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    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

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    [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.

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    [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

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