Residues of the carbamate acaricide, 3-methyl-5-isopropylphenyl-N(n-butanoyl)-N-methylcarbamate (promacyl) and two metabolites in the tissues and milk of cattle

In order to assess some of the residue characteristics of the experimental carbamate acaricide, 3-methyl-5-isopropylphenyl-N-(n-butanoyl-)-N-methylcarbamate (promacyl) a 0.2 % aqueous emulsion was applied to cattle in a series of five trials and in a sixth, the technical product was added to the feed of stalled cattle. A method of analysis involving the formation of a derivative suitable for gas chromatographic analysis on electron capture detection mode was developed. Separate estimations of levels of the parent compound and the metabolites, 3-methyl-5-isopropylphenyl -N-methylcarbamate and 3-methyl-5- isopropylphenol, were carried out on fatty tissues and butterfat but for non-fatty tissues “total” levels, which were a combined estimate of 3-methyl-5-isopropylphenol itself and all substances hydrolysable to it, were estimated and quoted as Promacyl. The highest group average level of the parent compound was 0.9 part/million in fatty tissues 24 h after the last of 8 applications at 3 day intervals. In a single spray trial the maximum group average of 0.7 part/million in fatty tissues 24 h after treatment fell to 0.2 part/million after 5 days. Residues in butterfat, 7 h after a single dermal application showed a maximum level of 1.2 parts/million and this declined to 0.1 part/million on the seventh day after treatment. “Total” residues in non-fatty tissues were of the order of 1/10 those found in fatty tissues.     

Residues of some chlorinated hydrocarbon pesticides in milk and milk products after their addition to the feed of cows

Lactating cows fed 0.05 part/million aldrin, 0.2 part/million γ-BHC and 2.0 parts/million pp'-DDT in their concentrate ration gave detectable residues of dieldrin, γ-BHC, pp'-DDE, pp'-TDE and pp'-DDT in the milk and also aldrin in the butter and cheese. The levels found after 28 days of feeding were not significantly greater than those after 14 days. Subsequent increase of the pesticide content of the feed increased the residue content of the milk, butter and cheese. Only a small percentage of pesticide residue was found in the buttermilk, separated milk and the whey.     

氯虫苯甲酰胺和吡唑醚菌酯在铁皮石斛中的残留及消解动态

建立了QuEChERS-液相色谱-质谱联用 (LC-MS/MS) 同时测定铁皮石斛茎和叶中氯虫苯甲酰胺和吡唑醚菌酯残留量的分析方法,并采用该方法研究了这2种农药在铁皮石斛中的消解动态及最终残留量。样品经乙腈提取,用N-丙基乙二胺 (PSA)、C₁₈和石墨化碳 (PC) 净化。正离子电离,多反应监测模式,LC-MS/MS测定,外标法定量。结果表明:在0.10~60 mg/kg添加水平下,氯虫苯甲酰胺在铁皮石斛茎和叶中的平均回收率为74%~90%,相对标准偏差 (RSD) 为3.2%~4.1%;吡唑醚菌酯在铁皮石斛茎和叶中的平均回收率为75%~104%, RSD为1.7%~4.4%。样品中氯虫苯甲酰胺和吡唑醚菌酯的定量限 (LOQ) 均为 0.1 mg/kg。氯虫苯甲酰胺和吡唑醚菌酯在铁皮石斛中消解较慢,120 d时,氯虫苯甲酰胺在铁皮石斛茎和叶中的降解率分别为40%和72%,吡唑醚菌酯在铁皮石斛茎和叶中的降解率分别为80%和94%。吡唑醚菌酯在铁皮石斛叶中的消解半衰期为38.1 d。5%氯虫苯甲酰胺悬浮剂按有效成分37.5 g/hm2施药1~2次,施药间隔为7 d,当采收间隔期为30 d时,氯虫苯甲酰胺在茎和叶中的残留量均小于3 mg/kg。25%吡唑醚菌酯水分散粒剂按有效成分187.5 g/hm2施药2~3次,施药间隔为7 d,当采收间隔期为90 d时,吡唑醚菌酯在茎和叶中的残留量均小于8 mg/kg。     

毒死蜱在梨果实不同部位的残留及消解动态

为探明毒死蜱在梨果实不同部位的残留及消解规律,以20 a生鸭梨（Pyrus bretschneideri Rehd.cv.Yali）为试材,于果实生长期在套袋后向整株喷施48%毒死蜱乳油500倍液（有效成分960 mg/L）,分析毒死蜱向果实中的运输及分配规律;于果实成熟期在采收前向果面喷施48%毒死蜱乳油1 000倍液（有效成分480 mg/L）,分析采后毒死蜱在梨果实不同组织中的分布特征。采用乙腈萃取和GC-NPD检测方法,测定不同处理试材中的毒死蜱含量。结果表明,在果实套袋情况下,整株喷施毒死蜱后72 h内果实不同部位（果心除外）毒死蜱含量均呈现先逐渐上升而后下降趋势,其中果柄、果皮和果梗洼中毒死蜱最高含量值及其出现的时间分别为6.66 mg/kg（12 h）、2.42 mg/kg（24 h）和0.09 mg/kg（12 h）,表明套袋果实毒死蜱来源于枝叶运输,经果柄进入果实后易向果皮累积;而未套袋果施药后24和72 h果皮中毒死蜱含量分别为套袋果的12.56和7.29倍,表明套袋可有效降低果实中毒死蜱的残留量。于果实成熟期向果面喷施毒死蜱后7、14和25 d,果皮中毒死蜱残留量分别为15.54、13.70和12.81 mg/kg,占全果含量的100%,而果肉中毒死蜱残留量低于本检测方法的最低检出浓度（0.05 mg/kg）,因此果皮为果实中毒死蜱主要残留部位,且贮藏期果皮中毒死蜱不易向果肉扩散。     

A Field Bioassay Approach to Assess the Toxicity of Insecticide Residues on Soil to Collembola

Field bioassays were conducted to assess the toxicity of three insecticides, chlorpyrifos, cypermethrin and pirimicarb, to four species of springtails, Isotoma viridis, Isotomurus palustris, Folsomia candida (Collembola: Isotomidae) and Sminthurus viridis (Collembola: Sminthuridae). Spray residues on two soil types (a sandy clay loam and a sandy soil) were obtained in the field, in the presence and absence of a wheat crop canopy, after spray application by a commercial tractor-mounted sprayer. Collembola were then confined for 24-h periods on the sprayed soils in a constant laboratory environment at 1, 2, 3, 8 and 15 days after treatment. Residual insecticide toxicity was compared between species, insecticides, soils and exposure conditions (crop or no crop) using the age of residue at which median mortality occurred (DAT₅₀). Cypermethrin and pirimicarb residues were of low toxicity, causing less than 10% mortality, whereas residues of chloryprifos were toxic to all four species of Collembola on both soil types and in both exposure treatments. Interspecific differences in collembolan susceptibility to chlorpyrifos residues gave the ranking (from most to least susceptible) S. viridis>F. candida>Isotomurus palustris>Isotoma viridis. Residues on the sandy soil were more toxic than those on the sandy clay loam. These results are discussed in terms of how field bioassay approaches may be used to determine pesticide residual toxicity to microarthropods. We conclude that field bioassays offer a feasible method for evaluating the toxicity of pesticides and the persistence of toxic effects on Collembola. Advantages and disadvantages of this method are considered.     

毒死蜱对蚯蚓生长和繁殖的影响

为探明毒死蜱对蚯蚓的影响,以赤子爱胜蚓Eisenia foetida为受试生物,以人工土壤为试验基质,采用接触暴露法,研究了毒死蜱对赤子爱胜蚓的急性毒性以及对蚯蚓生长和繁殖的影响。结果表明:在有效试验条件下,毒死蜱对蚯蚓的14 d-LC50值为88.75 mg/kg(每千克干土中含毒死蜱有效成分毫克数,其余同);暴露28 d后,10、25、50、80及100 mg/kg处理组蚯蚓的平均体重与对照相比依次下降了9.8%、15.7%、17.5%、23.9%和27.0%,体重下降与药剂处理浓度之间高度相关,且除10 mg/kg处理组外均与对照差异显著(P0.01,r=0.984);毒死蜱10、25、50、80及100 mg/kg处理组对蚯蚓繁殖的抑制率分别为32.26%、80.97%、89.03%、89.68%和97.42%,繁殖抑制率与药剂浓度之间存在一定的相关性(P0.01,r=0.788);毒死蜱影响蚯蚓生长和繁殖的28 d最低可观测效应浓度(LOEC)值为25 mg/kg。     

拟除虫菊酯类杀虫剂在烟叶烘烤过程中的消解动态与最终残留

采用气相色谱-质谱联用技术,测定了良好农业规范(GAP)条件下3种常用拟除虫菊酯类杀虫剂高效氯氟氰菊酯、高效氯氰菊酯及溴氰菊酯在山东、四川、云南、辽宁和江西5地烟叶中的消解动态及最终残留。样品经乙腈提取,SPE-PSA柱净化,气-质联用、选择离子监测模式(GC-MS/SIM)下测定,外标法定量。结果表明:在0.01 ~1 mg/kg添加水平下,3种农药在鲜烟叶和干烟叶中的平均回收率分别在82.9% ~ 110.9%和85.2%~108.3%之间,相对标准偏差(RSD)分别为1.7% ~4.4%和2.3% ~5.7%;3种农药在鲜烟叶和干烟叶中的定量限(LOQ)均为0.01mg/kg;方法的准确度和精密度均符合农药残留检测要求。烘烤过程中残留农药消解明显,高效氯氟氰菊酯、高效氯氰菊酯和溴氰菊酯的消解率分别高达78%、89%和91%。高效氯氟氰菊酯、高效氯氰菊酯和溴氰菊酯乳油分别按有效成分450~675 g/hm2、600~900 g/hm2及450~675 g/hm2于烟叶采 烤初期喷雾施药2次,距末次施药后14d,干烟叶中3种农药的残留量分别为0.022~ 0.50、0.14~0.82和0.046~0.21 mg/kg,均低于国际烟草合作研究中心(CORESTA)提出的指导性农药残留限量标准(GRL)值(0.5、1和1mg/kg),因此建议其安全间隔期可定为14d。     

毒死蜱微球和乳油在水中的消解动态及其对白纹伊蚊幼虫的毒力

室内条件下,研究了不同浓度毒死蜱微球和毒死蜱乳油在水中的消解动态及其对白纹伊蚊Aedes albopictus 3龄幼虫的持续毒杀作用。结果表明:毒死蜱微球在水中的消解速率比乳油慢,半 衰期比乳油的长,高浓度微球和乳油的消解半衰期均长于低浓度下的消解半衰期。有效成分为1.2、 12和24 mg/L的毒死蜱微球和毒死蜱乳油在水中的消解半衰期分别为(19.4±2.1) d、(27.8±1.6) d、(31.0±1.7) d和(12.8±1.0) d、(16.1±0.9) d、(19.7±1.1) d;毒死蜱微球对白纹伊蚊3龄幼虫的毒杀作用强于乳油且持效期长,1.2 mg/L的毒死蜱微球水解85 d后处理白纹伊蚊3龄幼虫的死亡率高达76.6%,高于相同浓度、相同条件乳油的处理(53.3%),具有良好的持效性。     

吡虫啉和毒死蜱对尿素氮在土壤中转化的影响

为了考察杀虫剂施用对尿素态氮在土壤中转化过程的影响,采用室内培养法,通过测定土壤铵态氮和硝态氮质量分数以及反硝化损失的动态变化,研究了在施用尿素的土壤（有效氮含量为200 mg/kg）中分别添加不同剂量的吡虫啉和毒死蜱2种杀虫剂时,杀虫剂对尿素的水解、土壤氮的硝化及反硝化过程的影响。结果表明:吡虫啉和毒死蜱各剂量处理在第3天时对尿素水解具有显著的促进作用（PPPPP<0.01）,减少反硝化损失量39.69%。     

毒死蜱对稀有鮈鲫不同生命阶段的毒性效应

为探明毒死蜱对鱼类不同生命阶段的毒性效应,以稀有鮈鲫Gobiocypris rarus为测试生物,评价了毒死蜱对其的急性毒性及对胚胎生长发育的毒性效应。结果表明:毒死蜱对稀有鮈鲫胚胎、仔鱼、幼鱼和成鱼的96 h-LC50值分别为7.59(5.14~9.86)、0.393(0.326~0.447)、0.047 8(0.038 2~0.054 9)和0.027 2(0.021 9~0.041 9)mg/L,毒死蜱对稀有鮈鲫4个生命阶段的毒性大小依次为成鱼幼鱼仔鱼胚胎;稀有鮈鲫暴露于毒死蜱后最明显的中毒症状是脊柱畸形;此外,质量浓度为6.13~35.8 mg/L的毒死蜱在48 h时可明显促进稀有鮈鲫胚胎的孵化。     

Residues of organochlorine pesticides in broilers from feed fortified with known levels of these compounds

p, p'-DDT, HEOD, endrin, heptachlor epoxide, hexachlorobenzene and lindane were fed in combination to day-old broiler chickens at levels of 0.05, 0.15 and 0.30 part/million in the feed, for a period of about 7 weeks. Birds were killed at regular intervals and samples of abdominal fat and other tissues examined for residues of the chlorinated pesticides by gas-liquid chromatography. The lipid content of each sample was determined and the residue levels calculated for the whole tissue and also for the fat contained in the sample. At the end of the 7 weeks (when in practice broilers are slaughtered) residues were highest for heptachlor epoxide, followed by hexachlorobenzene, HEOD, DDT (total), endrin, and lindane. Heptachlor epoxide residue levels in fat were 13 times the levels in the feed, for lindane the ratio was 3.3. Fat residues of each pesticide reached a plateau level relatively quickly, and these levels were proportional to the fortification rates in the feed. HEOD and p, p'-DDT alone were fed to separate groups of birds. No differences in residue build-up of these compounds were found between these groups and the groups that had received these compounds in combination with the other pesticides. The total amounts of each pesticide in the tissues were reduced when the meat was fried, probably by loss of fat during preparation and frying. For p, p'-DDT and heptachlor epoxide also smaller residue were observed in the remaining fat after frying.     

48%毒死蜱乳油在杭白菊和土壤中的消解动态

通过田间植株直接施药-定期采样-样品提取净化-气相色谱分析的方法,研究了48%毒死蜱乳油中毒死蜱在杭白菊胎菊和土壤中的消解动态,并在室内探讨了不同温度对干胎菊中毒死蜱消解的影响。结果表明:在有效成分0.48和0.72 kg/hm22个施药剂量下,毒死蜱在杭白菊土壤和鲜胎菊中的消解半衰期分别为9.24~10.82 d和2.94~4.22 d;不同温度下,干胎菊中毒死蜱的半衰期在12.64~27.39 d之间,存在显著性差异(P0.05),其消解速率随温度升高而加快;在杭白菊上分别以有效成分0.48 kg/hm2(推荐高剂量)和0.72 kg/hm2(1.5倍推荐高剂量)的剂量喷雾施药2次,距末次施药后21 d时,毒死蜱在干胎菊中的残留量分别为0.58和0.89 mg/kg,均低于我国制定的毒死蜱在茶叶中的最大残留限量(MRL)标准(1 mg/kg)。     

Residues and fate of endosulfan on field-grown pepper and tomato

Endosulfan (Thiodan 3 EC), a mixture of α- and β-isomers, was sprayed on 92-day-old field-grown pepper and tomato at the recommended rate of 0·61 kg AI ha^-1. Plant tissue samples were collected at 1 h to 14 days after application and analysed to determine the content and dissipation rate of endosulfan isomers (α- and β-endosulfan) and the major metabolite, endosulfan sulfate. Analysis of samples was accomplished using gas chromatography-mass selective detection (GC-MSD). The results indicated the formation of endosulfan sulfate as a residue component on the plant tissues and also the relatively higher persistence of the β-isomer as compared to the α-isomer on pepper fruits. The initial total residues (α- and β-endosulfan isomers plus endosulfan sulfate) were higher on leaves than on fruits. On pepper fruits, the α-isomer, which is the more toxic to mammals, dissipated faster than the less toxic β-isomer. Total residues (α- and β-endosulfan isomers plus the sulfate metabolite) on tomato leaves revealed longer persistence (t_1/2 4·6 days) compared to the total residues detected on pepper leaves (t_1/2 2·0 days) 3–14 days following spraying. Persistence of the β-isomer on pepper fruits was high 3–14 days following spraying compared to on tomato fruits. This long persistence increases risk of exposure of the consumer. In addition, the longer persistence of the total residues on tomato foliage should be considered of importance for timing the safe entry of tomato harvesters due to the high mammalian toxicity of endosulfan. © 1998 Society of Chemical Industry     

Accumulation and distribution of pp′-DDT and related compounds in an apple orchard. II. Residues in trees and herbage

DDT residues in or on the roots and leaves of the herbage and the roots, bark, leaves and fruit of the trees are given for an apple orchard sprayed annually (1953–1969). The distribution of DDT in both the grass and the grass roots was in circular areas of residues, with maximum values at each trunk and decreasing radially to each alley. Of the spray applied at the green cluster stage 80% was deposited on the grass sward and very little, if any, directly on the soil surface. The pp′-DDT content of the grass fell rapidly with successive mowings (from which the cuttings remained in situ) from 400 μg/g at spraying to 2 μg/g after nine months. 33 g/ha pp′-DDT was found in the herbage roots (0.87% of the total residues in the soil). The residues in the bark (87.5 g/ha) were much lower than expected after 13 years spray application. There were increased amounts of pp′-DDE, pp′-TDE and pp′-TDEE relative to pp′-DDT, indicating some breakdown on the bark, but the chief losses were attributed to volatilisation and to removal by wind and rain. The residue content of root bark varied from 3 μg/g near the emerging trunk to 0.05 μg/g at a depth of 90 cm. The pp′-DDT content of leaves at leaf fall rose from <1 ng/g after a single spring spray to 8.33 μg/g following an additional spray in late June. There was a large loss of DDT from the canopy between the June spray and leaf fall (440–480 g/ha down to 25 g/ha), attributed to volatilisation. The amount of pp′-DDT on the fruit, after a single spray, was 3 ng/g fresh weight (80.9 mg/ha out of a total of 1.0–1.5 kg/ha used).     

The analysis of crops and soils for the triazine herbicide cyanazine and some of its degradation products. II. Results

Crops and soils from field trials in 1967–1970 in several countries have been analysed for residues of the triazine herbicide cyanazine (‘BLADEX’

1 Shell Registered Trade Mark.

^a or ‘FORTROL’^a' 2-chloro-4-(1-cyano-1-methylethylamino)-6-ethylamino-1,3,5-triazine) and for its degradation products 2-chloro-4-(1-carbarmoyl-1-methylethylamino)-6-ethylamino-1,3,5-triazine ( II ), 2-chloro-4-(1-cyano-1-methylethylamino)-6-amino-1,3,5-triazine ( V ) and 2-chloro-4-(1-carbonyl-1-methylethylamino)-6-amino-1,3,5-triazine ( VI ). The time for the concentration of cyanazine in soils to fall to half the initial value was in the range 1.3 to 5 weeks with a mean value of 2.4 weeks. The rate of loss was not affected by sparse crop cover and there was some indication that the rate was greater under moist soil conditions. Residues of up to 0.5 part/million of ( II ) and up to 0.08 part/million of ( VI ) were detected in soils at 4 weeks from cyanazine application at 2 kg/ha. The residues of cyanazine and the degradation products declined rapidly and were 0.07 part/million or less at 16 weeks from treatment. Repeated annual applications did not lead to a detectable build up of residues in soil. Neither residues of cyanazine nor those of ( II ), ( V ) or ( VI ) could be detected in a wide range of crops harvested from soil treated in accordance with the likely recommendations and the limits of detectability were 0.01 to 0.04 part/million.     

氯溴异氰尿酸在烟叶及其土壤中的残留分析及消解动态

建立了烟叶及其土壤中氯溴异氰尿酸残留的检测方法,并测定了氯溴异氰尿酸在烟叶及其土壤中的消解动态和最终残留。样品经乙腈提取,三氯甲烷、石油醚萃取后,采用高效液相色谱(HPLC-UV)检测。结果表明:在0.01~0.5 mg/kg添加水平下,氯溴异氰尿酸在鲜烟叶、干烟叶和土壤中的平均回收率分别为82.7% ~91.6%、89.2% ~91.8%和89.2% ~94.4%,相对标准偏差(RSD)分别为1.1% ~3.9%、2.6% ~5.5%和1.5% ~4.6%,方法的检出限(LOD)均为0.003 mg/kg, 定量限(LOQ)均为0.01 mg/kg。田间消解动态结果表明,氯溴异氰尿酸在烟叶及其土壤中消解较快,半衰期分别为3.94~4.25 d和2.83~3.41d,施药后14d,其在烟叶和土壤中的消解率均达90%以上。氯溴异氰尿酸可湿性粉剂按有效成分600 g/hm2(推荐高剂量)和900 g/hm2(1.5倍推荐高剂量)于烟草现蕾期对水喷雾施药3~4次,距末次施药后间隔21d采样,烟叶中氯溴异氰尿酸的残留量为1.47~3.52 mg/kg,土壤中的残留量为未检出~0.43 mg/kg。     

亚致死浓度毒死蜱对小麦禾谷缢管蚜生长和繁殖的影响

为探讨毒死蜱对小麦禾谷缢管蚜Rhopalosiphum padi(Linnaeus)的亚致死效应,采用玻璃管药膜法确定了其亚致死浓度(LC10、LC20和LC30),并研究了该浓度下毒死蜱对小麦禾谷缢管蚜生长和繁殖的影响。结果表明:以LC10、LC20和LC30浓度处理后,禾谷缢管蚜成蚜的寿命分别为(8.60±0.22)、(8.03±0.18)和(6.68±0.18)d,均显著短于对照的(10.36±0.31)d;单雌产仔量分别为(21.88±0.63)、(20.41±0.53)和(16.68±0.35)只,也均显著少于对照的(26.40±0.89)只;产仔历期分别为(7.55±0.22)、(6.69±0.17)和(5.64±0.15)d,均显著短于对照的(9.13±0.31)d;试验浓度药剂处理对下一代若蚜期的影响不显著;LC30浓度处理对下一代成蚜繁殖有显著的抑制作用,可减少单雌产仔量3.74只,缩短产仔历期1.39 d。生命表参数分析表明:LC30浓度毒死蜱处理使小麦禾谷缢管蚜的净增殖率(R0)比对照降低了34.71%,使种群加倍时间(t)比对照延长了17.37%;LC20浓度处理使小麦禾谷缢管蚜的平均世代历期(T)延长了12.59%;LC10浓度处理组各项指标与对照间无显著性差异。研究表明,亚致死浓度毒死蜱能够缩短小麦禾谷缢管蚜成蚜的寿命,降低其繁殖力,该结果对小麦禾谷缢管蚜综合防治策略的制定具有积极意义。     

含酰腙结构的新型吡唑酰胺衍生物对小菜蛾的生物活性

采用浸虫法、夹毒叶片法和叶碟法分别测定了13个含酰腙结构的新型吡唑酰胺衍生物对小菜蛾3龄幼虫的触杀、胃毒和拒食活性。结果表明:该类化合物对小菜蛾3龄幼虫具有较高的胃毒和拒食活性,其中苯环上含有氯原子、且酰腙一端的取代基含有杂原子且体积较小的化合物 H7的胃毒和拒食活性最好,明显高于对照药剂毒死蜱。H7 72 h胃毒作用LC50值为0.6 mg/L(毒死蜱的LC50值为7.4 mg/L);有10个化合物的拒食活性高于毒死蜱,其中 H7 48 h的拒食中浓度(AFC50) 最低,为0.6 mg/L,明显低于毒死蜱(AFC50=6.5 mg/L)。供试化合物对小菜蛾3龄幼虫均无触杀活性。     

三种常用农药对环棱螺、圆田螺和河蚬的急性毒性研究

采用急性毒性试验方法,研究了3种常用农药毒死蜱、丁草胺和三唑酮对3种本地底栖生物环棱螺Bellamya quadrata、圆田螺Cipangopaludina cathayensis和河蚬Corbicula fluminea的毒性效应,同时测定了螺类不同大小个体对供试农药的敏感性。结果显示:毒死蜱、丁草胺和三唑酮对环棱螺的96 h-LC50值分别为4.32、3.62和15.2 mg/L,对圆田螺的96 h-LC50值分别为6.31、4.31和16.9 mg/L,对河蚬的96 h-LC50值分别为8.75、6.83和26.5 mg/L;毒死蜱和丁草胺对3种供试生物均为中等毒性,三唑酮属低毒。环棱螺幼螺对毒死蜱、丁草胺和三唑酮的敏感性分别比大螺高2.52、1.84和1.72倍,圆田螺幼螺对毒死蜱、丁草胺和三唑酮的敏感性分别比大螺高2.26、2.26和2.67倍。因此,在田间使用3种供试农药时需注意对供试底栖生物尤其是其幼体的保护。     

改进的QuEChERS气相色谱-串联质谱法测定草莓中21种杀菌剂残留

采用改进的QuEChERS气相色谱-串联质谱法建立了检测草莓中21种杀菌剂（螺环菌胺、甲霜灵、四氟醚唑、酞菌酯、嘧菌环胺、戊菌唑、氟吡菌酰胺、氟菌唑、嘧菌胺、E-苯氧菌胺、抑霉唑、腈菌唑、醚菌酯、环氟菌胺、肟菌酯、丙环唑、环酰菌胺、氟环唑、咪唑菌酮、啶酰菌胺、嘧菌酯）残留的方法。样品经乙腈提取,采用N-丙基乙二胺（primary secondary amine,PSA）和石墨化碳黑（graphitized carbon blacks,GCB）作为分散固相萃取（dispersive solid phase extraction,DSPE）的吸附材料,净化液经氮气吹干、用V（正己烷）:V（丙酮）=9:1混合溶液定容,采用气相色谱-串联质谱（gas chromatography-tandem mass spectrometry,GC-MS/MS）测定。结果表明:在质量浓度0.005~0.2 mg/kg范围内,21种杀菌剂与对应的峰面积间呈良好的线性关系;在0.01、0.05和0.1 mg/kg 3个添加水平下,21种杀菌剂的平均回收率均在70%~122%之间,RSD < 20%。该方法适用于草莓中21种杀菌剂残留的快速、高效和准确分析。