• 
    

    
    

      99热精品在线国产_美女午夜性视频免费_国产精品国产高清国产av_av欧美777_自拍偷自拍亚洲精品老妇_亚洲熟女精品中文字幕_www日本黄色视频网_国产精品野战在线观看 ?

      Uncertainty Evaluation of Preparation of Organophosphorus Pesticide Mixed Standard Solution

      2015-11-18 08:02:16JielianWANGZhengYANAgriculturalProductsQualitySafetyMonitoringCenterofShanxiProvinceTaiyuan030025China
      Agricultural Science & Technology 2015年3期
      關(guān)鍵詞:殘留量有機(jī)磷標(biāo)準(zhǔn)溶液

      Jielian WANG,Zheng YAN,Agricultural Products Quality Safety Monitoring Center of Shanxi Province,Taiyuan 030025,China

      Uncertainty Evaluation of Preparation of Organophosphorus Pesticide Mixed Standard Solution

      Jielian WANG*,Zheng YAN,
      Agricultural Products Quality Safety Monitoring Center of Shanxi Province,Taiyuan 030025,China

      The uncertainty of standard solution plays an important role in detection of pesticide residues.It may affect the accuracy of detection results.In this study,the 14 organophosphorus pesticides mixed standard solution was used as the material to analyze all the influencing factors for the preparation of mixed standard solution with uncertainty as the only judging index.The preparation uncertainty of mixed standard solution was calculated with the top-down calculation method.In the end,the expanded uncertainty was presented.The results showed that the preparation of mixed standard solution from stock solution with precise pipettes had a relatively low uncertainty.

      Organophosphorus pesticide;Mixed standard solution;Preparation and dilution;Uncertainty;Evaluation

      M ost of the organophosphorus pesticides have high toxicity. According to statistics[1],the cases of organophosphorus pesticide residue exceeding account for 2/3 of the total vegetables with excessive pesticide residues.So the detection of organophosphorus pesticide residues has attracted much attention.To improve the reasonability of detection results,the measurement of uncertainty is essential.In the detection of pesticide residues in vegetables,the standard solution is needed.And the uncertainty of preparation of standard solution will directly affect the accuracy of detection results[2].There have been rare reports on uncertainty evaluation of preparation of standard solution. Sun et al.[3]ever evaluated the preparation uncertainties of 6 monostandards for organophosphorus pesticides.The 6 monostandards were prepared with solid standards.However,in current pesticide residue detection,liquid standards are commonly used.The researches on uncertainty

      evaluation of preparation of organophosphorus standard solution are rare. In this study,the 14 organophosphorus pesticides were used as material. Then the mixed standard solution was prepared with 2 methods respectively. The uncertainties of mixed standard solutions were prepared so as to provide a guarantee for the detection results.

      Preparation of Mixed Standard Solution of Organophosphorus Pesticides

      According to the requirements for standard solution preparation by "Multi-residue Detection of Organophosphorus,Organochlorine,Pyrethroid and Carbamate in Vegetables and Fruits"(NY/T761-2008)[4],the 100 μg/ml of organophosphorus standard solution,purchased from the National Standard Centre,should be diluted into 0.2 μg/ml of sampling solution.In the past,certain amount of single organophosphorus standard (100 μg/ml)should be cracked[5]and thendissolved to certain volume with repeated rinsing.During the cracking,loss of standard is forbidden.There have been currently many preparation methods.In this study,two preparation methods were selected and compared.Their expanded uncertainties were obtained.

      (1)At current,the volume of organophosphorus standard solution is generally higher than 1.0 ml.Before the beginning of preparation,the crystals in standard solution must be cracked.Subsequently,1 ml of original standard solution was transferred with 1 ml graduated pipette and dissolved in acetone to 10 ml.Thus 10 μg/ml of stock solution was prepared. The stock solutions of the 14 organophosphorus pesticides were all prepared like that.Then 0.2 ml of each stock solution was mixed together and diluted to 10 ml.The sampling solution with 0.2 μg/ml of each pesticide was prepared.

      (2)Certain amount(1.0 ml)of each pesticide standard solution was transferred accurately with 1 ml graduated pipette and mixed together to 25 ml.Thus the stock solution with 4 μg/ml of each pesticide was prepared. Subsequently,0.5 ml of stock solution was transferred accurately with 0.5 ml graduated pipette and diluted in acetone to 10 ml.The sampling solution with 0.2 μg/ml of each pesticide was also prepared.

      (3)The prepared mixed standard solutions were detected with Agilent7890A-FDP Detector(column,DB-1701),which could completely separate the 14 kinds of pesticides.The approximate read of each standard solution was all 0.2 μg/ml.

      Sources of Uncertainty

      The concentration of each pesticide in the mixed standard solution was calculated according to Eq.(1). The uncertainty of each ingredient in the organophosphorus mixed standard solution mainly came from two parts: the uncertainty of each purchased standard solution itself and the uncertainty caused by two times of dilution[6].

      Wherein,C refers to the final concentration of standard solution;C0refers to the concentration of purchased standard solution;V1refers to the volume of transferred standard solution;V2refers to the volume of transferred stock solution;V3refers to the final volume of transferred stock solution is diluted to;V4refers to the volume of prepared sampling solution.

      Assessment of Uncertainties from Various Sources

      Relative uncertainty assessment of each ingredient in the mixed standard solution caused by its own original concentration

      The uncertainty of each pesticide can be obtained from the product instruction(Table 1).The relative uncertainty of each ingredient in the mixed standard solution was calculated according to Eq.(2)[7].

      Wherein,u (c0)refers to the uncertainty described in the instruction;c0 refers to the concentration of standard solution;k refers to expanded factor.

      Uncertainty of two times of dilution

      The relative uncertainty from volumetric flasks and pipettes consists of three parts.

      Calculation of uncertainty (u1rel)from volume scales In terms of relative uncertainty from volume scales[8],the tolerances of glass apparatus were first obtained through referring to verification regulations of common volumetric glassware (JJG246-2006)[3]. According to rectangular distribution,the relative uncertainties of glass apparatus were calculated according to Eq.(3)(Table 2).

      Wherein,u1(v)refers to the tolerance of glass apparatus,ml;v refers to the capacity of glass apparatus,ml.

      Table 1 Relative uncertainties of 14 organophosphorus pesticides in the mixed standard solution caused by their own original concentrations

      Table 2 Relative uncertainties from volume scales

      Table 3 Uncertainty from difference between solution temperature and calibrated temperature

      Calculation of relative uncertainty(u2rel)from temperature change

      The temperature inside laboratories is required to be 20℃.Once the temperature changes,the volume of acetone will also change.Thus the volume expansion coefficient is needed.The volume expansion coefficient of acetone is 0.001 49 ml/℃.During the preparation,the acetone temperature was 23℃.So the uncertainty(rectangular distribution)of volumetric flask caused by temperature change wascalculated as follows:

      0.00149(volume expansion coefficient of acetone)×3(temperature difference)×10 (capacity of glassware)=0.044 7 ml.

      Table 4 Relative uncertainty of approximate read

      Table 5 Combination of relative uncertainties from different sources

      According to Eq.(4),the uncertainty caused by difference between solution temperature and calibrated temperature was calculated(Table 3).

      Wherein,u2(v)refers to the change in volume,ml;v refers to the capacity of glass apparatus,ml.

      Calculation of relative uncertainty(u3rei)of reading staff The approximate read of the same volumetric glassware by different staff may be different,resulting in the generation of different error.Under the same conditions,the same volumetric flask filled with acetone to the maximum scale was red by two different people respectively.The reads were first calibrated by temperature,and then their repeatability standard deviation was calculated.According to Eq.(5),the relative uncertainty of glass apparatus caused by approximate read was calculated(Table 4).

      Wherein,u3(v)refers to the standard uncertainty of approximate read of glass apparatus,ml;v refers to the capacity of glass apparatus,ml.

      Combined uncertainty of glass apparatus

      During the dilution from standard solution to sampling solution,the uncertainties from various sources of various glass apparatus were calculated.Then the combined uncertainty of each glass apparatus was calculated in according to Eq.(6)(Table 5).

      Table 6 Expanded uncertainty of each standard solution

      Table 7 Final concentration of each standard solution

      Expanded Uncertainty

      According to analysis and calculation above,the uncertainties from different sources were calculated first.Then the combined uncertainties of the mixed standard solutions prepared by two different methods were calculated.In the first preparation method,10 ml volumetric flask was used twice;1 ml graduated pipette was used once;0.2 ml graduated pipette was used once.The uncertainty of mixed standard solution consisted of the uncertainty of each ingredient in the mixed standard solution and the uncertainties of various glass apparatus used in the preparation (Eq.(7)). The combined uncertainties of mixed standard solutions prepared by the two methods were calculated according to Eq.(8).Under conditions of normal distribution,if the coverage factor(k)wasassigned to be 2,the expanded uncertainties of the two mixed standard solutions could be calculated according to Eq.(9)(Table 6).

      Final Concentrations

      Based on the combination of uncertainties of preparation and dilution,the final concentrations the two mixed standard solution were obtained.As shown in Table 7,the second method was significantly better than the first one.In the first preparation method,10 ml volumetric flask was used twice;1 ml graduated pipette was used once;0.2 ml graduated pipette was used once;while in the second method,25 ml volumetric flask was used once;10 ml volumetric flask was used once;1 ml graduated pipette was used once;0.5 ml graduated pipette was used once.In addition to difference in used pipettes,the stock solutions of the two preparation methods were also different.One was monostandards,while the other was mixed standard.Therefore,the precise pipettes are recommended in the preparation of mixed standard solution with stock solution.

      Discussion

      The detection of pesticide residues in agricultural products has attracted much attention from researchers and detectors[8-15].However there are rare reports on uncertainty assessment of organophosphorus pesticide standards[3,9].The solid monostandards are commonly used in the past.At current,the liquid standards are often used in the detection of pesticide residues.The uncertainty assessment of mixed standard solutions consisting of various liquid organophosphorus standards is also reported rarely in China.The previous studies on uncertainty assessment of preparation of pesticide standards mostly conclude that the precise pipettes should be used in the preparation of mixed standards.But they don’t pay their attention to the procedures of the preparation.The precision of pipettes produces greater impact on detection results.However,for the detectors,it is unchangeable.Instead,the uncertainty improvement of standard solutions through comparing preparation methods is more practical for detectors.

      References

      [1]WANG JL(王潔蓮),DONG L(董琳),CHANG H(常宏),et al.Analysis of and strategies for pesticide residue situation in vegetables in Shanxi,2010(2010年山西省蔬菜農(nóng)藥殘留情況分析及應(yīng)對(duì)策略)[J].Agricultural Technology&Equipment(農(nóng)業(yè)技術(shù)與裝備),2011,18:24-25.

      [2]State Bureau of Technical Supervision(國(guó)家技術(shù)監(jiān)督局).JJF1059-2011 E-valuation and Expression of Uncertainty in Measurement(Revised)(JJF1059-2011測(cè)量不確定度評(píng)定與表示 (修訂稿))[S].Beijing:China Standard Press(北京:中國(guó)標(biāo)準(zhǔn)出版社),2011.

      [3]SUN XM(孫曉梅),LIU CY(劉慈玉).Uncertainty analysis of six organophosphorus pesticides standard solution(6種有機(jī)磷農(nóng)藥標(biāo)準(zhǔn)溶液不確定度分析)[J].Chemical Reagent(化學(xué)試劑),2011,33(8):733-735.

      [4]Environmental Quality Supervision and Testing Center(Tianjin)of Ministry of Agriculture,Institute for Environmental Protection and Research of Ministry of Agriculture(農(nóng)業(yè)部環(huán)境質(zhì)量監(jiān)督檢驗(yàn)測(cè)試中心(天津),農(nóng)業(yè)部壞境保護(hù)科研監(jiān)測(cè)所).NY/T 761-2008 Pesticide multiresidue screen methods for determination of organophosphorus pesticides,organochlorine pesticides,pyrethroid pesticides and carbamate pesticides in vegetables and fruits(NY/T 761-2008蔬菜和水果中有機(jī)磷、有機(jī)氯、擬除蟲菊酯和氨基甲酸酯類農(nóng)藥多殘留的測(cè)定)[S].Beijing:China Agriculture Press(北京:中國(guó)農(nóng)業(yè)出版社),2008.

      [5]ZENG Y(曾艷),LANG H(郎紅),SHAO H(邵輝),et al.Uncertainty evaluation of preparation of organ chlorine pesticides mixed standard solution(有機(jī)氯農(nóng)藥混合標(biāo)準(zhǔn)溶液配制不確定度評(píng)定)[J].Pesticide Science and Administration(農(nóng)藥科學(xué)與管理),2013,3,4(8):37-41.

      [6]General Administration of Quality Supervision,Inspection and Quarantine(國(guó)家質(zhì)量監(jiān)督檢驗(yàn)檢疫總局).JJG196-2006 Verification Regulation of Working Glass Container(JJG196-2006常用玻璃量器檢定規(guī)程)[M].Beijing:China Metrology Press(北京:中國(guó)計(jì)量出版社),2007.

      [7]China National Accreditation Board for Conformity Assessment(中國(guó)合格評(píng)定國(guó)家認(rèn)可委員會(huì)).CNAS-GL06 Guidance on Evaluating the Uncertainty in Chemical Analysis(CNAS-GL06化學(xué)分析中不確定度的評(píng)估指南)[M].Beijing:China Metrology Press(北京:中國(guó)計(jì)量出版社),2006.

      [8]PENG HJ(彭慧蓮),CHENG XJ(成秀娟),XU WS(徐偉松),et al.Analysis of uncertainties in determination of four pesticide residues in vegetables by gas chromatography(蔬菜中毒死蜱等幾種農(nóng)藥殘留量測(cè)定不確定度分析)[J].Pesticide Science and Administration(農(nóng)藥科學(xué)與管理),2012,4:35-39.

      [9]JIANG YX(蔣永祥),YE L(葉麗).Uncertainty evaluation of determination of organophosphorus pesticide multiresidues in tea(茶葉中多種有機(jī)磷農(nóng)藥殘留量測(cè)定不確定度的評(píng)定)[J].Analytical Laboratory(分析實(shí)驗(yàn)室),2006,12: 54-57.

      [10]WANG LJ(王立君),YANG T(楊挺),HUANGFU WG(皇甫偉國(guó)).Uncertainty evaluation for determinating pyrethroids residues in vegetables by GC(氣相色譜(GC)測(cè)定蔬菜中擬除蟲菊酯類農(nóng)藥殘留量的不確定度計(jì)算與分析)[J].Chinese Agricultural Science Bulletin(中國(guó)農(nóng)學(xué)通報(bào)),2009,7:219-222.

      [11]HAN HX(韓紅新),SUN CP(孫翠平),WU LY(吳莉宇),et al.Measurement uncertainty in determination of pesticides testing(測(cè)量不確定度在農(nóng)藥殘留分析測(cè)試中的應(yīng)用)[J].Shanghai Measurement and Testing(上海計(jì)量測(cè)試),2008,1:15-18.

      [12]GONG J(龔劍),ZHAN YG(占永革). Uncertainty evaluation of dilution of standard solution(標(biāo)準(zhǔn)溶液稀釋不確定度評(píng)定)[J].Experimental Technology and Management(實(shí)驗(yàn)室技術(shù)與管理),2011,5(28):52-54.

      [13]MA LS(馬麗莎),ZHENG GM(鄭光明). Uncertainty evaluation for determination of chloramphenicol residue in aquatic products by gas chromatography(氣相色譜法測(cè)定水產(chǎn)品中氯霉素的不確定度分析)[J].Chinese Fishery Quality and Standards(中國(guó)漁業(yè)質(zhì)量與標(biāo)準(zhǔn)),2013,4:15-20.

      [14]LONG Y(龍陽(yáng)),MA XH(馬新華),HOU CL(侯翠麗),et al.Application of uncertainty evaluation in determination of moisture in rapeseed seeds(不確定度評(píng)定在油菜籽水分測(cè)定中的應(yīng)用)[J]. Grain and Oil Storage Technology Newsletter(糧油倉(cāng)儲(chǔ)科技通訊),2013,6:44-45.

      [15]ZHANG QL(張青齡).Evaluation of uncertainty in determination of cadmium in rice(大米中鎘含量的測(cè)量不確定度評(píng)定)[J].Fujian Analysis&Testing(福建分析測(cè)試),2014,1:59-62.

      Responsible editor:Tingting XU

      Responsible proofreader:Xiaoyan WU

      有機(jī)磷農(nóng)藥混合標(biāo)準(zhǔn)溶液配制不確定度評(píng)價(jià)

      王潔蓮*,閆 征 (山西省農(nóng)產(chǎn)品質(zhì)量安全檢驗(yàn)監(jiān)測(cè)中心,山西太原030025)

      標(biāo)準(zhǔn)溶液的不確定度對(duì)農(nóng)藥殘留檢測(cè)起著非常重要的作用,影響著檢測(cè)結(jié)果的準(zhǔn)確性。筆者以實(shí)際應(yīng)用的14種有機(jī)磷農(nóng)藥混合標(biāo)準(zhǔn)溶液為例,采用配制混合標(biāo)準(zhǔn)溶液過程單元操作的不確定度計(jì)算方法(top down),分析了在配制混合標(biāo)準(zhǔn)溶液過程中的所有影響因素,得到了最終的擴(kuò)展不確定度。最終結(jié)果顯示使用精準(zhǔn)的移液器將儲(chǔ)備液配置為混合標(biāo)液,得到最終的擴(kuò)展不確定度相對(duì)小。

      有機(jī)磷農(nóng)藥;混合標(biāo)準(zhǔn)溶液;配制稀釋;不確定度;評(píng)價(jià)

      山西省科技攻關(guān)項(xiàng)目(20130310011-4)。

      王潔蓮(1980-),女,山西臨猗人,高級(jí)農(nóng)藝師,研究生,研究方向:農(nóng)產(chǎn)品中農(nóng)藥殘留檢測(cè)。*通訊作者,E-mail:agilent2006@163. com。

      2014-12-16

      2015-01-26

      Supported by Key Science and Technology Program of Shanxi Province,China(20130310011-4).

      .E-mail:agilent2006@163.com

      December 16,2014Accepted:January 26,2015

      猜你喜歡
      殘留量有機(jī)磷標(biāo)準(zhǔn)溶液
      碘標(biāo)準(zhǔn)溶液的均勻性、穩(wěn)定性及不確定度研究
      氣相色譜串聯(lián)質(zhì)譜法測(cè)定茶葉中戊唑醇的殘留量
      HPLC-MS/MS法檢測(cè)花生中二嗪磷的殘留量
      有機(jī)磷化工廢水治理方法探討
      黨參中二氧化硫殘留量的測(cè)定
      中成藥(2018年1期)2018-02-02 07:20:31
      Portal vein embolization for induction of selective hepatic hypertrophy prior to major hepatectomy: rationale, techniques, outcomes and future directions
      標(biāo)準(zhǔn)溶液配制及使用中容易忽略的問題
      有機(jī)磷改性納米SiO2及其在PP中的應(yīng)用
      有機(jī)磷中毒致周圍神經(jīng)損害的電生理研究
      浙貝母中有機(jī)氯農(nóng)藥殘留量和二氧化硫殘留量分析
      介休市| 班戈县| 开平市| 高清| 泗阳县| 寻乌县| 宝丰县| 泗洪县| 遵化市| 辽阳市| 嘉兴市| 石台县| 石狮市| 通城县| 南江县| 岑溪市| 崇州市| 新密市| 乐平市| 河北区| 黄骅市| 浮山县| 托里县| 平舆县| 枞阳县| 五寨县| 股票| 定西市| 德阳市| 六安市| 绵竹市| 宕昌县| 邓州市| 西城区| 康定县| 龙井市| 思茅市| 定襄县| 安陆市| 延边| 阜阳市|