4中列出的莴苣
4500 4000 3500 2500 2500 2000 200
1.4 1.5
冰型生菜 为婴儿和儿童加工的谷物制品和婴幼儿食品 (3)(4)
第二部分 毒枝菌素
食品(1) 2.1 黄曲霉毒素 B1 8(5) 5(5) 2(5) 5 最大限量(μ g/kg) B1、B2、G1、G2 的总和 15(5) 10(5) 4(5) 10
在食用落花生或将其作为食品配料之前应对其 2.1.1 进行挑选,或者进行其他的物理处理 在食用坚果或将其作为食品配料之前应对其进 2.1.2 行挑选,或者进行其他的物理处理 用于人类直接食用或作为食品配料的落花生、 2.1.3 坚果和其他加工制品 在食用干制水果或将其作为食品配料之前应对 2.1.4 其进行挑选,或者进行其他的物理处理 用于人类直接食用或作为食品配料的干制水果 2.1.5 和其他加工制品 所有谷物及其制品,包括经加工的谷物制品 2.1.6 (2.1.7、2.1.10、2.1.12列出的食品除外) 在食用玉米或将其作为食品配料之前应对其进 2.1.7 行挑选,或者进行其他的物理处理 2.1.8 生乳(6)、热处理牛奶和用于制造奶制品的奶
委员会法规(EC)No 1881/2006 2006年12月19日发布 规定食品中特定污染物的最大限量 附录
第一部分 硝酸盐 食品(1)
1.1 1.2 新鲜菠菜(2) 保存、深低温冷冻或冷冻菠菜 10.1-3.31收获 覆膜生菜 露天生长的生菜 4.1-9.30收获 覆膜莴苣 露天生长的莴苣 覆膜生菜 露天生长的生菜
熏鱼及熏制水产品(25、36)不包括双壳贝类。最 大限量按熏制甲壳动物计,褐色蟹肉及龙虾肉胸肉 及类似的大甲壳动物除外(海螯虾科及龙虾科) 非熏制甲壳动物、头足类动物类(26)。最大限量 按熏制甲壳动物计,褐色蟹肉及龙虾肉胸肉及类似 的大甲壳动物除外(海螯虾科及龙虾科)
最大限量(μ g/kg重量)
6.1
200 100 200(20)
75 200(20) 50 50(20) 20(20) 20(20) B1和B2的总和 2000(23) 1000(23) 400(23) 200(23) T-2毒素及HT-2毒素总和
第三部分:重金属 食品(1)
3.1
3.1.1 3.1.2 3.1.3 3.1.4 3.1.5 3.1.6 3.1.7 3.1.8 3.1.9
3.2.6 3.2.7 3.2.8 3.2.9
0.1 0.3 0.5 1 1 0.1 0.1 0.2 0.05 0.2 0.1
3.2.10 头足类(出去内脏)(26) 3.2.11 谷物(糠、胚芽、小麦、大米除外) 3.2.12 糠、胚芽、小麦、大米 3.2.13 大豆 蔬菜和水果,不包括叶类蔬菜、新鲜草本植物、真 3.2.14 菌、茎类蔬菜、花生、根类蔬菜及马铃薯(27) 3.2.15 叶类蔬菜、新鲜草本植物、种植真菌及芹菜(27) 茎、根类蔬菜及马铃薯不包括芹菜。马铃薯的最大 3.2.16 限量按去皮马铃薯计
2 5 5 2 5 10 1
6.1.5 6.1.6 双壳贝类(26) 6.1.7 Байду номын сангаас供婴幼儿及儿童食用的经加工的谷物制品 婴幼儿奶粉和较大婴幼儿奶粉、包括婴幼儿牛 6.1.8 奶和较大婴幼儿奶(8、29) 6.1.9 专供婴幼儿食用的以医疗为目的的食疗食品
1
1
备注: 括号内序号详细解释请参考英文版标准
3.3

水产品(26)及鱼肉(24、25),在3.3.2中列出 的种类除外。最大限量按甲壳动物计,褐色蟹肉及 龙虾肉胸肉及类似的大甲壳动物除外(海螯虾科及 龙虾科) 以下种类的鱼肉:安康鱼、大西洋鲶鱼、鲣(等金 枪鱼科鱼类)、鳗鱼、太平洋胸棘鲷、腔吻鳕鱼、 大比目鱼(蝶鱼)、枪鱼,(青枪鱼,四鳃旗鱼)、 鳞鲆属、鲻鱼、梭鱼、鳕鱼、红鱼、旗鱼(两个种 类的)、安哥拉带鱼、鲨鱼(各种各样的)、金枪 鱼(金枪鱼类、鲔属 、鲣鱼 )、 鲟鱼 (鲟鱼 类;蝶鲛)、鲭或鲳鱼(鳞蛇鲭属 、棘鳞蛇鲭、 海鱼 )
3.3.1
0.5
3.3.2
1 200 100 50
3.4
3.4.1 3.4.2 3.4.3

非饮料类罐装食品 罐装饮料,包括水果汁及蔬菜汁 专供婴幼儿食用的罐装婴儿食品及经加工的谷物食 品,不包括干燥粉末状制品(3、29) 罐装婴幼儿奶粉及较大婴幼儿罐装奶粉(包括也婴 幼儿牛奶及较大婴幼儿牛奶),不包括干燥精粉制 品(8、29) 专供婴幼儿的特殊医疗用罐装食品不包括干燥精粉 制品(8、29)
2
4
2 5 —
4 10 —
2.1.9 2.1.10 2.1.11 2.1.12 2.2 2.2.1
2.2.2 2.2.3 2.2.4 2.2.5 2.2.6
以下调味料种类:辣椒粉(干制水果和其他, 包括辣椒、辣椒粉);胡椒粉(其他水果、包 括白胡椒和黑胡椒)肉豆蔻(肉豆蔻的种 子);姜提取物(姜);姜黄(姜黄粉) 为婴儿和儿童加工的谷物制品和婴幼儿食品 (3)(7) 婴幼儿奶粉和较大婴幼儿奶粉、包括婴幼儿牛 奶和较大婴幼儿奶(4、8) 专用于婴幼儿的有特殊医疗目的(9、10)的 食疗食品 赭曲霉素A 未加工的谷物 所有经未加工谷物制成的产品,包括加工谷物 制品和直接供人类食用的谷物(2.2.9、 2.2.10中列出的除外) 干燥藤本科植物水果(黑醋栗、葡萄干、无子 葡萄干) 炒咖啡豆、炒咖啡粉不包括速溶咖啡 速溶咖啡 葡萄酒(包括汽酒、不包括烈酒和酒精度不小 于15%的酒)和果酒(11)
3.4.4 3.4.5
50 50
食品(1) 4.1 4.2
海藻水解蛋白(30) 豆浆(30)
第四部分:3-氯-1,2-丙二醇 最大限量(μ g/kg) 20 20 第五部分:二恶英类及多氯联苯(31) 最大限量
食品(1)
食品(1)
5.1 以下肉及肉制品(可食内脏除外): 牛及羊 禽类 猪 陆生动物肝脏参考5.1(6),及其他衍生产品
谷物、豆类蔬菜及豆类 蔬菜,不包括芸薹属蔬菜、叶类蔬菜、新鲜草本植 物及真菌(27).马铃薯的限量按照去皮马铃薯计 3.1.10 算 3.1.11 芸薹蔬菜、叶类蔬菜及养殖真菌 3.1.12 水果,不包括草莓及小水果(27) 3.1.13 草莓及小水果(27) 3.1.14 脂肪和油,不包括乳脂 3.1.15 水果汁、浓缩果汁及水果花蜜(14) 葡萄酒(包括汽酒、不包括烈酒)、苹果酒、梨酒 3.1.16 及果酒(11) 3.1.17 加香葡萄酒、加香葡萄酒饮料及加香鸡尾酒(13)
水产品(26)及鱼肉(24、25),在3.3.2中列出 的种类除外。最大限量按甲壳动物计,褐色蟹肉及 龙虾肉胸肉及类似的大甲壳动物除外(海螯虾科及 龙虾科)
二恶英总和(32)
3pg/g 2pg/g 1pg/g 6pg/g 脂肪 脂肪 脂肪 脂肪
多氯联苯总和(32)
4.5pg/g 脂肪 4pg/g 脂肪 1.5pg/g 脂肪 12pg/g 脂肪
最大限量(mg/kg)
0.02 0.02 0.1 0.5 0.3 0.5 1.5 1 0.2 0.1 0.3 0.1 0.2 0.1 0.05 0.2(28) 0.2(28)

生乳(6)、热处理牛奶和用于制造奶制品的奶 婴幼儿配方及较大婴幼儿配方(4、8) 牛肉、羊肉、猪肉、及禽肉(6)(不包括内脏) 牛、羊、猪及禽的内脏(6) 鱼肉(24、25) 甲壳类动物,不包括褐色蟹肉、龙虾胸肉及类似的 大甲壳动物(海螯虾科和龙虾科)(26) 双壳贝类(26) 头足类(出去内脏)
3.2
3.2.1 3.2.2 3.2.3 3.2.4 3.2.5

牛、羊、猪及禽肉(不包括内脏)(6) 马肉,不包括内脏 牛、羊、猪、禽及马内脏(6) 牛、羊、猪、禽及马肾脏(6) 鱼肉(24、25)不包括3.2.6及3.2.7中列出的种类 以下这些鱼类的肌肉:凤尾鱼(鳀鱼类)、鲣鱼 (沙丁鱼类)、鲷(鲷科)、鳗(鳗鱼)、乌鱼(鲻 鱼类)、竹夹鱼(竹夹鱼类)、鲯鲭(鲯鲭科)、 沙丁鱼(沙丁鱼 )、沙丁鱼(沙丁鱼类)、金枪 鱼(鲔属)、楔型鱼(鳎鱼) 箭鱼肉(箭鱼)(24、25) 甲壳类动物,不包括褐色蟹肉、龙虾胸肉及类似的 大甲壳动物(海螯虾科和龙虾科)(26) 双壳贝类(26) 0.05 0.2 0.5 1 0.05
相关文档
最新文档