霜霉威FAO残留数据
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欧盟农残限量标准(2019.4.27更新)欧盟农残限量标准产品:茶叶(干叶和茎,已经发酵或用其他方法加工的商品茶叶)2019年4月27日更新(*) 表明该最大残留限量设定在残留分析方法的测定低限。
单位:mg/kg序号[***********][***********]3242526农药通用英文名称1,1-dichloro-2,2-bis(4-ethylphenyl)ethane(F)1,2-dibromoethane (ethylene dibromide) (F)1,2-dichloroethane (ethylene dichloride)(F)1,3-Dichloropropene 1-Naphthylacetamide 1-Naphthylacetic acid1-methylcyclopropene 2,4,5-T (F)2,4-D (sum of 2,4-D and its estersexpressed as 2,4-D)2,4-DB (sum of 2,4-DB, its salts, itsesters and its conjugates, expressed as2,4-DB) (R)2-phenylphenolAbamectin (sum of avermectin B1a,avermectinB1b and delta-8,9 isomer ofavermectin B1a) (F)Acephate Acequinocyl Acetamiprid (R)AcetochlorAcibenzolar-S-methyl (sum of acybenzolar-S-methyl and acibenzolar acid (CGA 210007)expressed as acybenzolar-S-methyl)AclonifenAcrinathrin (F)AlachlorAldicarb (sum of aldicarb, its sulfoxideand its sulfone, expressed as aldicarb)Aldrin and Dieldrin (Aldrin and dieldrincombined expressed as dieldrin) (F)AmetoctradinAmidosulfuron (R)Aminopyralid Amisulbrom农药通用中文名称1,1-二氯-2,2-二(4-乙苯)乙烷1,2-二溴乙烷1,2-二氯乙烷1,3-二氯丙烯1-萘乙酰胺1-萘乙酸1-甲基环丙烯2,4,5-三氯苯氧乙酸2,4-滴(2,4-滴和以2,4-滴表示的其酯的总2,4-滴丁酸2-邻苯基苯酚阿维菌素,阿巴克丁乙酰甲胺磷亚醌螨啶虫脒乙草胺苯并噻二唑苯草醚氟丙菊酯甲草胺涕灭威艾试剂与狄试剂辛唑嘧菌胺酰嘧磺隆氯氨基吡啶酸吲唑磺菌胺(安美速)最大残留限量0.1*0.02*0.02*0.05*0.05*0.05*0.02*0.05*0.1*0.1*0.1*0.02*0.05*0.02*0.1*0.01*0.0 5*0.05*0.05*0.05*0.05*0.02*0.01*0.05*0.02*0.01*序号农药通用英文名称Amitraz (amitraz including the metabolitescontaining the 2,4 -dimethylaniline moietyexpressed as amitraz)Amitrole Anilazine Aramite(F)AsulamAtrazine (F)Aureobasidium pullulans strains DSM 14940and DSM 14941 (++)Azadirachtin AzimsulfuronAzinphos-ethyl (F)Azinphos-methyl (F)Azocyclotin and Cyhexatin (sum ofazocyclotin and cyhexatin expressed ascyhexatin) Azoxystrobin Barban(F)BeflubutamidBenalaxyl including other mixtures ofconstituent isomers including benalaxyl-M(sum of isomers)Benfluralin (F)BenfuracarbBentazone (sum of bentazone and theconjugates of 6-OH and 8-OH bentazoneexpressed as bentazone) (R)Benthiavalicarb (Benthiavalicarb-isopropyl(KIF-230 R-L) and its enantiomer (KIF-230S-D) and diastereomers (KIF-230 R-L andKIF-230 S-D)Bifenazate Bifenox (F)Bifenthrin (F)Binapacryl (F)BiphenylBitertanol (F)Bixafen (R)Boscalid (F) (R)Bromide ionBromophos-ethyl Bromopropylate (F)农药通用中文名称最大残留限量[***********][***********]45双甲脒杀草强敌菌灵杀螨特磺草灵莠去津普鲁兰短梗霉菌株DSM14940 and DSM 14941(++)印楝素四唑嘧磺隆乙基谷硫磷甲基谷硫磷三唑锡和三环锡亚托敏燕麦灵氟丁酰草胺苯霜灵包括其他异构体的混合物包括间-苯霜灵(异构体的混合物)氟草胺丙硫克百威灭草松(苯达松)0.1*0.020.05*0.1*0.05*0.1*0.01*0.01*0.1*0.05*0.1*0.05*0.1*0.1*0.1*0.1*0.05*0.1 *0.1*[***********]555657苯噻菌胺联苯肼酯甲羧除草醚联苯菊酯乐杀螨、双苯唑菌醇联苯联苯三唑醇丙硫唑醇啶酰菌胺溴化物离子乙基溴硫磷溴螨酯0.01*0.02*0.05*50.1*0.05*0.1*0.01*0.5700.1*0.05*序号[***********][***********][***********][1**********]091农药通用英文名称农药通用中文名称最大残留限量0.1*0.05*0.05*0.05*0.02*0.05*0.01*0.1*0.1*0.05*0.05*0.1*0.05*0.05*0.05*0.05*0. 02*0.1*0.02*0.1*0.1*0.02*0.02500.1*0.05*0.1*0.1*0.1*0.02*0.1*0.05*0.1*0.1*Bromoxynil (bromoxynil including its esters溴苯腈expressed as bromoxynil) (F)糠菌唑(非对映异构体Bromuconazole (sum of diasteroisomers) (F)的混合物)Bupirimate 磺嘧菌灵、乙嘧酚磺酸Buprofezin (F)噻嗪酮Butralin 仲丁灵(地禾安)Butylate 丁草敌(苏达灭)硫线磷,克线丹CadusafosCamphechlor (Toxaphene) (F) (R)毒杀芬Captafol (F)敌菌丹Captan (R)克菌丹Carbaryl (F)胺甲萘Carbendazim and benomyl (sum of benomyl and多菌灵与苯菌灵carbendazim expressed as carbendazim) (R)双酰草胺(草长灭,长杀Carbetamide草)Carbofuran (sum of carbofuran and 3-虫螨威hydroxy-carbofuran expressed as carbofuran)Carbosulfan 丁硫克百威Carboxin 萎锈灵Carfentrazone-ethyl (determined ascarfentrazone and expressed as唑酮草酯carfentrazone-ethyl) Cartap 杀螟丹Chlorantraniliprole (DPX E-2Y45) (F)氯虫苯甲酰胺Chlorbenside (F)杀螨醚Chlorbufam 氯草灵Chlordane (sum of cis- and trans-chlrodane)氯丹(F) (R)Chlordecone (F)十氯酮Chlorfenapyr 虫螨腈Chlorfenson (F)杀螨酯Chlorfenvinphos (F)毒虫畏(氯芬磷)Chloridazon 氯草敏Chlormequat 矮壮素Chlorobenzilate (F)乙酯杀螨醇Chloropicrin 氯化苦(硝基氯仿)Chlorothalonil (R)百菌清Chlorotoluron 绿麦隆Chloroxuron (F)枯草隆(氯醚隆)Chlorpropham (chlorpropham and 3-chloroaniline, expressed as chlorpropham)氯普芬(F) (R)序号[***********][***********]6107108农药通用英文名称Chlorpyrifos (F)Chlorpyrifos-methyl (F)ChlorsulfuronChlorthal-dimethyl ChlorthiamidChlozolinate ChromafenozideCinidon-ethyl (sum of cinidon ethyl and itsE-isomer)Clethodim (sum of Sethoxydim and Clethodimincluding degradation products calculatedas Sethoxydim)Clodinafop and its S-isomers, expressed asclodinafop (F)Clofentezine(R)Clomazone Clopyralid ClothianidinCopper compounds (Copper)Cyanamide including salts expressed ascyanamide Cyazofamid农药通用中文名称毒死蜱甲基毒死蜱氯磺隆二甲基敌草索草克乐(2,6-二氯硫代苯甲酰胺)乙菌利环虫酰肼吲哚酮草酯烯草酮炔草酸四螨嗪氯胺T(异恶草松)二氯吡啶酸(古草立可尼丁铜化合物(铜制剂)氰胺氰霜唑(氰唑磺菌胺)环丙酸酰胺(环烷基酰苯胺)最大残留限量0.1*0.1*0.05*0.05*0.05*0.1*0.02*0.1*0.10.05*0.05*0.02*0.50.7400.1*0.02*0.1*109Cyclanilide (F)Cycloxydim including degradation andreaction products which can be determinedas 3-(3-thianyl)glutaric acid S-dioxide (BH517-TGSO2) and/or 3-hydroxy-3-(3-thianyl)glutaric acid S-dioxide (BH 517-5-OH-TGSO2) or methyl esters thereof,calculated in total as cycloxydimCyflufenamid: sum of cyflufenamid (Z-isomer) and its E-isomerCyfluthrin (cyfluthrin including othermixtures of constituent isomers (sum ofisomers)) (F)Cyhalofop-butyl (sum of cyhalofop butyl andits free acids)CymoxanilCypermethrin (cypermethrin including othermixtures of constituent isomers (sum ofisomers)) (F)Cyproconazole (F)110噻草酮(噻环定、草噻喃)0.05*[***********]环氟菌胺氟氯氰菊酯氰氟草酯霜脲氰(酰脲氰)氯氰菊酯环丙唑醇0.05*0.1*0.05*0.05*0.50.05*序号农药通用英文名称农药通用中文名称嘧菌环胺环丙氨嗪(灭蝇胺、环丙马秦)滴滴涕(DDT)二硝基甲酚(DNOC)茅草枯丁酰肼(二甲基琥珀酰肼)福美甲酯(棉隆)溴氰菊酯甜菜安(双苯胺灵)燕麦敌敌匹硫磷麦草畏敌草腈2,4-滴丙酸敌敌畏二氯苯氧基丙酸(禾草灵)氯硝胺(二氯硝基苯开乐散乙霉威苯醚甲环唑(恶醚唑)二氟苯隆(除虫脲)吡氟酰草胺(普草克)二甲草胺(油菜安)噻吩草胺-P噻节因乐果烯酰吗啉醚菌胺(嘧菌胺)烯唑醇消螨普地乐酚最大残留限量0.05*0.05*0.2*0.1*0.10.1*0.02*50.1*0.1*0.05*0.05*0.05*0.10.02*0.05*0.01*200.05*0.05*0.10.05*0.02*0.02*0.1*0.05*0.05*0.01*0.05*0.1*0.1*117Cyprodinil (F) (R)118Cyromazine[***********][***********][***********][***********][**************]DDT (sum of p,p´-DDT, o,p´-DDT, p-p´-DDEand p,p´-TDE (DDD) expressed as DDT) (F)DNOC DalaponDaminozide (sum of daminozide and 1,1-dimethyl-hydrazine, expressed asdaminazide)Dazomet (Methylisothiocyanate resultingfrom the use of dazomet andmetam)Deltamethrin (cis-deltamethrin) (F)Desmedipham Diallate Diazinon(F)Dicamba DichlobenilDichlorprop: sum of dichlorprop (includingdichlorprop-P) and its conjugates,expressed as dichlorpropDichlorvosDiclofop (sum diclofop-methyl and diclofopacid expressed as diclofop-methyl)DicloranDicofol (sum of p, p´ and o,p´ isomers) (F)Diethofencarb DifenoconazoleDiflubenzuron (F) (R)Diflufenican DimethachlorDimethenamid-p (dimethenamid-p includingother mixtures of constituent isomers (sumof isomers))DimethipinDimethoate (sum of dimethoate and omethoateexpressed as dimethoate)Dimethomorph (sum of isomers)Dimoxystrobin DiniconazoleDinocap (sum of dinocap isomers and theircorresponding phenols expressedas dinocap)(F)Dinoseb序号148Dinoterb 149Dioxathion农药通用英文名称农药通用中文名称地乐消酚(特乐酚)敌噁磷(敌杀磷、二恶硫磷)二苯胺敌草快乙拌磷二氰蒽醌(二噻农、二腈蒽醌)二硫代氨基甲酸酯类(以CS2表示的二硫代氨基甲酸酯类,包括代森锰、代森锰锌、代森联、丙森锌、福美双及福最大残留限量0.1*0.1*0.05*0.1*0.05*0.01*150Diphenylamine 151DiquatDisulfoton (sum of disulfoton, disulfoton152sulfoxide and disulfoton sulfone expressedas disulfoton) (F)153DithianonDithiocarbamates (dithiocarbamatesexpressed as CS2, including maneb,154mancozeb, metiram, propineb, thiram andziram)0.1*Diuron (including all components containing1553,4-dichloraniline moiety expressed as 3,4敌草隆dichloraniline) 156Dodine 多果定(十二烷基胍)菌草敌,扑草灭,N,N-157EPTC (ethyl dipropylthiocarbamate)二丙基硫赶氨基甲酸S-Emamectin benzoate B1a, expressed as甲胺基阿维菌素苯甲酸158emamectin 盐Endosulfan (sum of alpha- and beta-isomers硫丹(包括α、β以及有效成分为硫丹的硫丹硫159and endosulfan-sulphate expresses as酸酯的总和)(F)endosulfan) (F)160Endrin (F)异狄氏剂161Epoxiconazole (F)氟环唑162Ethalfluralin 丁氟消草(乙丁烯氟灵)163Ethametsulfuron-methyl 油磺,隆胺苯磺隆164Ethephon 乙烯磷,乙烯利165Ethion 乙硫磷166Ethirimol 乙嘧酚,乙菌定Ethofumesate (sum of ethofumesate and themetabolite 2,3-dihydro-3,3-dimethyl-2-oxo-乙氧呋草黄,灭草呋喃167benzofuran-5-yl methane sulphonate、甜菜呋expressed asethofumesate)168Ethoprophos 灭线磷169Ethoxyquin (F)乙氧喹啉,促长啉170Ethoxysulfuron 乙氧嘧磺隆,嘧啶磺隆Ethylene oxide (sum of ethylene oxide and1712-chloro-ethanol expressed as ethylene环氧乙烷或氧化乙烯oxide) (F)172Etofenprox (F)醚菊酯0.10.2*0.05*0.02*300.01*0.05*0.02*0.02*0.1*30.05*0.1*0.02*0.05*0.1*0.2*0.01*序号[1**********]6农药通用英文名称农药通用中文名称乙螨唑土菌灵恶唑菌酮咪唑菌酮苯线磷氯苯嘧啶醇喹螨醚分菌氰唑(腈苯唑:杀真菌剂)苯丁锡(托尔克六苯丁锡氧)皮蝇磷,皮蝇硫磷环酰菌胺杀螟硫磷精恶唑禾草灵苯氧威甲氰菊酯苯锈啶丁苯吗啉胺苯吡菌酮唑螨酯倍硫磷(倍硫磷和其氧化相似物,及其亚硫和硫化物)三苯基乙酸锡(F)(R)毒菌锡(羟基三苯锡)氰戊菊酯和高效氰戊菊酯(RR和SS异构体)氰戊菊酯和高效氰戊菊酯(RS和SR异构体)氟虫腈(含氟虫腈和以其表达的硫代物)勿拉莠,啶嘧磺隆农药/除草剂最大残留限量150.05*0.05*0.05*0.05*0.05*100.05*0.1*0.1*0.1*0.05*0.10.05*20.05*0.10.01*0.10. 05*0.1*0.1*0.05*0.05*0.005*0.02*0.05*0.1*0.1Etoxazole Etridiazole Famoxadone FenamidoneFenamiphos (sum of fenamiphos and its177sulphoxide and sulphone expressed asfenamiphos) 178Fenarimol 179Fenazaquin 180Fenbuconazole 181Fenbutatin oxide (F)[***********][***********][1**********]7Fenchlorphos (sum of fenchlorphos andfenchlorphos oxon expressed asfenchlorphos) Fenhexamid Fenitrothion Fenoxaprop-P Fenoxycarb FenpropathrinFenpropidin (sum of fenpropidin and itssalts, expressed as fenpropidin) (R)Fenpropimorph (R)FenpyrazamineFenpyroximate (F)Fenthion (fenthion and its oxigen analogue,their sulfoxides and sulfone expressed asparent) (F)Fentin acetate (F) (R)Fentin hydroxide (F) (R)Fenvalerate and Esfenvalerate (Sum of RR &SS isomers) (F)Fenvalerate and Esfenvalerate (Sum of RS &SR isomers) (F)Fipronil (sum fipronil + sulfone metabolite(MB46136) expressed as fipronil) (F)198Flazasulfuron 199Flonicamid (sum of flonicamid, TNFG and氟啶虫酰胺TNFA) (R)200Florasulam 双氟磺草胺Fluazifop-P-butyl (fluazifop acid (free and201精吡氟禾草灵conjugate))序号[***********][***********][***********][***********]226227农药通用英文名称Fluazinam (F)Flubendiamide (F)FlucycloxuronFlucythrinate (F) (R)FludioxonilFlufenacet (sum of all compounds containingthe N fluorophenyl-N-isopropyl moietyexpressed as flufenacet equivalent)Flufenoxuron (F)FlufenzinFlumioxazine Fluometuron Fluopicolide Fluopyram (R)Fluoride ionFluoroglycofene FluoxastrobinFlupyrsulfuron-methyl Fluquinconazole (F)FlurochloridoneFluroxypyr (fluroxypyr including its estersexpressed as fluroxypyr)(R)Flurprimidole FlurtamoneFlusilazole (F) (R)Flutolanil Flutriafol Fluxapyroxad Folpet (R)农药通用中文名称氟啶胺,福帅得氟虫酰胺,格列本脲氟螨脲,氟虫脲氟氰戊菊酯咯菌腈,氟咯菌腈氟噻草胺,苯噻酰草胺氟虫脲氟螨嗪丙炔氟草胺,速收伏草隆,氟硫隆氟啶酰菌胺氟吡菌酰胺氟离子乙羧氟草醚嘧菌酯氟啶嘧磺隆氟喹唑氟咯草酮氟草烟抑嘧醇呋草酮氟硅唑(F)(R)纹枯胺(氟酰胺)粉唑醇氟唑菌酰胺灭菌丹除豆莠(虎威),氟磺胺草醚酰胺磺隆氯吡脲伐虫脒安果磷(安果),安硫磷三乙磷铝噻唑磷麦穗宁,呋喃基苯并咪呋线威糠醛赤霉酸,赤霉烯酸最大残留限量0.05*0.02*0.05*0.1*0.05*0.05*150.1*0.1*0.02*0.02*0.01*3500.02*0.1*0.05*0.05*0. 1*0.1*0.02*0.05*0.05*0.05*0.05*0.01*0.05*0.05*0.05*0.05*0.05*0.05*5*0.05*0.05* 0.05*15228Fomesafen229Foramsulfuron 230ForchlorfenuronFormetanate: Sum of formetanate and its231salts expressed asformetanate(hydrochloride)232FormothionFosetyl-Al (sum fosetyl + phosphorous acid233and their salts, expressed as fosetyl)234Fosthiazate 235Fuberidazole236Furathiocarb 237Furfural238Gibberellic acid序号农药通用英文名称Glufosinate-ammonium (sum of glufosinate,its salts, MPP and NAG expressed asglufosinate equivalents)Glyphosate GuazatineHalosulfuron methylHaloxyfop including haloxyfop-R (Haloxyfop-R methyl ester, haloxyfop-R and conjugatesof haloxyfop-R expressed as haloxyfop-R)(F) (R)Heptachlor (sum of heptachlor andheptachlor epoxide expressed as heptachlor)(F)Hexachlorobenzene (F)Hexachlorociclohexane (HCH), sum ofisomers, except the gamma isomerHexaconazole Hexythiazox Hymexazol Imazalil Imazamox Imazapic Imazaquin Imazosulfuron ImidaclopridIndoxacarb (sum of indoxacarb and its Renantiomer) (F)Iodosulfuron-methyl (iodosulfuron-methylincluding salts, expressed as iodosulfuron-methyl)Ioxynil ( sum of Ioxynil, its salts and itsesters, expressed as ioxynil (F))Ipconazole Iprodione (R)Iprovalicarb Isoprothiolane Isoproturon Isopyrazam IsoxabenIsoxaflutole (sum of isoxaflutole and RPA202248, expressed as isoxaflutole)Kresoxim-methyl (F) (R)LactofenLambda-Cyhalothrin (F) (R)农药通用中文名称草丙磷铵(草胺磷、草丁磷)草甘膦双胍辛胺,双胍盐氯吡氯磺隆吡氟氯禾灵最大残留限量[**************]0.1*20.1*0.02*0.05[***********][***********][***********][***********]268269七氯六氯代苯六六六六那唑(已唑醇)噻螨酮甲羟异唑,恶霉灵抑霉唑甲氧咪草烟甲咪唑烟酸灭草喹,咪唑喹啉酸咪唑磺隆,唑吡嘧磺隆吡虫啉茚虫威(S和R异构体)甲基碘磺隆碘苯腈种菌唑异菌脲(R)丙森锌稻瘟灵异丙隆—异恶草胺,异噁草胺异恶唑类,异恶唑草酮亚胺菌乳氟乐草灵,乳氟禾草高效氯氟氰菊酯0.02*0.020.02*0.05*40.05*0.1*0.1*0.01*0.05*0.02*0.05*0.05*0.05*0.1*0.02*0.1*0. 1*0.01*0.1*0.01*0.02*0.1*0.1*0.05*1序号农药通用英文名称农药通用中文名称环草定林丹利谷隆虱螨脲二甲四氯和二甲四氯丁酸马拉硫磷马来酰肼双炔酰菌胺灭蚜磷2-甲-4-氯丙酸(含精2甲4氯丙酸和2甲4氯丙嘧菌胺甲哌鎓,甲哌啶担菌宁敌螨普汞化合物甲磺胺磺窿硝磺酮氰氟虫腙甲霜灵和甲霜灵-M蜗牛敌,四聚乙醛苯嗪草酮吡唑草胺叶菌唑,羟菌唑噻唑隆,甲基苯噻隆虫螨畏杀螨隆,甲胺磷杀扑磷最大残留限量0.1*0.05*0.1*0.02*0.1*0.50.5*0.02*0.1*0.1*270LenacilLindane (Gamma-isomer of271hexachlorociclohexane (HCH)) (F)272Linuron273Lufenuron(F)MCPA and MCPB (MCPA, MCPB including their274salts, esters and conjugates expressed asMCPA) (F) (R)Malathion (sum of malathion and malaoxon275expressed as malathion)276Maleic hydrazide (R)277Mandipropamid 278MecarbamMecoprop (sum of mecoprop-p and mecoprop279expressed as mecoprop)Mepanipyrim (Mepanipyrim and its metabolite(2-anilino-4(2-hydroxypropyl)-6-280methylpyrimidine), expressed asmepanipyrim) 281Mepiquat 282MepronilMeptyldinocap (sum of 2,4 DNOPC and 2,4283DNOP expressed as meptyldinocap)Mercury compounds (sum of mercury compounds284expressed as mercury) (F)Mesosulfuron-methyl expresssed as285mesosulfuronMesotrione (Sum of mesotrione and MNBA (4-286methylsulfonyl-2-nitro benzoic acid),expressed as mesotrione)287Metaflumizone (sum of E- and Z- isomers)Metalaxyl and metalaxyl-M (metalaxylincluding other mixtures of constituent288isomers including metalaxyl-M (sum ofisomers)) 289Metaldehyde290Metamitron 291Metazachlor 292Metconazole (F)293Methabenzthiazuron294Methacrifos (F)295Methamidophos 296Methidathion0.02*0.1*0.05*0.1*0.02*0.02*0.1*0.1*0.1*0.10.1*0.2*0.02*0.05*0.1*0.05*0.1*序号农药通用英文名称Methiocarb (sum of methiocarb andmethiocarb sulfoxide and sulfone, expressedas methiocarb)Metholachlor and metholachlor-S(metholachlor including other mixtures ofconstituent isomers including S-metholachlor (sum of isomers))Methomyl and Thiodicarb (sum of methomyland thiodicarb expressed as methomyl)MethopreneMethoxychlor (F)Methoxyfenozide (F)Metosulam Metrafenone MetribuzinMetsulfuron-methylMevinphos (sum of E- and Z-isomers)Milbemectin (sum of MA4+8,9Z-MA4, expressedas milbemectin) (R)MolinateMonocrotophos Monolinuron MonuronMyclobutanyl (R)Napropamide Nicosulfuron Nicotine Nitrofen (F)Novaluron (F)Orthosulfamuron Oryzalin Oxadiargyl Oxadiazon Oxadixyl OxamylOxasulfuron OxycarboxinOxydemeton-methyl (sum of oxydemeton-methyland demeton-S-methylsulfone expressed asoxydemeton-methyl) Oxyfluorfen Paclobutrazol ParaquatParathion (F)农药通用中文名称最大残留限量297甲硫威0.1*298异丙甲草胺和S异丙甲草胺灭多威灭幼宝,甲氧普烯,烯虫异丙甲草胺甲氧虫酰肼磺草唑胺依他苯酮,四嗪酮嗪草酮甲磺隆速灭磷弥拜菌素草达灭久效磷绿谷隆灭草隆腈菌唑敌草胺烟嘧磺隆尼古丁,烟碱除草醚杀虫剂敌草胺嘧苯胺磺隆氨磺乐灵丙炔恶草酮恶草酮恶唑烷酮 (恶霜灵)杀线威环氧嘧磺隆氧化萎锈灵砜吸磷(乙酰甲胺磷)乙氧氟草醚多效唑百草枯对硫磷0.1*[***********][***********][***********][***********][***********]3293303310.1*0.1*0.1*0.05*0.01*0.05*0.1*0.1*0.02*0.1*0.1*0.05*0.1*0.05*0.050.05*0.05*0.60.02*0.01*0.01*0.02*0.05*0.05*0.02*0.02*0.1*0.05*0.05*0.05*0.02*0.05*0.1*序号农药通用英文名称Parathion-methyl (sum of Parathion-methyland paraoxon-methyl expressed as Parathion-methyl)Penconazole (F)Pencycuron (F)Pendimethalin (F)Penoxsulam PenthiopyradPermethrin (sum of isomers)Pethoxamid农药通用中文名称最大残留限量[***********]338339甲基对硫磷戊菌唑戊菌隆二甲戊乐灵(胺硝草)五氟磺草胺吡噻菌胺氯菊酯烯草胺甲双苯胺灵(苯敌草-乙酯)苯醚菊酯甲拌磷伏杀硫磷亚胺硫磷磷胺磷化氢&磷化物辛硫磷氨氯吡啶酸(毒莠定)氟吡草胺(普草克)啶氧菌酯唑啉草酯抗蚜威甲基嘧啶磷抗蚜威腐霉利丙溴磷环苯草酮调环酸毒草胺0.05*0.10.05*0.1*0.02*0.02*0.1*0.02*0.1*0.05*0.05*0.05*0.1*0.02*0.050.10.01*0. 1*0.1*0.05*0.05*0.05*0.1*0.05*0.05*0.1*0.1*0.1*340Phenmedipham (R)341PhenothrinPhorate (sum of phorate, its oxygen342analogue and their sulfones expressed asphorate) 343PhosalonePhosmet (phosmet and phosmet oxon expressed344as phosmet) (R)345PhosphamidonPhosphines and phosphides:sum of aluminiumphosphide, aluminium phosphine, magnesium346phosphide, magnesium phosphine, zincphosphide and zinc phosphine347Phoxim (F)348Picloram 349Picolinafen350Picoxystrobin (F)351PinoxadenPirimicarb: sum of pirimicarb and desmethyl352pirimicarb expressed as pirimicarb353Pirimiphos-methyl (F)Prochloraz (sum of prochloraz and itsmetabolites containing the 2,4,6-354Trichlorophenol moiety expressed asprochloraz)355Procymidone (R)356Profenofos (F)357ProfoxydimProhexadione (prohexadione (acid) and its358salts expressed as prohexadione-calcium)Propachlor: oxalinic derivateof359propachlor, expressed as propachlor序号360农药通用英文名称农药通用中文名称霜霉威二氯丙酰苯胺(敌稗)喔草酯克螨特(灭虫醚、杀螨净、丙炔螨特)苯胺灵丙环唑丙森锌异丙草胺残杀威丙苯磺隆炔苯酰草胺丙氧喹啉苄草丹氟磺隆(三氟丙磺隆)丙硫菌唑吡嗪酮唑菌胺酯吡草醚磺酰草吡唑定菌磷除虫菊酯哒螨灵啶虫丙醚最大残留限量0.2*0.1*0.05*50.1*0.1*0.10.01*0.1*0.05*0.05*0.05*0.05*0.1*0.02*0.1*0.05*0.05*0 .02*0.1*0.50.05*0.02*Propamocarb (Sum of propamocarb and itssalt expressed aspropamocarb)361Propanil362Propaquizafop 363Propargite (F)[***********][***********][***********]382383[***********]390391ProphamPropiconazolePropineb (expressed as propilendiamine)Propisochlor PropoxurPropoxycarbazone (propoxycarbazone, itssalts and 2-hydroxy-propoxy-propoxycarbazone, calculated aspropoxycarbazone) Propyzamide (F)(R)Proquinazid Prosulfocarb ProsulfuronProthioconazole (Prothioconazole-desthio)(R)PymetrozinePyraclostrobin (F)Pyraflufen-ethyl Pyrasulfotole Pyrazophos (F)Pyrethrins Pyridaben (F)PyridalylPyridate (sum of pyridate, its hydrolysisproduct CL 9673 (6-chloro-4-hydroxy-3-phenylpyridazin) and hydrolysableconjugates of CL 9673 expressed aspyridate) Pyrimethanil Pyriproxyfen (F)Pyroxsulam Quinalphos Quinclorac QuinmeracQuinoxyfen (F)Quintozene (sum of quintozene andpentachloro-aniline expressed asquintozene) (F)哒草特0.1*乙胺嘧啶吡丙醚啶磺草胺喹硫磷二氯喹啉酸氯甲喹啉酸异丁乙氧喹啉五氯硝基苯0.1*0.05*0.02*0.1*0.05*0.1*0.050.1*序号农药通用英文名称农药通用中文名称喹禾灵苄呋菊酯砜嘧磺隆鱼藤酮硅噻菌胺西玛津乙基多杀菌素多杀菌素螺螨酯螺甲螨酯螺虫乙酯螺环菌胺磺草酮磺酰磺隆硫酰氟硫磺特普,焦磷酸四乙酯氟胺氰菊酯;马扑立克戊唑醇虫酰肼,灭虫灭死丁基嘧啶磷吡螨胺噻草啶伏虫隆七氟菊酯环己二酮类化合物吡喃草酮特丁硫磷特丁津四氟醚唑三氯杀螨砜噻菌灵噻虫啉噻虫嗪噻酚磺隆硫双威甲基硫菌灵福美双最大残留限量0.05*0.2*0.1*0.02*0.1*0.05*0.1*0.05*0.05*0.02*0.1*0.1*0.05*0.1*0.02*50.02*0.01 *0.05*0.10.10.1*0.05*0.050.05*0.1*0.01*0.05*0.02*0.05*0.1*10200.1*0.1*0.1*0.2*392Quizalofop, incl. quizalfop-PResmethrin (resmethrin including other393mixtures of consituent isomers (sum ofisomers)) (F)394Rimsulfuron 395Rotenone 396Silthiofam 397Simazine398Spinetoram (XDE-175)Spinosad: sum of spinosyn A and spinosyn D,399expressed as spinosad (F)400Spirodiclofen (F)401SpiromesifenSpirotetramat and its 4 metabolitesBYI08330-enol, BYI08330-ketohydroxy,402BYI08330-monohydroxy, and BYI08330 enol-glucoside, expressed as spirotetramat (R)403Spiroxamine (R)404Sulcotrione 405Sulfosulfuron 406Sulfuryl fluoride407Sulphur 408TEPP409Tau-Fluvalinate (F)410Tebuconazole 411Tebufenozide (F)412Tebufenpyrad (F)413Tecnazene (F)414Teflubenzuron 415Tefluthrin (F)416Tembotrione(R)417Tepraloxydim 418Terbufos419Terbuthylazine 420Tetraconazole (F)421Tetradifon422Thiabendazole (R)423Thiacloprid (F)Thiamethoxam (sum of thiamethoxam and424clothianidin expressed as thiamethoxam)425Thifensulfuron-methyl426Thiobencarb427Thiophanate-methyl (R)428Thiram (expressed as thiram)序号农药通用英文名称农药通用中文名称甲基立枯磷甲苯氟磺胺苯吡唑草酮三甲苯草酮/脱莠定/肟草酮野麦畏三唑酮醚苯磺隆三唑磷苯磺隆敌百虫绿草定三环唑十三吗啉肟菌酯最大残留限量0.1*0.1*0.02*0.05*0.1*0.2*0.1*0.02*0.02*0.05*0.1*0.05*0.05*0.05*429Tolclofos-methylTolylfluanid (Sum of tolylfluanid and430dimethylaminosulfotoluidide expressed astolylfluanid) (R)431Topramezone (BAS 670H)432Tralkoxydim433Tri-allateTriadimefon and triadimenol (sum of434triadimefon and triadimenol) (F)435Triasulfuron 436Triazophos(F)437Tribenuron-methyl 438Trichlorfon 439Triclopyr 440Tricyclazole441Tridemorph (F)442Trifloxystrobin (F) (R)Triflumizole: Triflumizole and metaboliteFM-6-1(N-(4-chloro-2-443trifluoromethylphenyl)-n-propoxyacetamidine), expressed asTriflumizole (F)444Triflumuron (F)445Trifluralin 446Triflusulfuron 447TriforineTrimethyl-sulfonium cation, resulting from448the use of glyphosate (F)449Trinexapac 450Triticonazole 451Tritosulfuron 452ValifenalateVinclozolin (sum of vinclozolin and allmetabolites containing the 3,5-453dichloraninilinemoiety, expressed asvinclozolin) (R)454Ziram 455Zoxamide氟菌唑0.1*杀虫隆氟乐灵氟胺磺隆嗪氨灵硼酸三甲酯抗倒酯灭菌唑三氟甲磺隆啶虫醚乙烯菌核利福美锌苯酰菌胺0.05*0.05*0.05*0.05*0.05*0.05*0.02*0.02*0.02*0.1*0.2*0.05*。
国家农药残留限量标准与绿色食品标准、CAC标准的差异分析孙钰洁;王磊【摘要】以常见的10种农产品为分析对象,对我国最新食品中农药最大残留限量标准(GB 2763—2016)和绿色食品标准、国际食品法典委员会(CAC)标准进行对比分析.通过分析数据找出目前我国农药最大残留限量标准存在的问题,并提出针对性的建议和措施.【期刊名称】《现代农药》【年(卷),期】2019(018)001【总页数】4页(P20-23)【关键词】农产品;农药残留;最大残留限量标准;绿色食品标准;国际食品法典委员会标准【作者】孙钰洁;王磊【作者单位】江苏省农产品质量检验测试中心,南京 210036;江苏省农产品质量检验测试中心,南京 210036【正文语种】中文【中图分类】TQ450.2+63《食品安全国家标准食品中农药最大残留限量》(GB 2763—2016)是我国最新版强制性国家标准,是判定食品安全的重要依据,是指导食品、农产品安全生产的重要技术指标,也是农产品、食品监管和执法的重要法定依据[1]。
绿色食品标准经过二十几年的发展,已形成了一套较为严密的标准体系,是目前我国最高的食品标准,代表了我国食品安全发展的方向[2]。
国际食品法典委员会(CAC)是由联合国粮农组织(FAO)和世界卫生组织(WHO)共同建立的政府间组织,它以保障消费者的健康和确保食品贸易公平为宗旨,主要工作是制定国际食品标准。
在相关食品标准制定方面,国际食品法典是唯一的、最重要的国际参考标准[3]。
国际食品法典委员会目前有180个成员国,覆盖全球98%的人口,中国于1984年正式加入CAC组织。
深入研究我国农药残留限量标准和CAC标准之间的差距,可以为我国标准修订提供参考,尽量缩小与国际标准的差距,有效应对农产品出口技术贸易壁垒。
1 10种我国常见农产品的国家标准和绿色食品标准、CAC标准农药残留限量值的对比分析选取了10种我国居民日常消费农产品,包括谷物、蔬菜、水果等,对这10种农产品的农药残留限量国家标准、相应绿色食品标准、CAC标准进行对比,结果见表1~表10。
气相色谱-氮磷检测器测定辣椒及其土壤中的霜霉威残留卢静宜;杨仁斌;傅强;蒋诗琪;欧阳文森【摘要】[目的]建立辣椒和土壤中霜霉威残留量的气相色谱-氮磷检测器(GC-NPD)测定方法.[方法]辣椒和土壤样品以丙酮与水(7∶3,V/V)混合溶液提取,经正己烷和二氯甲烷萃取净化后,用气相色谱-氮磷检测器测定,外标法定量.[结果]霜霉威在0.05 ~ 10.00mg/L范围内浓度和峰面积成良好的线性关系;方法的最低检测质量浓度为0.05 mg/kg;平均添加回收率为84.1%~96.3%,变异系数为0.8%~2.6%.[结论]该测定方法灵敏、稳定,符合农药残留分析方法的技术要求.【期刊名称】《安徽农业科学》【年(卷),期】2015(000)002【总页数】3页(P149-151)【关键词】霜霉威;辣椒;气相色谱-氮磷检测器;残留量分析方法【作者】卢静宜;杨仁斌;傅强;蒋诗琪;欧阳文森【作者单位】湖南农业大学农业环境保护研究所,湖南长沙410128;湖南农业大学农业环境保护研究所,湖南长沙410128;湖南化工研究院,湖南长沙410128;湖南农业大学农业环境保护研究所,湖南长沙410128;湖南农业大学农业环境保护研究所,湖南长沙410128【正文语种】中文【中图分类】S482.2霜霉威是一种具有局部内吸作用的低毒杀菌剂[1],属氨基甲酸酯类,对卵菌纲真菌有特效,广泛适用于黄茄、辣椒、莴苣、马铃薯等蔬菜及烟草、草莓、草坪、花卉卵菌纲真菌病害的防治,如霜霉病、猝倒病、晚疫病、黑胫病等。
我国已有许多厂家生产霜霉威,目前它是全球应用较广泛的杀菌剂之一。
国内外已建立对霜霉威的检测方法有高效液相色谱法(HPLC)[2]、超高效液相色谱与串联四级杆质谱联用法(UPLC/MS/MS)、气相色谱(GC)-氮磷检测(NPD)法和气相色谱(GC)-火焰离子化检测器(FID)法[3-7]。
目前已有霜霉威在黄瓜、烟草、菠菜、结球生菜和大葱等各类果蔬上的残留分析方法的研究报道[3-7],但关于霜霉威在辣椒上的残留量分析方法的研究尚未见报道。
产品名称 银法利INFINITO 687.5克/升悬浮剂(氟菌·霜霉威) 产品成分及含量 氟吡菌胺:6.25%,霜霉威盐酸盐:62.5%产品说明 该产品为低毒内吸性杀菌剂,由新的治疗性杀菌剂氟吡菌胺和内吸传导性杀菌剂霜霉威盐酸盐复配而成,既具有保护作用又具有治疗作用。
对马铃薯和番茄晚疫病、黄瓜和大白菜霜霉病、西瓜和辣椒疫病具有较好的防效。
该产品具有活性较高、持效期较长、内吸性较强、施药时间灵活的特点。
按照推荐方法施用,对作物安全。
产品包装 袋装25ml 、瓶装100ml 、1L特点说明● 独特性:混剂配方——氟吡菌胺+霜霉威盐酸盐● 保护性:较强的薄层穿透性,良好的系统传导性● 治疗性:对病原菌的各主要形态均有很好的抑制活性● 持效性:持效期长● 耐雨水冲刷,不受天气影响● 不留药渍● 低毒、低残留:完全符合食品产业链的需求● 对作物安全 使用方法适用作物防治对象 制剂用量 使用方法 番茄晚疫病 60-75毫升/亩 1. 配制药液时,向喷雾器中注入少量水,然后加入推荐用量的银法利制剂。
充分搅拌药液使之完全溶解后,加入足量水; 2. 据作物大小,按每亩推荐用药量,对水45~75升,进行叶面均匀喷雾处理; 3. 在病害发生初期进行叶面喷雾处理效果最佳,并可以降低用药量。
建议每隔7-10天施用一次。
大风天或预计1小时内降雨,请勿施药。
黄瓜霜霉病 60-75毫升/亩 大白菜霜霉病 60-75毫升/亩 辣椒疫病 60-75毫升/亩 西瓜疫病 60-75毫升/亩 马铃薯 晚疫病 60-75毫升/亩 注意事项说明 注意事项: 1.安全间隔期:黄瓜和番茄建议为3天;每季最多施用次数: 3次; 2.用药时应穿戴防护衣物,禁止吸烟、饮食; 3.施药后用肥皂和足量清水彻底清洗手和面部以及其它可能接触药液的身体部位;4.用药后的空包装应妥善安置于安全场所;5.禁止在河塘等水体中清洗施药工具;6.建议与不同作用机制杀菌剂轮换使用。
农药残留检测方法【定义】本药典中的农药系指用于保护,消灭或控制害虫的任意物质或混合物,其中,害虫是在中药的生产、加工、储存、运输和市场销售过程中对动植物造成危害的物种。
农药包括生长调节剂、脱叶剂、干燥剂或其他用于农作物丰收前后为保护农作物在贮存和运输中免于污染的物质。
【限量】除另有规定外,按表2.8.13-1的要求检查。
农药限量要求也包括它们的附加物和后续的衍生物,限量要求未列在表中的,但存在确实可疑的物质,可根据欧洲共同市场指示76/895和90/642的限量要求。
农药的限量要求未在表2.8.13-1,也没有欧洲共同市场指示要求的用下式计算:ADI×MMDD×100ADI = 日最大摄取量mg/kg(根据FAO-WHO要求)M = 体重kgMDD = 每千克体重平均每日剂量如果该药是用于制备提取液,酊剂或其他药剂,其制备方法可能会改变最后药品中农药含量,限量用下式计算:ADI×M×EMDD×100E = 制备方法的萃取因数由试验决定在特殊情况下,最高限量也是允许的,尤其当该植物使用特殊的种植方法,或有一种代谢物或它的结构使其高于农药限量的正常值。
如果该批中药的种植过程是清楚的,或者可以准确追踪的,也就是说农药的性质和用量,以及种植过程中使用农药的时间都是可是清楚的,监管部门可能会对这批中药全部或部分免检。
【取样】方法对于1kg装的,取样一份,充分混匀,取适量用于检查。
对于1kg至5kg装的,分别自容器顶部,中部,底部取等量样品一份,然后充分混匀后,取适量用于检查。
对于5kg以上容器装的,分别自容器顶部,中部,底部取不少于250g的样品,然后将样品充分混匀,取适量用于检测。
取样量如果容器的数量不多于三个,用上述方法从每个容器中取一份样。
如果容器的数量多于3个,用上述方法取n+1份样,如有必要,取近似整数单位。
为防止残留物降解,用于检测的样品取出后应尽快用于检测,否则,将样品置于密闭容器或食物容器中,在0℃下避光密闭保存。
利用气相色谱检测黄瓜果实中霜霉威的残留量马佰慧;秦志伟;谭行之【摘要】为了建立一种快速、准确测定黄瓜果实中霜霉威农药残留量的分析方法.采用将黄瓜果实经组织破碎,利用丙酮匀质提取,过脱水剂、硅化层析柱层析,旋转蒸发仪旋蒸近干,甲醇定容,用Rtx-1毛细色谱柱、FID检测器对其残留进行定量分析.结果表明,标样回收率为85%~94%,检出限为0.01 mg/kg.此方法可快速、准确的测定出瓜类中的霜霉威残留量.【期刊名称】《长江蔬菜》【年(卷),期】2010(000)020【总页数】3页(P51-53)【关键词】黄瓜;气相色谱;霜霉威;农药残留【作者】马佰慧;秦志伟;谭行之【作者单位】东北农业大学园艺学院,黑龙江哈尔滨,150030;东北农业大学园艺学院,黑龙江哈尔滨,150030;东北农业大学园艺学院,黑龙江哈尔滨,150030【正文语种】中文黄瓜霜霉病是黄瓜生产中的主要病害之一,其来势猛、传播快、为害重,能在1~2周内使植株大部分叶片枯死,造成严重减产,以致绝收[1]。
为了防治霜霉病,在生产上需使用大量农药,不仅提高了生产成本,也易造成农残量超标,为害消费者健康。
长期食用受污染蔬菜,是导致癌症、动脉硬化、心血管病、胎儿畸形、死胎、早夭、早衰等疾病的重要原因。
霜霉威(Propamocarb),是国内抑制霜霉病病害的主要喷洒类药剂之一,能够有效地抑制霜霉病的扩散,目前在生产上已广泛使用,因而选择一种快捷的方法定量分析黄瓜内霜霉威残留量尤为重要[2,3]。
本试验的目的就是建立一种快速、准确、经济、实用的黄瓜果实霜霉威残留量的检测方法。
1 材料与方法1.1 试验材料①试验样品供试材料D0313(腌渍型)、D0351(腌渍型)、D0328-6(欧洲鲜用型)、北进(华北型)、D9320-2(华南型)均是经过多代自交选育的自交系,由东北农业大学园艺学院黄瓜育种研究室提供。
②仪器设备岛津GC-2010气相色谱仪;岛津 Rtx-1 (30 m×0.25 mm×0.25μm)色谱柱;AOC-20i自动进样器;旋转蒸发仪;DY89-Ⅰ型高速玻璃均质器;Philips HR2860高速组织捣碎机,硅烷化白色担体玻璃层析柱(20 mm×20 cm),250 mL分液漏斗。
液相色谱-串联质谱法测定黄瓜中霜霉威残留潘艳坤;韦英亮【摘要】Sample of cucumber was extracted with acetonitrile, and the extract was purified by passing through the activated carbon SPE column and eluting with acetonitrile. The eluate was evaporated rotationally to near dryness, and made up its volume to 1. 0 mL with acetonitrile-H2O (1+1) solution. Hypersil GOLD C18 (2.0 mm×150 mm, 3 μm)chromatographic column was used for separation, using the mixed solutions of 10 mmol·L^-1 ammonium acetate (containing φ 0. 1% formic acid) and acetonitrile in different ratios as mobile phase in the gradient elution. ESI with positive ionization mode and select ion monitoring mode was used in the MS/ MS analysis. Linear relationship between values of peak area and mass concentration of propamocarb was found in the range of 1.02--1 020 μg ·L^-1, with lower limit of determination (lOS/N) of 0.2 μg ·L^-1. Test for recovery was made by standard addition method, giving values of recovery and RSDfs (n=6) in the ranges of 88%-96%and 4.7 %- 6.4 % respectively.%黄瓜样品经乙腈超声波提取后,用活性炭固相萃取小柱净化,用乙腈洗脱,将洗脱液旋转蒸发至近干,用乙腈-水(1+1)溶液1.0mL溶解测定。
719PROPAMOCARB (148)First draft prepared by Eloisa Dutra Caldas, University of Brasilia, Brasilia, BRAZIL EXPLANATIONPropamocarb hydrochloride is a carbamate fungicide with specific activity against Oomycete species that cause seed, seedling, root, foot and stem rots and foliar diseases in a number of edible crops. The compound was evaluated by the JMPR in 1984, 1986, 1987 and 2005, when an ADI of 0–0.4 mg/kg bw and an ARfD of 2 mg/kg bw were established. At the 37th Session of the CCPR it was scheduled for residue evaluation, within the periodic review programme, by the 2006 JMPR. The manufacturer submitted data on metabolism in animal and plants, degradation in soil, residues in succeeding crops; GAP, analytical methods and processing studies. Residue trials submitted were conducted on potato, radish, onion, lettuce, spinach, cabbage, cauliflower, chicory, sweet pepper, tomatoes, summer squash, cantloupe and melon. GAP information and residue trials results on lettuce, cucumber and ginger were provided by the Government of Japan.IDENTITYCommon name: Propamocarb hydrochlorideChemical name:IUPAC: Propyl 3-(dimethylamino) propylcarbamate hydrochlorideCAS: Propyl [3-(dimethylamino)propyl] carbamate hydrochloride CAS number: 25606-41-1CIPAC number: 399EEC number: 245-125-9Molecular formula:C9H21ClN202Molecular mass: 224.7 g/molStructural formula:H3NCH3NH O3x HClPHYSICAL AND CHEMICAL PROPERTIESA detailed chemical and physical characterisation of the active ingredient is given below.Property Results Reference Report No.Colour and odour Cream coloured sticky crystals with typicalcarbamate odour/white opaque crystalline softliquid with weak, sickly sweet odour (Sixl/Rexer, 1998; C001715/C001717; Walker et al., 1995; 722/013)Melting point 64.2°C (Lehne, 1990; A89312)Relative density 1.051 g/cm³ at 20°C/1.15 g/cm³ at 20.5 +0.5°C (Bittner/Rexer, C003480. Muehlberger andLemke, 2004; C044109. Walker et al., 1995;722/013)Vapour pressure (extrapolated) 3.8x10-5 / 1.4 x10-3 Pa at 20 °C8.1x10-5 / 1.7x10-3 Pa at 25 °C1.6x10-4 Pa at 30 °C(Miklautz, 1990; A85057; Howarth et al.,1995; 722/015)720PropamocarbPropertyResults Reference Report No.Volatility (calculated) Henry's law constant at 20 °C: 8.50 x 10-9 Pa m3mol-1(Renaud, 2005; C046819)Solubility in water at 20ºC > 900 g/L at pH 3> 855 g/L at pH 6.9> 536 g/L at pH 9.6between 89.2 and 93.5%w/w at pH 4between 89.1 and 93.8%w/w at pH 7between 89.6 and 94.6%w/w at pH 10(Muehlberger, 2001; C012641/C042353;Renaud, 2004; C045318 ; Walker et al.,1995 ; 722/013)Solubility in organic solvent [g/L] at 20°C s Hexane: < 0.01Toluene: 0.14Methanol: > 656Dichloromethane: > 626Ethyl acetate: 4.34 – 4.8Acetone: 560.3Xylene: 1.6x10-2Heptane: < 1x10-4(Müller, 1990; A85046; Walker et al., 1995;722/013; Ryckel, 2002; 20528)Dissociation constant pKa=9.3+ 0.03 at 20°CpKa=9.63+ 0.03 at 20°C (Miklautz, 1991; A85060; Poerschke, 2001; C014007; Walker et al., 1995; 722/013)Partition coefficient n-octanol/water Log Pow at 22°C = -2.87 (at pH 2),-1.21 (at pH 7) and 0.67 (at pH 9)Log Pow at 21-22°C = -0.98 (at pH 4),-1.36 (at pH 7) and 0.32 (at pH 9)(Muehlberger, 2004; C012642; Walker et al.,1995; 722/013)Hydrolysis rate < 10% hydrolysis after 5 days at 50°C at pH 4, 7and 9 (Shepler et al., 2001; B003419; Walker et al., 1995 ; 722/013)Photochemical degradation No photo degradation of propamocarb HCl inaqueous solution by irradiation with artificialsunlight during 22 days(Klehr, 2003; A85564/A85466; Mullee et al.1995; 722/014)METABOLISM AND ENVIRONMENTAL FATEAll the metabolism and environmental fate studies submitted to the Meeting were conducted with 14C-propamocarb hydrochloride labelled as shown on Figure 1.Parent compoundFigure 1. Position of 14C in propamocarb and the metabolites found in animals and plants.Animal metabolismRatFour studies conducted in rats with 14C-propamocarb hydrochloride were submitted to the Meeting (Reynolds, 1994, A85144; O’Boyle, 1994, A85146/A91169; Reynolds, 1994, A85148/ A91170;Propamocarb721 Morley, 1997, A8386, A84072/C000632). These studies were evaluated by the 2005 JMPR during the toxicological periodic review of propamocarb, and are detailed in the 2005 JMPR Toxicology Evaluation and Report. In summary, propamocarb was rapidly absorbed and extensively metabolised in rat, with no accumulation of parent compound or metabolites in tissues, which are mainly excreted in urine and faeces. Half-life for all tissues ranged from 11–26 hours, with 3 to 20% of the applied dose being excreted as parent compound. The proposed metabolism of propamocarb hydrochloride in the rat involved aliphatic oxidation of the propyl chain, N-oxidation of the tertiary amine and N-dealkyation. Four major metabolites were identified: 2-hydroxy propamocarb, mono-N-desmethyl propamocarb (AEB132677), propylpropamocarb N-oxide (Met IV) and the cyclic propamocarb oxazolidin-2-one (Met VI). There was no evidence of conjugation with glucuronic or sulfuric acid.LivestockA lactating cow was orally dosed twice daily for seven consecutive days at a dose level equal to 11.5 mg/kg [14C]-propamocarb HCl equivalents in the diet. Based on dry weight of feed, this corresponds to 2.0 mg propamocarb HCl/kg body weight per day (Daniel and Rupprecht, 2000; B002935). Milk, faeces and urine were collected twice a day during the treatment period. Approximately 15 hours after the last dose, the cow was sacrificed and edible tissues (liver, kidney, muscle, fat and bile) were collected.Samples of kidney, liver, and muscle were extracted 6 to 8 times with acidified methanol. Radioactivity in the extracts was directly counted by liquid scintillation counting (LSC). Total radioactive residues (TRR) in fat was 0.002 mg/kg propamocarb HCl eq. and no further extraction was performed. Liver and kidney extracts were directly subject to chromatography, but muscle extracts were ‘de-fatted’ previously with hexane. Milk was extracted with hexane to remove the fat before being dialysed with water. Faeces were extracted with acidic methanol followed by soxhlet extraction with acidic methanol. Identification and quantification of the metabolites in the extracted residue was accomplished by reverse phase and cation exchange HPLC. Samples were analyzed within 2−6 months after collection.The majority of the administered dose was excreted (81.4%), via the urine (71.9%) and the faeces (9.5%). An overall recovery (including stall wash) of 82.9% of the administered dose was achieved. The residues in the milk were always higher in the afternoon, with a mean of 0.054 ± 0.008 mg/kg propamocarb HCl eq (n=7), and a maximum of 0.057 mg/kg on Day 6 than in the morning (mean: 0.035 ± 0.003 mg/kg propamocarb HCl eq. (n=7) and the maximum of 0.037 mg/kg on Day 5). Cumulative radioactivity recovered in the milk (0.599 mg/kg) accounted for 0.46% of the administered dose. TRR found in tissues and bile accounted for 0.7% of the administered dose. Radioactivity found in tissues, milk and faeces are summarized in Tables 1 and 2. Unextracted residues were not analyzed further.Table 1. Extractability of residues in tissues, milk and faeces.MatrixTRR Extracted Residue Unextracted Residuemg/kg a %TRR mg/kg a%TRR mg/kg a Kidney 0.107 92.5 0.099 7.2 0.008 Liver 0.415 96.4 0.4 3.6 0.015Milk b 0.057 100 0.057 NA NA Muscle 0.019 83.2 0.016 16.8 0.003Milk fat b < 0.01 NA NA NA NA Faeces c NA 93.6 - 6.3 -a. Expressed as propamocarb HCl equivalents;b. sample from day 6 afternoon;c. days 4 and 5; NA= not analysed722PropamocarbThe majority of the residue comprised propamocarb, propamocarb N-oxide (Met IV), and the cyclic propamocarb oxazolidin-2-one (Met VI). Minor amounts of 2-hydroxy propamocarb and desmethyl propamocarb (AE B132677) were also identified (Table 2; Figure 1). The majority of the residue was identified in all matrices.Table 2. Summary of metabolite identification in tissues, milk and excreta.Propamocarb Propylpropamocarb N-oxide (Met IV) Propamocarboxazolidin-2-one (Met VI)2-HydroxypropamocarbN-desmethylpropamocarbIdentified%TRR mg/kg %TRR mg/kg %TRR mg/kg %TRR mg/kg %TRR mg/kg %TRR mg/kg Kidney 23.5 0.025 40.8 0.044 14.1 0.015 13 0.014 nd nd 91.4 0.098 Liver 6.2 0.026 49.0 0.203 21.7 0.09 4.8 0.02 nd nd 81.7 0.339 Milk 6.0 0.003 21.3 0.012 23.4 0.014 37.6 0.022 3.4 0.002 91.7 0.053 Muscle 24.6 0.005 40.5 0.008 2.3 < 0.001 0.9 < 0.001 4.1 0.001 72.4 0.014 Faeces 33.7 NA 24.6 NA 2.0 NA 13.1 NA 7.6 NA 81 NA Urine 1.2 NA 28.2 NA 59.0 NA 9.9 NA NA NA 98.3 NA Figure 2 shows the proposed metabolic pathway for propamocarb hydrochloride in the cow. The compound is oxidised or N-demethylated at the di-methyl amine group, or is hydroxylated at the propyl side chain, with the subsequent cyclization to form propamocarb oxazolidin-2-one(metabolite VI).Met VI (AE B132679)2-hydroxy propamocarb AE B132677PropamocarbMet IV (AE B155306)N-demethylationN N OH3CON N OH3CH3OHN N OH3CH3OH OH3N+N O-OH3CH3CN N OH3CH3OFigure 2. Proposed metabolic pathway of propamocarb hydrochloride in the cow.Propamocarb723 Plant metabolismSpinachIn a study conducted in USA in 2000, [14C]-propamocarb HCl was applied twice to spinach by foliar spray at a rate of 2.53 kg ai/ha (Rupprecht and Daniel, 2000; B002936).Duplicate samples were harvested immediately following the 1st application (day 0), just prior to the second application (Day 20) and 3 days after the second application (Day 23). Samples were extracted three times with methanol/1M hydrochloric acid (99:1), the extract filtered and the 14C content determined by LSC. The filter cake was extracted with acidic methanol in a soxhlet system. Sample extracts were analysed by HPLC and TLC using a radioactive detector. Propamocarb and a selected number of targeted metabolites were used as external standards to identify the residues present. The results are presented in Table 3. Propamocarb was the main residues found in all samples collected.Table 3. Distribution of metabolites in spinach extracts.Sample time TRR,mg/kg aPropamocarb,%TRRPropylpropamocarbN-oxide(MetIV),%TRRPropamocarboxazolidin-2-one (MetVI),%TRR2-Hydroxypropamocarb,%TRRN-desmethylpropamocarb,%TRRTotalidentified,%TRRDay 0 203.0 89.2 2.2 1.8 0.0 0.0 93.2 Day 20 207.3 76.0 3.5 2.6 7.1 3.6 92.7 Day 23 236.9 83.1 3.6 2.8 5.4 1.1 96.1a. Expressed as propamocarb HCl equivalents; mean values from duplicate samplesLettuceIn one study conducted in UK in 2002, [14C]-Propamocarb HCl (>98% radiochemical purity) was applied (a) to soil on which lettuce was grown three times at 7.22 g ai/m2, corresponding to 72.2 kg ai/ha. immediately after sowing and at intervals of 14 and 28 days thereafter, and (b) three times as a foliar spray in a greenhouse at 1.08 kg ai/ha with 10 day intervals (Goodyear, 2002a; 16669/6-D2149).Plants were harvested at mature size 38 days after the final soil treatment and 21 days after final foliar treatment. Samples were homogenized in dry ice and stored frozen until analyzed. Portions (approximately 20g) of the homogenates were extracted with methanol, the extracts centrifuged and the radioactivity present determined by LSC. The plant residue remaining was air-dried and the unextracted radioactivity determined by LSC following combustion. The results are shown in Table 4.Table 4. Radioactive residues in lettuce after soil and foliar treatment.Treatment, days after the lasttreatmentTRR(mg/kg)aMethanol(mg/kg)a (%)Unextracted(mg/kg)a (%)Soil, 38 days 10.7 3.8 35.5 6.9 64.5 Foliar, 21 days 9.51 8.04 84.3 1.47 15.5 Control0.35 0.10 29.1 0.24 70.9a. As propamocarb HCl equivalents.Larger sub-samples (about 100 g) were extracted sequentially with methanol and water. The plant residue remaining was re-extracted by refluxing with 2M HCl and with 2M NaOH. The liquid extracts in each case were separated by centrifugation and the radioactivity present determined by724PropamocarbLSC. The unextracted radioactivity accounted for 7.1 and 0.2% of the total residue in soil and foliar treated sample respectively (Table 5).Table 5. Distribution of radioactivity in extracts of lettuce.Treatment aTRR(mg/kg)Methanol(mg/kg) (%)Water(mg/kg) (%)2M HCl(mg/kg) (%)2M NaOH(mg/kg) (%)Unextracted(mg/kg) (%)Soil 8.19 4.37 53.3 0.95 11.7 1.58 19.3 0.71 8.6 0.58 7.1 Foliar 10.7 9.76 91.5 0.69 6.5 0.15 1.4 0.04 0.4 0.02 0.2 Control 0.292 0.20 68.4 NA NA 0.05 16.9 0.03 11.2 0.01 3.5a. After 38 days of the last soil treatment and 21 days after foliar application; NA = not analyzedMethanol and water extracts of plants following soil and the foliar treatments, containing 65% and 98% of TRR, were analysed by HPLC. Table 6 shows that propamocarb formed only in a small proportion of the residue (2.8%) in the lettuce plants grown in treated soil. The residue was composed mainly of an unidentified polar region, Unknown 1. Extracts from the foliar treated samples showed predominantly unchanged propamocarb (90.2%) (Table 7).Table 6. Profile of radioactive residues in (14C)-propamocarb soil treated lettuce.Methanol Extract Water Extract Total CompoundResidue (mg/kg) %TRR Residue(mg/kg)% TRR Residue(mg/kg)%TRRPropamocarb Unknown 1 Unknown 4 Unknown 8 Unknown 10 Unallocated 0.2153.6500.1580.274ND0.0702.644.61.93.4ND0.80.0150.811ND0.0690.0500.0100.210.0ND0.80.60.10.2304.4610.1580.3430.0500.0802.854.61.94.20.60.9Extracted residue 4.367 53.3 0.954 11.7 5.321 65.02M HCl reflux 1.579 19.32M NaOH reflux 0.708 8.6Unextracted 0.580 7.1TRR = 8.19mg/kgTable 7. Profile of radioactive residues in (14C)-propamocarb foliar treated lettuce.Methanol Extract Water Extract Total CompoundResidue (mg/kg) Percent TRR Residue (mg/kg) Percent TRR Residue(mg/kg)Percent TRRPropamocarb Unknown 1 Unknown 4 Unknown 7 Unallocated 9.0160.0810.2840.3180.05784.60.82.73.00.50.5990.0530.0190.0200.0015.60.50.20.2< 0.19.6150.1340.3030.3380.05890.21.32.93.20.5Extracted residue 9.756 91.5 0.692 6.5 10.448 98.02M HCl reflux 0.151 1.42M NaOH reflux 0.043 0.4Unextracted 0.020 0.2TRR = 10.662mg/kgA total radioactive residue of 0.346 mg/kg was observed in samples from the untreated control lettuce, 29% of which was extracted with methanol. More exhaustive extraction of a second sub-sample of control lettuce using methanol, water, acid and base reflux, showed that 68% of the total residue was extracted with methanol, 17% with acid and 11% with base.Propamocarb725 PotatoIn a greenhouse study conducted in 1989 in Germany, [14C]-Propamocarb hydrochloride was applied three times to potato plants, at a rate corresponding to 2.45 kg ai/ha (approximately 20 days between applications) (Förtsch, 1991; A85140).Potatoes samples were harvested 6 weeks after the final application, extracted using acidified methanol and the radioactivity of the combined extracts measured by LSC. On average, 45.5% TRR was found in the extracts (10 samples), corresponding to a TRR of 0.82 mg/kg propamocarb HCl equivalents. The 14C residue present was equally distributed between peel and flesh (0.96 mg/kg and 0.84 mg/kg, respectively). Control potatoes which were grown in the vicinity of the treated plants contained up to 0.3 mg/kg of propamocarb equivalents, the bulk of which was not extracted with acidified methanol.Further extraction and partitioning of the extracted residue into chloroform was conducted, following the acidification and alkalisation of the extracts. Between 22 to 31% of the residue partitioned into the aqueous phase (mean = 25.5%) while 14 to 29% of the residue (mean = 23.6%) was present in the organic fraction (n=6). HPLC analysis of the crude methanol extract of sample No. 10 indicated that propamocarb was the main component, representing 58.4% of the total radioactivity extracted (Table 8). The identities of the metabolites shown on Table 8 were not confirmed in the study, but M1 had the same chromatographic behaviour as propyl propamocarb-N-oxide (Met IV).Table 8. Extracted resides in potato treated with propamocarb.Crude methanol extract After purification% TRR* mg/kg prop HCl equ. Chloroform,% TRR* Aqueous,% TRR* Propamocarb HCl 27.8 0.23 11.8 1.5M1 8.6 0.07 2.3 18.8M2 7.2 0.06 3.5 -M3 2.0 0.02 1.6 -M4 - - 2.5 1.4 Undefined region 2.0 - 0.6 3.6 Total 47.6 0.32 22.3 25.3 * % of the total amount of recovered radiolabel residues of sample No. 10 (47.6% TRR)In another greenhouse study conducted in German in 1994, potato plants were treated as in the previous study and tubers harvested about 6 weeks after the final treatment (Förtsch, 1994; A85141). Samples were macerated and soxhlet extracted with acidified methanol or acetonitrile followed by alkaline and acid hydrolysis of the remaining material. About 90% of the radiolabeled material was recovered by this method. One sample containing 1.12 mg/kg propamocarb eq, had 31.8% of this residue extracted by acetonitrile and 6.6% unextracted. Table 9 shows the chromatographic profile of this sample using different HPLC elution systems. About 7% of TRR was identified as the parent compound in the two HPLC systems, about 50% of TRR showed the same chromatographic behavior as radiolabeled natural products formed from the exposure of spinach plants with 14CO2gas, and identified as d-glucose.Table 9. Metabolic patterns of the extracted residues present in plant extracts.HPLC peak i.d. Retentiontime (min)Macerateextract (%)Soxhletextract (%)HClhydrolysate (%)NaOHhydrolysate (%)Total(%)Normal phase HPLC analysis of potato tubers, System 1Si-1 2- 3 0.17 0.6 1.84 5.86 8.47 Si-2 – d-glucose 3.5-6 5.62 6.18 28.46 13.58 53.84 Si-3 6.5-7 0.14 1.79 1.89 0.5 4.32 Si-4 – propamocarb HCl 8- 10.5 2.75 4.41 n.d. n.d. 7.16 Si-5 11- 12.5 0.07 0.38 n.d. n.d. 0.45 Si-6 13- 15 0.35 0.67 n.d. n.d. 1.02 Si-7 15.5- 18 0.19 n.d. n.d. n.d. 0.19726PropamocarbHPLC peak i.d. Retentiontime (min)Macerateextract (%)Soxhletextract (%)HClhydrolysate (%)NaOHhydrolysate (%)Total(%)Si-8 22- 25 0.06 0.11 n.d. n.d. 0.17 Total characterized 9.95 14.14 32.19 19.94 75.62 Unassigned 14C 1.6 0.5 6.2 2.9 11.2 % of 14C lost 1.1 5.1 -- -- 6.2% of 14C recovered. 12.1 19.7 38.4 22.8 93 Reverse phase HPLC analysis of potato tubers, System 2RP-1 - d-glucose 2 – 4.5 4.83 5.89 27.38 7.4 45.5 RP-2 5.5- 8.5 1.01 0.96 1.61 4016 7.74 RP-3 9 – 11.5 0.72 0.74 1.18 1.16 3.8 RP-4 14 – 16.5 0.32 0.56 1.1 3.53 5.51 RP-5 17 – 19.5 0.29 0.28 n.d. 0.5 1.07 RP-6 20 – 22 0.31 0.64 n.d. n.d. 0.95 RP-7 propamocarb HCl 23.5 – 25.5 2.5 3.26 0.68 0.47 6.91 RP-8 26 - 28 0.5 1.07 2.03 1.79 5.39 Total characterized 10.47 13.4 33.98 19.01 76.86 Unassigned 14C 0.5 1.2 4.4 3.8 9.9% of 14C lost 1.1 5.1 -- -- 6.2% of 14C recovered. 12.1 19.7 38.4 22.8 93In a third study conducted with potato in the UK in 2002 (Goodyear, 2002b; 1669/5-D2149) [14C]-Propamocarb (> 98% radiochemical purity) was applied 6 times as a foliar spray to potatoes grown outdoors in crates at a rate of 2.2 kg ai/ha and at 10.8 kg ai/ha. Initially the treatment solution was applied to the foliage and the drift to soil was small, however by the sixth application the foliage had died back to such an extent that the majority of the treatment solution was sprayed on soil.Samples were harvested when the tubers reached maturity, about 7 days after the last treatment, or 161 days after sowing. Samples of tubers were washed with water and divided equally into two samples, one of which was peeled. Samples of foliage and roots were also taken.Fresh sub-samples of the whole tuber, peel, flesh and foliage were extracted sequentially with methanol, water and refluxed in 2M HCl acid and 2M NaOH base. The liquid extracts in each case were separated by centrifugation and the radioactivity present determined by LSC (Table 10).Table 10. Distribution of residues of [14C]-propamocarb in extracts of parts of treated potato.Whole tuber Peel Flesh Foliage Extract% TRR mg/kg % TRR mg/kg % TRR mg/kg % TRR mg/kg 2.2 kg ai/haMethanol 48.5 0.054 59.2 0.029 60.2 0.013 38.7 33.260 Water 27.3 0.031 18.6 0.009 15.7 0.003 14.7 12.670 2M HCl 19.4 0.022 11.5 0.006 15.2 0.003 20.4 17.511 2M NaOH ND ND ND ND ND ND 13.9 11.952 UnextractedResidue4.8 0.005 10.7 0.005 9.0 0.002 12.2 10.520TRR =0.112mg/kg TRR =0.05mg/kg TRR =0.02mg/kg TRR =85.9mg/kg 10.8 kg ai/haMethanol 39.2 0.02 59.9 0.119 52.0 0.164 52.5 249.8 Water 32.3 0.016 16.4 0.033 18.7 0.059 15.5 73.6 2M HCl 22.0 0.011 13.3 0.027 21.2 0.067 14.0 66.62 2M NaOH ND ND ND ND ND ND 11.7 55.93 UnextractedResidue6.6 0.003 10.3 0.021 8.1 0.025 6.3 30.0TRR =0.050 mg/kg TRR =0.199 mg/kg TRR =0.316 mg/kg TRR =476.0 mg/kgThe methanol, water and acid extract of whole tuber and foliage from the lower rate treatment were analysed by HPLC, TLC and LC-MS (Table 11). Only a small proportion of the residue (< 2% TRR) in whole tuber was identified as propamocarb. The residue was composed predominantly of anPropamocarb727 unidentified region (Unknown 1) and five smaller regions containing each ≤ 6% of TRR. In foliage extracts, a greater proportion of the residue was present as unchanged propamocarb (29%). The remainder of the residue showed a similar pattern of metabolites to those seen in the tuber.HPLC with positive ion mass spectrometry analysis using reference standards tentatively identified the compounds 4, 6 and 7 as being a hydroxypropyl-propamocarb, N-methyl-propamocarb and propamocarb-N-oxide. There was no indication which carbon atom in the propane chain has been hydroxylated. Unknown compounds 2, 3, 5, 8, 9 and 10 were not identified.Table 11. Total amounts of propamocarb and metabolites in potato tuber and foliage.Whole tuber FoliageCompound Residue (mg/kg) % TRR Residue (mg/kg) % TRR Propamocarb 0.002 1.9 24.506 28.6Unknown 1 0.087 77.4 25.843 30.0Unknown 3 < 0.001 0.4 0.675 0.80.001 0.5 1.188 1.4Compound 4: HydroxypropylpropamocarbUnknown 5 0.006 6.0 1.095 1.3Compound 6: N-methyl propamocarb ND ND 4.838 5.7Compound 7: Propamocarb N-oxide 0.004 3.2 3.543 4.1Unknown 8 ND ND 0.359 0.4Unknown 9 ND ND 0.567 0.7Unknown 10 0.001 0.8 ND NDThe nature of the metabolites was investigated using the water extract of foliage treated at the higher rate. The radioactivity present in the water extract was composed mainly of the polar materials (Unknown 1 and Unknown 5). These materials were isolated and subjected to different treatments: 2M HCl at 60 ºC; β-glycosidase in 0.1M ammonium acetate (pH5) at 37 ºC; cellulase in 0.1M ammonium acetate (pH5) at 37 ºC; hesperidinase in 0.1M ammonium formate (pH3.8) at 37ºC; 0.1M ammonium acetate (pH5) at 37 ºC. Between 91−106% radioactivity was recovered following each treatment. The reaction products analysed by HPLC showed that the treatments had no observable effect on the nature of the radioactivity present and no unchanged propamocarb was released. CucumbersIn a greenhouse study, conducted in Germany in 1998, cucumbers were grown in soil treated once with [14C]-propamocarb HCl applied at 2.9 kg ai/ha (11.8 mg ai/plant) and samples harvested at 30 days PHI. Hydroculture-grown cucumbers were treated once at a rate of 53.4 mg ai/plant, applied directly to the hydroponic solution and samples were harvested at 21 days post-application. Analysis of the hydroponic nutrient solution used to feed the cucumber plants showed that propamocarb hydrochloride was the only 14C active compound present. Plant samples were separated into fruit, leaves/stems and roots and were analysed by LSC and by HPLC (Feyerabend and Rupprecht, 1998; A85149).Cucumber samples were first extracted by maceration with methanol/1 M hydrochloric acid (99:1), centrifuged and the extracted solids re-extracted using the same solvent system in a soxhlet. Sample extracts were analysed using both normal phase and reverse phase HPLC conditions. The majority of the radioactivity was extracted by maceration (about 81% TRR) with unextracted residues representing < 8% of TRR. In the foliar treatment, propamocarb represented < 20% of TRR, and it was the major source of the extracted radioactivity in the hydroponic treatment (Table 12). The polar metabolites were not identified in the study. As part of the same study, sample extracts from spinach grown in a 14CO2 enriched atmosphere were analysed in a similar manner and demonstrated that apart728Propamocarbfrom parent propamocarb the majority of the remaining 14C residues detected were present as a result of the incorporation of 14C into natural products.Table 12. Extraction profile of cucumber fruit after soil and hydroponic treatments with propamocarb hydrochloride.Foliar (TRR = 0.069 mg/kg eq.) Hydroponic (TRR = 3.09 mg/kg eq.)mg/kg eq. (% TRR) mg/kg eq. (% TRR)Acid methanol extract Total inextractPropamocarbHClPolarmetabolitesTotal inextractPropamocarbHClPolarmetabolitesMaceration 0.056 (81.2) 0.012 (17.4) 0.029 (42) 2.57 (83.3) 1.59 (51.4) 0.885 (28.6) Soxhlet 0.008 (11.6) 0.0013 (1.9) 0.005 (7.2) 0.341 (11.0) 0.217 (7.0) 0.107 (3.5) Unextracted 0.005 (7.2) - - 0.18 (5.8) - -TomatoesIn a greenhouse study conducted, in the UK in 2001, on tomato [14C]-propamocarb (> 98% radiochemical purity) was applied 4 times to soil at rates of 0.007 and 0.036 kg ai/ha, and as a single foliar treatment at 2.2 kg ai/ha (Goodyear, 2001; 1669/3-D2149). Immature foliage (BBCH Stage 18, 8 true leaves unfolded) was harvested 7 days after the second soil treatment, i.e., 45 days after sowing. Mature tomatoes from the soil treatment were harvested at intervals of 14, 21, 28 and 35 days following the last application. Mature tomatoes, from foliar treated plants, were harvested at intervals of 7, 14, 21 and 28 days following application. Plant foliage was also sampled at the final harvest interval for both treatments. Samples were homogenised in dry ice and stored until analysis.Plant material was extracted by maceration with methanol and water, with further extraction in 0.1M HCl and 0.1M NaOH (maceration and reflux) performed as necessary. The resulting extracts were separated by centrifugation and the radioactivity determined by LSC. The residue remaining was air-dried and the unextracted radioactivity was determined by LSC following combustion. Table 13 shows the radioactivities recovered from the foliage from soil and foliar treatments.Table 13. Radioactivity from foliage extracts.Treatment, TRR mg/kg eq. (% TRR)kg ai/ha PHI mg/kg eq. Water methanol 0.1M HCl 0.1M NaOH Non-extracted Soil, 7 11.8 6.6 (56.5) 0.792 (8.2) 0.31 (2.6) 1.02 (8.6) 2.8 (23.9) 0.007 (1X) 35 4.9 - 2.1 (43.1) 2.8 (56.9) Soil, 7 69.4 38.5 (55.5) 5.4 (7.9) 1.76 (2.5) 6.04 (8.7) 17.6 (25.4) 0.036 (5X) 35 19.8 - 8.2 (41.4) - - 11.6 (59.6) Foliar, 2.2 28 5.21 - 367 (70.6) - - 1.53 (29.4) The water and methanol extracts from the homogenised immature foliage (7 days PHI) were partitioned with chloroform and the resulting aqueous fractions contained 43% of TRR for the 1×treated samples and 37% of TRR for the 5× treated samples. HPLC of the extracts showed about 5% of TRR (0.61 and 3.1 mg/kg eq) as propamocarb, and four unidentified regions of radioactivity ranging from 2 to 22% TRR. The largest single region was polar in nature.Residues in tomato fruit extracts harvested at each interval from the soil and foliar treated plants are shown in Table 14.Table 14. Residues in mature tomato fruit.Interval TRR Methanol Unextracted Treatment (days) mg/kg eq mg/kg eq. % TRR mg/kg eq. % TRRSoil 1× / 5×14 1.48 / 8.4 1.0 / 5.35 67.5 / 63.4 0.41 / 3.03 32.5 / 36.121 1.34 / 7.32 0.89 / 4.84 66.3 / 66.1 0.45 / 2.48 33.7 / 33.928 1.39 / 6.17 0.93 / 4.01 67.0 / 65.0 0.46 / 2.16 33.0 / 35.0。