CN102823783B - Method for degrading pesticide residues in ginseng oral liquid by irradiation - Google Patents
Method for degrading pesticide residues in ginseng oral liquid by irradiation Download PDFInfo
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Abstract
Description
技术领域 technical field
本发明属于中草药中农药残留的降解处理技术领域,特别是涉及一种电子束辐照降解人参口服液商品中杀扑磷、地虫硫磷、二嗪磷、伏杀硫磷、吡虫啉、甲氰菊酯等六种禁限用农药的辐照降解方法。The invention belongs to the technical field of degradation treatment of pesticide residues in Chinese herbal medicines, and in particular relates to an electron beam irradiation method for degrading methapon, fenfofos, diazinon, thionon, imidacloprid, and cyanide in commercial products of ginseng oral liquid Irradiation degradation method of six banned and restricted pesticides including permethrin.
背景技术 Background technique
我国是中草药的发祥地,经过多年的不懈努力,国外终于逐渐肯定了中草药在医疗卫生领域的重要地位。然而中草药中的农药残留问题已成为我国中草药出口受阻的主要原因,是阻碍我国这一宝贵文化遗产走向世界最难攻克的壁垒。目前,欧盟、美国、日本等发达国家对进口的中药及保健品中农药残留限量指标的控制提出非常严格的技术指标要求。例如,欧盟药典第五版中规定了162种有毒有害物质的限量指标,从我国进口的中药必须符合其药典才能进入欧洲市场。其中几种有机磷农药的限量标准分别为:二嗪磷0.5mg/kg,地虫硫磷0.05mg/kg,杀扑磷0.2mg/kg,伏杀硫磷0.1mg/kg。再如,日本于2006年重新制定中药中农药残留量的行业标准,其中规定中药材及其制剂中农药残留限量分别为:杀扑磷0.2mg/kg,吡虫啉0.3mg/kg,甲氰菊酯0.2mg/kg。而我国中草药中农药残留标准的制定相对落后于发达国家和地区。因此,必须尽快寻找出有效降低中草药中农药残留的技术方法,使之适应不断严格化的检测标准,对于我国应对国际贸易的机遇和挑战,具有深远意义。my country is the birthplace of Chinese herbal medicine. After years of unremitting efforts, foreign countries have gradually affirmed the important position of Chinese herbal medicine in the field of medical and health care. However, the problem of pesticide residues in Chinese herbal medicines has become the main reason why the export of Chinese herbal medicines is blocked in my country, and it is the most difficult barrier to overcome this precious cultural heritage of our country to the world. At present, developed countries such as the European Union, the United States, and Japan have put forward very strict technical index requirements for the control of pesticide residue limit indicators in imported traditional Chinese medicine and health care products. For example, the fifth edition of the European Pharmacopoeia stipulates the limit indicators of 162 kinds of toxic and harmful substances. Traditional Chinese medicine imported from my country must comply with its pharmacopoeia before entering the European market. The limit standards for several organophosphorus pesticides are: diazinon 0.5mg/kg, tefenthion 0.05mg/kg, methapion 0.2mg/kg, and thionon 0.1mg/kg. As another example, Japan re-established the industry standards for pesticide residues in traditional Chinese medicine in 2006, which stipulated that the pesticide residue limits in Chinese herbal medicines and their preparations were: 0.2 mg/kg of methapon, 0.3 mg/kg of imidacloprid, and 0.3 mg/kg of fenpropathrin. 0.2mg/kg. However, the establishment of pesticide residue standards in Chinese herbal medicines in my country lags behind developed countries and regions. Therefore, it is necessary to find a technical method to effectively reduce pesticide residues in Chinese herbal medicine as soon as possible, so as to adapt to the increasingly stringent testing standards, which has far-reaching significance for our country to deal with the opportunities and challenges of international trade.
农业工作者一直致力于对农药残留降解方法的研究与探索,微生物降解、臭氧降解、光催化降解、双氧水降解、吸附去除等方法分别利用物理吸附或化学反应等原理,对不同种类的农药分别有一定的降解作用。我国的辐照技术目前在遗传育种、食品保藏、工业废水处理、医疗药品消毒等方面已经取得突破性进展,但辐照降解作为一种提高食品安全的新技术,研究尚处于起步阶段,林艳等研究证明10kGy剂量下的γ射线辐照可使笋干中残留的敌敌畏或三唑磷的降解率达到35%以上,伍玲等也对辐照降解茶叶中菊酯类农药进行了可行性研究,但中草药中农药辐照降解研究尚未检索到有关文献。Agricultural workers have been committed to the research and exploration of pesticide residue degradation methods. Methods such as microbial degradation, ozone degradation, photocatalytic degradation, hydrogen peroxide degradation, and adsorption removal use the principles of physical adsorption or chemical reaction, respectively, and have different effects on different types of pesticides. certain degradation. my country's irradiation technology has made breakthroughs in genetic breeding, food preservation, industrial wastewater treatment, and disinfection of medical drugs. However, as a new technology to improve food safety, research on irradiation degradation is still in its infancy. Lin Yan etc. have proved that γ-ray irradiation at a dose of 10kGy can make the degradation rate of dichlorvos or triazophos remaining in dried bamboo shoots reach more than 35%. Wu Ling et al. also conducted a feasibility study on the irradiation degradation of pyrethroid pesticides in tea. , but the research on the radiation degradation of pesticides in Chinese herbal medicines has not retrieved relevant literature.
人参是我国特产的一种名贵中草药材,由于其极高的药用价值及保健功效,占有中草药市场和保健品市场很大的比重,其种植生长期较长(一般在四年以上),易受农药污染,故人参及其制品都存在着农药残留问题。人参口服液商品在生产过程中不可避免的残留农药,影响口服液的使用安全,而有关如何控制降解人参口服液中农药残留的研究未见报道。Ginseng is a kind of precious Chinese herbal medicine that is a special product of our country. Due to its extremely high medicinal value and health care efficacy, it occupies a large proportion of the Chinese herbal medicine market and the health care product market. Contaminated by pesticides, ginseng and its products all have pesticide residues. The unavoidable pesticide residues in the production process of ginseng oral liquid products affect the safety of the oral liquid, but there is no report on how to control the degradation of pesticide residues in ginseng oral liquid.
发明内容 Contents of the invention
本发明目的是提供一种辐照降解控制人参口服液中杀扑磷、地虫硫磷、二嗪磷、伏杀硫磷、吡虫啉、甲氰菊酯等六种禁限用农药残留的方法,采用该方法能有效、快速、安全、可靠的降低人参口服液中的多种农药残留,使人参口服液中这六类农药最高残留值达到欧盟等国家标准。The purpose of the present invention is to provide a method for controlling six prohibited and restricted pesticide residues in ginseng oral liquid, such as thiafos, tefenthion, diazinon, thionof, imidacloprid, and fenpropathrin, through irradiation degradation. The method can effectively, quickly, safely and reliably reduce the residues of various pesticides in the ginseng oral liquid, so that the maximum residue values of the six types of pesticides in the ginseng oral liquid can reach the national standards of the European Union and the like.
本发明所采取的技术方案是:The technical scheme that the present invention takes is:
以高能电子束为辐射源对含有六种禁限量农药(杀扑磷、地虫硫磷、二嗪磷、伏杀硫磷、吡虫啉、甲氰菊酯)的人参口服液进行处理,使农药降解;所述的高能电子束由电子加速器产生,电子加速器的能量为7.5MeV,电子辐照剂量为2~15kGy;人参口服液中农药残留量适用范围为0.05~0.5mg/kg。Using high-energy electron beams as radiation sources to treat ginseng oral liquid containing six prohibited and limited pesticides (thionon, fenfofos, diazinon, thionon, imidacloprid, and fenpropathrin) to degrade the pesticides The high-energy electron beam is generated by an electron accelerator, the energy of the electron accelerator is 7.5MeV, and the electron irradiation dose is 2-15kGy; the applicable range of pesticide residues in ginseng oral liquid is 0.05-0.5mg/kg.
对于农药残留量高于0.5mg/kg的人参口服液,应当稀释后再辐照处理,所述稀释为加入不含农药的空白人参口服液(实验中所用口服液均为市场上购买商品化棕色药剂瓶10mL装)混合,使混合后的农药含量低于0.5mg/kg。For ginseng oral liquid with pesticide residue higher than 0.5mg/kg, it should be diluted and then irradiated. 10mL medicament bottle) and mixed so that the mixed pesticide content is lower than 0.5mg/kg.
在辐照过程中,应保证人参口服液接受辐照剂量的均匀性,使最高接受剂量与最低接受剂量的比在1.5~2之间,最高不得大于2。During the irradiation process, the uniformity of the radiation dose received by Ginseng Oral Liquid should be ensured, so that the ratio of the highest received dose to the lowest received dose is between 1.5 and 2, and the maximum should not be greater than 2.
具体降解过程和步骤如下:The specific degradation process and steps are as follows:
将各种供试农药标准品溶解于乙腈中,配制浓度为10mg/kg的混合标准溶液;将以上混合标准品溶液加入到10mL装空白商品化人参口服液中,使其六种禁限用农药残留浓度为0.05~0.5mg/kg,将人参口服液样品置于电子加速器的辐照窗口下;开启电子加速器进行电子束辐照;电子加速器的能量为7.5MeV,电子辐照剂量为2~15kGy;辐照前后样品溶液的浓度通过高效液相色谱-串联质谱法检测,得知其降解率。辐照剂量越高,降解率越高。Dissolve various standard pesticides for testing in acetonitrile to prepare a mixed standard solution with a concentration of 10mg/kg; add the above mixed standard solution to 10mL blank commercial ginseng oral liquid to make six prohibited and restricted pesticides The residual concentration is 0.05~0.5mg/kg, the ginseng oral liquid sample is placed under the irradiation window of the electron accelerator; the electron accelerator is turned on for electron beam irradiation; the energy of the electron accelerator is 7.5MeV, and the electron irradiation dose is 2~15kGy ; The concentration of the sample solution before and after irradiation is detected by high performance liquid chromatography-tandem mass spectrometry, and its degradation rate is known. The higher the irradiation dose, the higher the degradation rate.
本发明实验中,人参口服液中添加的农药标样的浓度为0.2mg/kg,此方法对限量标准在0.05~0.5mg/kg之间的农药均适用。In the experiment of the present invention, the concentration of the pesticide standard sample added in the ginseng oral liquid is 0.2 mg/kg, and this method is applicable to the pesticides whose limit standard is between 0.05 and 0.5 mg/kg.
辐照对人参口服液品质的影响Effect of Irradiation on the Quality of Ginseng Oral Liquid
将辐照后人参口服液样品测定人参皂苷的含量。结果表明,辐照处理对人参口服液样品中人参皂苷的含量影响与对照相比无统计意义上的显著差异(p<0.01)。可见在此辐照剂量下,达到控制降解杀扑磷等所述六种农药的同时不影响人参口服液的品质。The irradiated ginseng oral liquid samples were used to determine the content of ginsenosides. The results showed that the irradiation treatment had no statistically significant difference (p<0.01) on the content of ginsenosides in the ginseng oral liquid samples compared with the control. It can be seen that under this irradiation dose, the quality of the ginseng oral liquid is not affected while achieving the controlled degradation of the six pesticides such as methadion.
本发明的有关机理和原理:Relevant mechanism and principle of the present invention:
电子束辐照技术是一种有效的高级氧化技术,辐照处理可使人参口服液中的水分子受到电子束辐照后产生水化自由电子eaq-,OH·,H·等反应活性非常高的物质,这些物质可与人参口服液中的杀扑磷、地虫硫磷、二嗪磷、伏杀硫磷、吡虫啉、甲氰菊酯农药分子结构中薄弱环节发生反应,如发生脱卤、断键等辐照化学反应,使所述六种目标农药发生降解,从而使农药最高限量值达到欧盟等国家标准,相关研究成果目前未见报道。Electron beam irradiation technology is an effective advanced oxidation technology. Irradiation treatment can make water molecules in ginseng oral liquid be irradiated by electron beams to produce hydration free electrons eaq - , OH·, H·, etc. The reactivity is very high These substances can react with the weak links in the molecular structure of the pesticides such as methapon, fenfofos, diazinon, thionon, imidacloprid, and fenpropathrin in the ginseng oral liquid, such as dehalogenation, Irradiation chemical reactions such as bond breaking degrade the six target pesticides, so that the maximum limit value of pesticides can reach the standards of the European Union and other countries. The relevant research results have not been reported so far.
本发明的优点和积极效果是:Advantage and positive effect of the present invention are:
目前对于人参口服液中农药的降解和去除的研究还处于起步阶段,所见的国内外的报道很少,没有特别理想的方法。由于辐照是唯一能够同时在水体系中产生浓度既高又几乎相等的强氧化剂和强还原剂的技术,因而特别适合于口服液商品中的农药降解。与其他处理技术相比,辐照技术具有广泛的适应性,不需添加任何化学试剂,安全可靠无二次污染,反应速率快,降解效率高。15kGy辐照时,方法所涉及的六种农药降解率均超过30%。At present, the research on the degradation and removal of pesticides in ginseng oral liquid is still in its infancy, and there are few reports at home and abroad, and there is no particularly ideal method. Since irradiation is the only technology that can simultaneously produce strong oxidants and strong reductants with high and almost equal concentrations in the water system, it is especially suitable for the degradation of pesticides in oral liquid products. Compared with other treatment technologies, irradiation technology has wide adaptability, does not need to add any chemical reagents, is safe and reliable without secondary pollution, has fast reaction rate and high degradation efficiency. When irradiated at 15kGy, the degradation rates of the six pesticides involved in the method were all over 30%.
本发明的创新性主要体现在以下几点:一是本发明采用电子束作为辐照源;二是辐照剂量的选择;三是本发明首次采用代表性中草药之人参口服液基质作为处理对象;四是本发明选取了中草药中代表禁限用农药杀扑磷、地虫硫磷、二嗪磷、伏杀硫磷、吡虫啉、甲氰菊酯。The innovation of the present invention is mainly reflected in the following points: one is that the present invention uses electron beams as the radiation source; the other is the selection of the radiation dose; the third is that the present invention firstly uses the ginseng oral liquid base of a representative Chinese herbal medicine as the treatment object; The fourth is that the present invention has selected representative banned and restricted pesticides such as difenfos, difenthion, diazinon, thionfos, imidacloprid, and fenpropathrin among Chinese herbal medicines.
附图说明 Description of drawings
图1是本发明不同辐照剂量条件下人参口服液中多农药的降解曲线。Fig. 1 is the degradation curve of multiple pesticides in ginseng oral liquid under different irradiation dose conditions of the present invention.
具体实施方式 Detailed ways
为能进一步了解本发明的发明内容、特点及功效,兹例举以下实施例,并配合附图详细说明如下,但本发明的保护范围不局限于此:In order to further understand the content of the invention, features and effects of the present invention, the following examples are given hereby, and detailed descriptions are as follows in conjunction with the accompanying drawings, but the protection scope of the present invention is not limited thereto:
实施例1Example 1
一种人参口服液的辐照处理方法:A kind of irradiation processing method of ginseng oral liquid:
选用市场上10mL棕色瓶装的人参口服液商品,该商品经检验不含本发明所涉及杀扑磷等六种农药。参照欧盟等国家限量标准将所选的六种待试农药标准品溶液添加于人参口服液商品中,添加浓度为约0.200mg/kg。辐照时设3个平行样,同时设空白对照。将加入上述溶液的人参口服液样品置于电子加速器的辐照窗口下,采用5kGy剂量辐照,开启电子加速器进行电子束辐照。Select the ginseng oral liquid commodity of 10mL brown bottle on the market for use, and this commodity does not contain six kinds of pesticides such as methadon involved in the present invention through inspection. The selected six kinds of pesticide standard solutions to be tested were added to the ginseng oral liquid commodity with reference to the limit standards of countries such as the European Union, and the added concentration was about 0.200 mg/kg. Three parallel samples were set up during irradiation, and a blank control was set up at the same time. The ginseng oral liquid sample added with the above solution was placed under the irradiation window of an electron accelerator, irradiated with a dose of 5 kGy, and the electron accelerator was turned on for electron beam irradiation.
辐照前后样品溶液经下述的前处理方法提取后,通过高效液相色谱-串联质谱法检测,得知其中农药的降解率。After the sample solution before and after irradiation was extracted by the following pretreatment method, it was detected by high performance liquid chromatography-tandem mass spectrometry, and the degradation rate of the pesticide was obtained.
前处理的方法:Pre-processing method:
称取混匀后的人参口服液约10mL于50mL离心管中,加入10mL1%乙酸酸化乙腈、2g氯化钠、0.5g柠檬酸二钠倍半水合物、1g柠檬酸钠,超声提取10min,加入5g无水硫酸镁,涡旋振荡1min,8000r/min离心5min,将上清液转移到15mL离心管中,在离心管中加入100mg PSA、100mg C18和1g无水硫酸镁,剧烈震荡1min,10000r/min离心5min,取上清液经0.22μm滤膜过滤后,供UPLC-MS-MS测定。Weigh about 10 mL of the mixed ginseng oral liquid into a 50 mL centrifuge tube, add 10 mL of 1% acetic acid acidified acetonitrile, 2 g of sodium chloride, 0.5 g of disodium citrate sesquihydrate, 1 g of sodium citrate, ultrasonically extract for 10 min, add 5g anhydrous magnesium sulfate, vortex for 1min, centrifuge at 8000r/min for 5min, transfer the supernatant to a 15mL centrifuge tube, add 100mg PSA, 100mg C18 and 1g anhydrous magnesium sulfate in the centrifuge tube, shake vigorously for 1min, 10000r /min centrifuged for 5min, and the supernatant was filtered through a 0.22μm filter membrane for UPLC-MS-MS determination.
优选的色谱条件:色谱柱:ACQUITYUPLC BEH C18柱,2.1×10mm,1.7μm;柱温:25℃;流动相:甲醇+10mmol/L乙酸铵;进样量:5μL;流速:0.25mL/min。Preferred chromatographic conditions: Chromatographic column: ACQUITYUPLC BEH C18 column, 2.1×10mm, 1.7μm; column temperature: 25°C; mobile phase: methanol + 10mmol/L ammonium acetate; injection volume: 5μL; flow rate: 0.25mL/min.
优选的质谱条件:离子源:电喷雾离子源;扫描方式:正离子扫描;采集模式:多反应监测模式MRM;毛细管电压:3.12kV;脱溶剂气温度:400℃;脱溶剂气流速:800L/Hr;锥孔反吹气流速:50L/Hr。Preferred mass spectrometry conditions: ion source: electrospray ion source; scan mode: positive ion scan; acquisition mode: multiple reaction monitoring mode MRM; capillary voltage: 3.12kV; desolvation temperature: 400°C; Hr; Taper hole blowback flow rate: 50L/Hr.
结果表明,杀扑磷的降解率为14.9%,残留量为0.186mg/kg,符合欧盟、日本等国家限量标准;甲氰菊酯的降解率为25.9%,残留量为0.145mg/kg,符合欧盟、韩国等国家限量标准。The results showed that the degradation rate of methadon was 14.9%, and the residual amount was 0.186mg/kg, which met the limit standards of EU, Japan and other countries; the degradation rate of fenpropathrin was 25.9%, and the residual amount was 0.145mg/kg, which met the European Union, South Korea and other countries limited standards.
表1(1)人参口服液中6种农药辐照后含量与辐照降解率Table 1 (1) Contents and irradiation degradation rates of 6 pesticides in ginseng oral liquid after irradiation
表1(2)人参口服液中6种农药辐照后含量与辐照降解率Table 1 (2) Contents and irradiation degradation rates of 6 pesticides in ginseng oral liquid after irradiation
实施例2Example 2
实施例1中的辐照剂量改为15kGy,其余条件均不变。吡虫啉降解率大于90%,属于显著降解,甲氰菊酯降解率大于50%,其余四种农药的降解率也均超过30%。The irradiation dose in Example 1 was changed to 15kGy, and all other conditions were unchanged. The degradation rate of imidacloprid is greater than 90%, which belongs to significant degradation, the degradation rate of fenpropathrin is greater than 50%, and the degradation rates of the other four pesticides are also more than 30%.
实施例1-2数据详见表1。The data of Examples 1-2 are detailed in Table 1.
实施例3Example 3
实施例1中的辐照剂量改为10kyG,添加剂量改为0.05mg/kg,其余条件均不变。地虫硫磷降解率为14.6%,残留量为0.043mg/kg,符合欧盟等国家残留限量标准。In Example 1, the irradiation dose was changed to 10kyG, the additive dose was changed to 0.05mg/kg, and the rest of the conditions remained unchanged. The degradation rate of tefenthion is 14.6%, and the residue is 0.043mg/kg, which is in line with the EU and other countries' residue limit standards.
实施例4Example 4
实施例1中的辐照剂量改为10kyG,添加剂量改为0.5mg/kg,其余条件均不变。二嗪磷降解率为22.5%,残留量为0.388mg/kg,符合欧盟等国家残留限量标准。In Example 1, the irradiation dose was changed to 10kyG, the additive dose was changed to 0.5 mg/kg, and the rest of the conditions remained unchanged. The degradation rate of diazinon was 22.5%, and the residue amount was 0.388mg/kg, which was in line with the residue limit standards of the European Union and other countries.
结果表明:The results show:
四个对照实施例比较发现,本发明方法电子束辐照可以有效的降低人参口服液中多种农药残留,使之达到欧盟等国家与地区的限量标准,并且六种农药的降解效果随辐照剂量的增大而增大(图1为不同辐照剂量条件下人参口服液中多农药的降解曲线)。本实施例辐照后被试农药的降解结果具有本发明所述的优点和积极效果。Four comparison examples find that, electron beam irradiation of the inventive method can effectively reduce multiple pesticide residues in the ginseng oral liquid, make it reach the limit standard of countries and regions such as European Union, and the degradative effect of six kinds of pesticides increases with irradiation The dose increases (Figure 1 shows the degradation curves of multiple pesticides in ginseng oral liquid under different irradiation doses). The degradation results of the tested pesticides after irradiation in this example have the advantages and positive effects described in the present invention.
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