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CN115005218A - Preparation of a pH-responsive controlled-release nanopesticide based on hydroxyapatite carrier - Google Patents

Preparation of a pH-responsive controlled-release nanopesticide based on hydroxyapatite carrier Download PDF

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CN115005218A
CN115005218A CN202210447499.5A CN202210447499A CN115005218A CN 115005218 A CN115005218 A CN 115005218A CN 202210447499 A CN202210447499 A CN 202210447499A CN 115005218 A CN115005218 A CN 115005218A
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nano
hydroxyapatite
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atrazine
pesticide
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田江
侯雪娟
葛飞
李峰
南慧
黄睿
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Xiangtan University
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    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01NPRESERVATION OF BODIES OF HUMANS OR ANIMALS OR PLANTS OR PARTS THEREOF; BIOCIDES, e.g. AS DISINFECTANTS, AS PESTICIDES OR AS HERBICIDES; PEST REPELLANTS OR ATTRACTANTS; PLANT GROWTH REGULATORS
    • A01N43/00Biocides, pest repellants or attractants, or plant growth regulators containing heterocyclic compounds
    • A01N43/64Biocides, pest repellants or attractants, or plant growth regulators containing heterocyclic compounds having rings with three nitrogen atoms as the only ring hetero atoms
    • A01N43/661,3,5-Triazines, not hydrogenated and not substituted at the ring nitrogen atoms
    • A01N43/681,3,5-Triazines, not hydrogenated and not substituted at the ring nitrogen atoms with two or three nitrogen atoms directly attached to ring carbon atoms
    • A01N43/70Diamino—1,3,5—triazines with only one oxygen, sulfur or halogen atom or only one cyano, thiocyano (—SCN), cyanato (—OCN) or azido (—N3) group directly attached to a ring carbon atom
    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01NPRESERVATION OF BODIES OF HUMANS OR ANIMALS OR PLANTS OR PARTS THEREOF; BIOCIDES, e.g. AS DISINFECTANTS, AS PESTICIDES OR AS HERBICIDES; PEST REPELLANTS OR ATTRACTANTS; PLANT GROWTH REGULATORS
    • A01N25/00Biocides, pest repellants or attractants, or plant growth regulators, characterised by their forms, or by their non-active ingredients or by their methods of application, e.g. seed treatment or sequential application; Substances for reducing the noxious effect of the active ingredients to organisms other than pests
    • A01N25/08Biocides, pest repellants or attractants, or plant growth regulators, characterised by their forms, or by their non-active ingredients or by their methods of application, e.g. seed treatment or sequential application; Substances for reducing the noxious effect of the active ingredients to organisms other than pests containing solids as carriers or diluents
    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01NPRESERVATION OF BODIES OF HUMANS OR ANIMALS OR PLANTS OR PARTS THEREOF; BIOCIDES, e.g. AS DISINFECTANTS, AS PESTICIDES OR AS HERBICIDES; PEST REPELLANTS OR ATTRACTANTS; PLANT GROWTH REGULATORS
    • A01N25/00Biocides, pest repellants or attractants, or plant growth regulators, characterised by their forms, or by their non-active ingredients or by their methods of application, e.g. seed treatment or sequential application; Substances for reducing the noxious effect of the active ingredients to organisms other than pests
    • A01N25/26Biocides, pest repellants or attractants, or plant growth regulators, characterised by their forms, or by their non-active ingredients or by their methods of application, e.g. seed treatment or sequential application; Substances for reducing the noxious effect of the active ingredients to organisms other than pests in coated particulate form
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/30Against vector-borne diseases, e.g. mosquito-borne, fly-borne, tick-borne or waterborne diseases whose impact is exacerbated by climate change

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  • Life Sciences & Earth Sciences (AREA)
  • General Health & Medical Sciences (AREA)
  • Health & Medical Sciences (AREA)
  • Wood Science & Technology (AREA)
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  • Plant Pathology (AREA)
  • Engineering & Computer Science (AREA)
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  • Agronomy & Crop Science (AREA)
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  • Environmental Sciences (AREA)
  • Toxicology (AREA)
  • Agricultural Chemicals And Associated Chemicals (AREA)

Abstract

本发明公开了一种羟基磷灰石载体pH响应控释纳米农药的制备。本发明采用粒径为200nm的纳米羟基磷灰石负载扑草净和阿特拉津两种农药,再用海藻酸钠包裹纳米颗粒制备成为凝胶微球(粒径约1mm),该农药在中性偏碱性条件下的控释效果优于酸性条件且基本不受光照和温度的影响,同时纳米羟基磷灰石中正磷酸盐的释放还可以为土壤中微生物和植物提供磷源。本发明材料成本低廉,环境友好,可以在发挥药效的同时改善土壤肥力,具有广泛的应用前景。

Figure 202210447499

The invention discloses the preparation of a hydroxyapatite carrier pH-responsive controlled-release nano-pesticide. The present invention adopts nano-hydroxyapatite with a particle size of 200nm to load two pesticides, promethazine and atrazine, and then wraps the nanoparticles with sodium alginate to prepare gel microspheres (with a particle size of about 1mm). The controlled release effect under neutral alkaline conditions is better than that under acidic conditions and is basically not affected by light and temperature. Meanwhile, the release of orthophosphate in nano-hydroxyapatite can also provide phosphorus source for microorganisms and plants in soil. The material of the invention has low cost and environmental friendliness, can improve soil fertility while exerting medicinal effect, and has wide application prospects.

Figure 202210447499

Description

一种基于羟基磷灰石载体pH响应控释纳米农药的制备Preparation of a pH-responsive controlled-release nanopesticide based on hydroxyapatite carrier

技术领域technical field

本发明设计新型农药领域,具体涉及一种基于羟基磷灰石载体的pH响应控释纳米农药制备及其控释效果。The invention designs the field of novel pesticides, in particular to the preparation of a pH-responsive controlled-release nano-pesticide based on a hydroxyapatite carrier and its controlled-release effect.

背景技术Background technique

我国是一个产粮大国,同时也是一个农药的生产和施用大国,农药由于具备有效除虫和除草能力被人们广泛的运用。在一般情况下,农药有一个推荐使用量,但由于集体农业的发展和经济利益的驱使,施用频次却不断增加,使得在实际生产过程中的使用量是推荐剂量的2倍或多倍。这就造成了有很大一部分农药不能被消耗而残留在了土壤环境当中。水环境,大气环境,土壤环境三者是紧密联系在一起的,当土壤中的农药过剩时,过剩的农药有可能通过大气蒸腾作用和降雨淋溶作用转移到大气环境和水环境中,进而整个生态环境系统都有可能农药含量超标。人类活动与生态环境相互影响相互制约,人的活动影响这生态环境,生态环境也反过来影响和制约着人类的活动,因此,当生态环境中的农药含量超标时,人类的正常生活活动也会受到影响。my country is a big grain-producing country, but also a big country in the production and application of pesticides. Pesticides are widely used because of their effective insect and weed control capabilities. In general, pesticides have a recommended dosage, but due to the development of collective agriculture and the driving of economic interests, the application frequency has been increasing, so that the amount used in the actual production process is 2 times or more than the recommended dosage. As a result, a large part of pesticides cannot be consumed and remain in the soil environment. The water environment, the atmospheric environment and the soil environment are closely linked. When there is an excess of pesticides in the soil, the excess pesticides may be transferred to the atmospheric environment and the water environment through atmospheric transpiration and rainfall leaching. The ecological environment system may have excessive pesticide content. Human activities and the ecological environment influence each other and restrict each other. Human activities affect the ecological environment, and the ecological environment in turn affects and restricts human activities. Therefore, when the pesticide content in the ecological environment exceeds the standard, the normal life activities of human beings will also be affected. affected.

纳米农药因为其具有一定的缓控释效果,是现在研究的一个重要方向,可以减少农药在土壤中的残留量从而减少人体内农药的聚集量。土壤的环境相比起于水来说非常之复杂,因此,不论我们制备的农药也好磷肥也罢都需要在土壤的复杂环境中有很好的稳定性。比如在pH变化,温度变化,以及在光照条件下变化不会对所施加的药物的性质有很大的改变。Because of its slow and controlled release effect, nano-pesticides are an important direction of current research, which can reduce the residual amount of pesticides in the soil and reduce the accumulation of pesticides in the human body. The soil environment is very complex compared to water. Therefore, whether we prepare pesticides or phosphate fertilizers, it needs to have good stability in the complex environment of the soil. Such as pH changes, temperature changes, and changes in light conditions do not significantly change the properties of the applied drug.

本发明利用纳米羟基磷灰石作为农药载体,考虑到纳米羟基磷灰石在酸性条件下会释放出磷,且纳米羟基磷灰石本身材料较为天然,在通常情况下不会对人或者动植物有副作用。因此纳米羟基磷灰石是一个良好的天然载体,将它负载农药一方面可以减少农药的施用量,另一方面还能够释放植物生长所必须的磷,有良好的施用前景。除此还用海藻酸钠包裹微球,使得纳米农药有良好的控制释放的能力,在延长了农药的作用时间的同时对于农民来说,在使用农药时,此产品降低了对人体直接接触的毒害作用。固体微小颗粒状态的农药也减少了降雨淋溶污染水环境和蒸腾作用污染大气环境的概率,也减少了农药的施用量,增强了农药精准施用的效果。The present invention uses nano-hydroxyapatite as a pesticide carrier, considering that nano-hydroxyapatite will release phosphorus under acidic conditions, and the material of nano-hydroxyapatite itself is relatively natural, and will not harm humans or animals and plants under normal circumstances. There are side effects. Therefore, nano-hydroxyapatite is a good natural carrier. On the one hand, loading it with pesticides can reduce the application amount of pesticides, and on the other hand, it can release phosphorus necessary for plant growth, and has a good application prospect. In addition, the microspheres are coated with sodium alginate, which makes the nano pesticides have a good ability to control the release. While prolonging the action time of the pesticides, for farmers, when using pesticides, this product reduces the direct contact with the human body. Toxic effect. Pesticide in the state of solid micro-particles also reduces the probability of rain leaching to pollute the water environment and transpiration to pollute the atmospheric environment, and also reduces the amount of pesticide application and enhances the effect of precise pesticide application.

发明内容SUMMARY OF THE INVENTION

本发明制备了一种有机磷纳米农药,目的在于通过纳米羟基磷灰石的负载和海藻酸钠的包裹,延长农药作用时间,减少农药施用量,增强了农药精准施用的效果。在一定程度上有效解决了农药残留和累积带来的环境问题,为纳米农药提供了良好发展前景。同时纳米羟基磷在控释农药的同时还可以为土壤中的微生物和植物提供磷源。是一种既能够除草又能够提供磷源的纳米农药。The invention prepares an organophosphorus nano pesticide, which aims to prolong the action time of the pesticide, reduce the pesticide application amount, and enhance the effect of precise pesticide application through the loading of nano-hydroxyapatite and the wrapping of sodium alginate. To a certain extent, it effectively solves the environmental problems caused by pesticide residues and accumulation, and provides a good development prospect for nano-pesticides. At the same time, nano-hydroxyphosphorus can provide phosphorus source for microorganisms and plants in the soil while controlling the release of pesticides. It is a nano-pesticide that can both weed and provide phosphorus source.

为实现上述发明目的,本发明采用的技术路线如下:In order to realize the above-mentioned purpose of the invention, the technical route adopted in the present invention is as follows:

(1)将粒径为200nm的纳米羟基磷灰石分别与扑草净乙醇溶液和阿特拉津水溶液搅拌24h,后经过滤烘干后,采用紫外分光光度计分别测定上清液中扑草净和阿特拉津的含量,计算分别得到了负载量为20.8%的扑草净纳米微球和负载量为8.1%的阿特拉津纳米颗粒。(1) The nano-hydroxyapatite with a particle size of 200nm was stirred with the ethanol solution of Promethazine and the aqueous solution of atrazine for 24h, and then filtered and dried, and an ultraviolet spectrophotometer was used to measure the Promethazine in the supernatant, respectively. The contents of net and atrazine were calculated to obtain 20.8% loading of Promethazine nanospheres and 8.1% loading of atrazine nanoparticles, respectively.

(3)将离心管中加入海藻酸钠和负载了农药的纳米羟基磷灰石经过超声震荡后利用注射器将其滴落在CaCl2溶液中,之后经过清洗预冬干燥的处理程序,得到海藻酸钠包裹后的微球。(3) adding sodium alginate and the nano-hydroxyapatite loaded with pesticides into the centrifuge tube, and then using a syringe to drop it into the CaCl solution after ultrasonic vibration, and then through the processing procedure of cleaning and pre-winter drying to obtain alginic acid Sodium-coated microspheres.

(4)研究两种纳米微球在不同温度,pH和光照条件下的控释效果,得出:①在中性和碱性环境下,海藻酸钠凝胶球会发生破裂,其释放速度也要高于酸性条件;②温度对农药的释放基本没有影响;③紫外光可以刺激扑草净的释放,可能是由于扑草净在紫外光照射下容易降解。而正常光照和避光两种环境对于扑草净的释放基本没有影响。三种光照条件对阿特拉津的释放基本没有影响。(4) The controlled release effects of the two kinds of nano-microspheres under different temperature, pH and light conditions were studied, and it was concluded that: (1) In neutral and alkaline environments, the sodium alginate gel spheres would rupture, and the release rate would also decrease. higher than the acidic conditions; ② the temperature had little effect on the release of pesticides; ③ ultraviolet light could stimulate the release of promethazine, which may be due to the easy degradation of promethazine under ultraviolet light irradiation. However, the two environments of normal light and dark light have basically no effect on the release of Promethazine. The three light conditions had little effect on the release of atrazine.

(5)分别对纳米羟基磷灰石,负载农药的羟基磷灰石和被海藻酸钠包裹后形成的凝胶微球进行扫描电镜(SEM)和能谱分析(EDS)表征研究手段,说明了农药成功负载到了纳米羟基磷灰石上,且海藻酸钠也成功包裹了负载农药的纳米羟基磷灰石。(5) Scanning electron microscopy (SEM) and energy dispersive analysis (EDS) were used to characterize nano-hydroxyapatite, pesticide-loaded hydroxyapatite and gel microspheres formed by encapsulating sodium alginate, respectively. The pesticide was successfully loaded on the nano-hydroxyapatite, and the nano-hydroxyapatite loaded with the pesticide was also successfully encapsulated by sodium alginate.

附图说明Description of drawings

图1:(a)为纳米羟基磷灰石SEM图,(b)为负载扑草净的纳米羟基磷灰石SEM图,(c)为扑草净凝胶微球SEM图,(d)为纳米羟基磷灰石EDX图,(e)为负载扑草净的纳米羟基磷灰石EDX图,(f)为扑草净凝胶微球EDX图;Figure 1: (a) is the SEM image of the nano-hydroxyapatite, (b) is the SEM image of the nano-hydroxyapatite loaded with promethazine, (c) is the SEM image of the promethazine gel microspheres, and (d) is the The EDX image of nano-hydroxyapatite, (e) is the EDX image of the nano-hydroxyapatite loaded with Promethazine, and (f) is the EDX image of the Propodazone gel microspheres;

图2:(a)为纳米羟基磷灰石SEM图,(b)为负载阿特拉津的纳米羟基磷灰石SEM图,(c)为阿特拉津凝胶微球SEM图,(d)为纳米羟基磷灰石EDX图,(e)为负载阿特拉津的纳米羟基磷灰石EDX图,(f)为阿特拉津凝胶微球EDX图;Figure 2: (a) SEM image of nano-hydroxyapatite, (b) SEM image of atrazine-loaded nano-hydroxyapatite, (c) SEM image of atrazine gel microspheres, (d) ) is the EDX image of nano-hydroxyapatite, (e) is the EDX image of atrazine-loaded nano-hydroxyapatite, and (f) is the EDX image of atrazine gel microspheres;

图3:(a)为负载扑草净的纳米羟基磷灰石实物图,(b)为负载阿特拉津的纳米羟基磷灰石实物图Figure 3: (a) is the actual picture of the nano-hydroxyapatite loaded with Promethazine, (b) is the actual picture of the nano-hydroxyapatite loaded with atrazine

图4:(a)为扑草净纳米微球随pH变化的累积释放曲线,(b)为扑草净纳米微球随温度变化的累积释放曲线,(c)为扑草净纳米微球随光照变化的累积释放曲线;Figure 4: (a) is the cumulative release curve of Protozam nano-microspheres with pH changes, (b) is the cumulative release curve of Protozam nano-microspheres with temperature changes, (c) is Cumulative release curves of light changes;

图5:(a)为阿特拉津纳米微球随pH变化的累积释放曲线,(b)为阿特拉津纳米微球随温度变化的累积释放曲线,(c)为阿特拉津纳米微球随光照变化的累积释放曲线;Figure 5: (a) is the cumulative release curve of atrazine nanospheres with pH, (b) is the cumulative release curve of atrazine nanospheres with temperature, (c) is atrazine nanospheres Cumulative release curve of microspheres with changes in light;

图6:(a)为纳米羟基磷灰石中磷的释放曲线,(b)为羟基磷灰石纳米微球中磷的释放曲线,(c)为负载农药的纳米羟基磷灰石凝胶微球中磷的释放曲线。Figure 6: (a) is the release curve of phosphorus from nano-hydroxyapatite, (b) is the release curve of phosphorus from hydroxyapatite nanospheres, (c) is the nano-hydroxyapatite gel microspheres loaded with pesticides Phosphorus release profile from spheres.

具体实施方案specific implementation

通过以下各个实施方案,可以使本领域的技术人员更好地了解本发明,有效提高农药施用的精准,减少环境中农药残留。为纳米农药之后的普及奠定了基础研究。Through the following embodiments, those skilled in the art can better understand the present invention, effectively improve the precision of pesticide application, and reduce pesticide residues in the environment. The basic research has been laid for the popularization of nano pesticides.

实施方案1:农药的负载Embodiment 1: Loading of pesticides

(1)扑草净的负载:配置10毫升1mg/ml的扑草净乙醇溶液,并在溶液中加入1g的纳米羟基磷灰石,在锥形瓶内放入转子并用保鲜膜封口后放入磁力搅拌机搅拌24h,24h后用抽滤机抽滤,用少量乙醇清洗负载了农药的纳米羟基磷灰石2-3次,将所得上清液用无水乙醇定容至10ml,再稀释至一定倍数,用紫外分光光度计测量其吸光度。并将滤纸上的材料放入一干净烧杯中,用保鲜膜封口,并在保鲜膜上用针扎细孔,放入60度的负压烘箱内烘干24小时即得到负载了扑草净的纳米羟基磷灰石粉末。(1) Loading of Promethazine: Prepare 10 ml of 1mg/ml Promethazine ethanol solution, add 1g of nano-hydroxyapatite to the solution, put a rotor in the conical flask and seal it with plastic wrap, put it in Stir with a magnetic stirrer for 24 hours. After 24 hours, use a suction filter to filter the nano-hydroxyapatite loaded with pesticides with a small amount of ethanol. multiples, and its absorbance was measured with a UV spectrophotometer. Put the material on the filter paper into a clean beaker, seal it with plastic wrap, poke pores on the plastic wrap, and put it into a 60-degree negative pressure oven to dry for 24 hours to obtain a protoprazine-loaded product. Nano-hydroxyapatite powder.

如图1(d)(e)对比含有N、S两种扑草净特征元素,表明扑草净成功负载在了纳米羟基磷灰石上。As shown in Fig. 1(d)(e), the characteristic elements of promethazine containing N and S are compared, indicating that promethazine was successfully loaded on the nano-hydroxyapatite.

(2)阿特拉津的负载:配置10毫升1mg/ml的阿特拉津丙酮溶液,并在溶液中加入1g的纳米羟基磷灰石成品,在锥形瓶内放入转子并用保鲜膜封口后放入磁力搅拌机搅拌24h,24h后用抽滤机抽滤,用少量丙酮清洗负载了农药的纳米羟基磷灰石2-3次,将所得上清液用丙酮定容至10ml,用水稀释至一定倍数,用紫外分光光度计测量其吸光度。并将滤纸上的材料放入一干净烧杯中,用保鲜膜封口,并在保鲜膜上用针扎细孔,放入60度的负压烘箱内烘干24小时即得到负载了阿特拉津的纳米羟基磷灰石粉末。(2) Atrazine load: configure 10 ml of 1 mg/ml atrazine acetone solution, add 1 g of finished nano-hydroxyapatite to the solution, put a rotor in the conical flask and seal it with plastic wrap Then put it into a magnetic stirrer and stir for 24 hours. After 24 hours, use a suction filter to filter the nano-hydroxyapatite loaded with the pesticide with a small amount of acetone for 2-3 times. A certain multiple is used to measure its absorbance with a UV spectrophotometer. Put the material on the filter paper into a clean beaker, seal it with plastic wrap, prick the pores with a needle on the plastic wrap, and put it in a negative pressure oven at 60 degrees to dry for 24 hours to get the atrazine loaded. of nano-hydroxyapatite powder.

如图2(d)(e)对比含有N、Cl两种阿特拉津特征元素,表明阿特拉津成功负载在纳米羟基磷灰石上。As shown in Figure 2(d)(e), the two characteristic elements of atrazine containing N and Cl are compared, indicating that atrazine is successfully loaded on the nano-hydroxyapatite.

如图3为两种纳米农药的实物图。Figure 3 is the physical map of the two nano-pesticide.

实施方案2:海藻酸钠的包裹Embodiment 2: Encapsulation of sodium alginate

在50ml离心管中加入25ml水,0.1g海藻酸钠和0.25g负载了农药的纳米羟基磷灰石,将其超声至基本看不见大块的固体颗粒后再用涡旋震荡机震荡,将所得溶液由注射器尾部倒入,使其能够从1mm的头部呈连续滴状滴落,将滴落的液体滴加到100ml,0.1mol/l的CaCl2溶液中,可以观察到滴落的液体在CaCl2溶液中形成白色的球状颗粒。全部滴加完毕后,将溶液静置30min,将浮在液面上的颗粒倒掉,其余的溶液及颗粒用滤纸过滤并用蒸馏水清洗2-3次。将滤纸上的颗粒微球倒入干净的锥形瓶中覆盖上保鲜膜在冰箱-20度的环境中预冻30min,30min后将锥形瓶上的保鲜膜用针头扎微小的孔,用冷冻干燥机干燥24h。所得产品即为用海藻酸钠包裹的负载了农药的纳米羟基磷灰石。Add 25ml of water, 0.1g of sodium alginate and 0.25g of pesticide-loaded nano-hydroxyapatite into a 50ml centrifuge tube, sonicate it until no large solid particles are seen, and then shake it with a vortex shaker. The solution is poured from the tail of the syringe, so that it can drip continuously from the head of 1mm, and the dripping liquid is added dropwise to 100ml, 0.1mol/l CaCl2 solution, it can be observed that the dripping liquid is in the White spherical particles formed in the CaCl2 solution. After all the dropwise additions are completed, the solution is allowed to stand for 30 minutes, the particles floating on the liquid surface are poured out, and the remaining solution and particles are filtered with filter paper and washed with distilled water for 2-3 times. Pour the particle microspheres on the filter paper into a clean conical flask, cover with plastic wrap, and pre-freeze in a refrigerator at -20 degrees for 30 minutes. After 30 minutes, prick the plastic wrap on the conical Dryer for 24h. The obtained product is the pesticide-loaded nano-hydroxyapatite wrapped with sodium alginate.

如图1(c)可以明显看出海藻酸钠成功包裹了负载药物的纳米羟基磷灰石,且图1(f)中N、S两种扑草净特征元素存在,所以进一步证明了包裹的成功性。As shown in Figure 1(c), it can be clearly seen that sodium alginate successfully encapsulated the drug-loaded nano-hydroxyapatite, and in Figure 1(f), there are two characteristic elements of promethazine, N and S, which further proves that the encapsulated nano-hydroxyapatite success.

如图2(c)以明显看出海藻酸钠成功包裹了负载药物的纳米羟基磷灰石,且图2(f)N、Cl两种阿特拉津特征元素依然存在,所以进一步证明了包裹的成功性。As shown in Figure 2(c), it is obvious that sodium alginate successfully encapsulated the drug-loaded nano-hydroxyapatite, and in Figure 2(f) the two characteristic elements of atrazine, N and Cl, still exist, which further proves the encapsulation. of success.

实施方案3:两种纳米农药控释效果探究Embodiment 3: Exploration on the controlled release effect of two nano-pesticide

(1)扑草净纳米微球的控释效果(1) Controlled release effect of promethazine nano-microspheres

①:不同pH对扑草净纳米微球控释效果的影响①: The effect of different pH on the controlled release effect of Prometraz nanospheres

先配置1/16mol的磷酸二氢钠溶液和1/16磷酸氢二钠溶液,将两种溶液按照一定配比配置pH为5.5、7.0、8.5的缓释溶液3瓶。在每一个瓶子中装入50ml缓释溶液0.05g扑草净纳米微球,每一种pH做3个平行,每隔一段时间1ml其上清液用紫外分光光度法测其吸光度,并在取样后加入1ml相应的缓释溶液。First prepare 1/16 mol sodium dihydrogen phosphate solution and 1/16 disodium hydrogen phosphate solution, and prepare 3 bottles of slow-release solution with pH 5.5, 7.0, and 8.5 of the two solutions according to a certain ratio. Fill each bottle with 50ml of slow-release solution 0.05g of Protozafloxacin nano-microspheres, make 3 parallels for each pH, and measure the absorbance of 1ml of the supernatant by UV spectrophotometry at regular intervals, and take samples after sampling. Then 1 ml of the corresponding sustained-release solution was added.

如图4(a),碱性条件下释放率最高,而酸性条件下释放率最低,但总得来说,相差并不明显。As shown in Figure 4(a), the release rate is the highest under alkaline conditions and the lowest under acidic conditions, but in general, the difference is not significant.

②:不同温度对扑草净纳米微球控释效果的影响②: The effect of different temperatures on the controlled release effect of Prometraz nanospheres

在瓶子中放入25ml乙醇和0.25g扑草净纳米微球,设定5℃、25℃、45℃3个温度梯度,每隔一段时间取1ml上清液用紫外分光光度法测其吸光度,并在取样后加入1ml无水乙醇。Put 25ml of ethanol and 0.25g of Promethazine nanospheres into the bottle, set 3 temperature gradients of 5°C, 25°C, and 45°C, and take 1ml of supernatant at regular intervals to measure its absorbance by UV spectrophotometry. And add 1 ml of absolute ethanol after sampling.

如图4(b),纳米微球对于温度的变化其控释效果较为稳定,温度对其影响并不明显。As shown in Fig. 4(b), the controlled release effect of the nano-microspheres is relatively stable with the change of temperature, and the effect of temperature on it is not obvious.

③:不同光照条件对扑草净纳米微球控释效果的影响③: The effect of different light conditions on the controlled release effect of Prometraz nanospheres

在瓶子中放入10ml乙醇和0.01g扑草净纳米微球,设定正常光照、避光、紫外三个光照射条件,每个条件设定3个平行,每隔一段时间取其上清液用紫外分光光度法测其吸光度,并在取样后加入1ml的无水乙醇。Put 10ml of ethanol and 0.01g of Prozafon nano-microspheres into the bottle, set three light irradiation conditions of normal light, dark light and ultraviolet light, set 3 parallels for each condition, and take the supernatant at regular intervals The absorbance was measured by ultraviolet spectrophotometry, and 1 ml of absolute ethanol was added after sampling.

如图4(c),在不同的光照条件下,在正常光下和黑暗条件下释放效果一致。但由于扑草净对紫外光较为敏感因此释放率高于正常光照和黑暗条件。As shown in Figure 4(c), under different lighting conditions, the release effect is consistent under normal light and dark conditions. However, the release rate was higher than normal light and dark conditions due to the sensitivity of Promethazine to UV light.

(2)阿特拉津纳米微球的控释效果(2) Controlled release effect of atrazine nanospheres

①:不同pH对阿特拉津纳米微球控释效果的影响①: Effect of different pH on the controlled release effect of atrazine nanospheres

先配置1/16mol的磷酸二氢钠溶液和1/16磷酸氢二钠溶液,将两种溶液按照一定配比配置pH为5.5、7.0、8.5的缓释溶液。在每一个瓶子中装入50ml缓释溶液0.05g阿特拉津纳米微球,每一种pH做3个平行,每隔一段时间1ml其上清液用紫外分光光度法测其吸光度,并在取样后加入1ml相应的缓释溶液,每组数据各设三个平行。First, 1/16 mol of sodium dihydrogen phosphate solution and 1/16 of disodium hydrogen phosphate solution were prepared, and the two solutions were prepared in a certain proportion to prepare a slow-release solution with pH of 5.5, 7.0, and 8.5. Fill each bottle with 50ml of slow-release solution and 0.05g of atrazine nano-microspheres, make 3 parallels for each pH, and measure the absorbance of 1ml of the supernatant by ultraviolet spectrophotometry at regular intervals. After sampling, 1 ml of the corresponding slow-release solution was added, and three parallels were set for each group of data.

如图5(a),阿特拉津纳米微球在pH为5.5和7.0时,累积释放曲线几乎一致,而pH为8.5时累积释放率更高一些,但总体相差不大,可以得出pH对阿特拉津纳米微球的释放基本没有影响。As shown in Figure 5(a), the cumulative release curves of atrazine nanospheres at pH 5.5 and 7.0 are almost the same, while the cumulative release rate is higher at pH 8.5, but the overall difference is not large, it can be concluded that the pH It has little effect on the release of atrazine nanospheres.

②:不同温度对阿特拉津纳米微球控释效果的影响②: The effect of different temperatures on the controlled release of atrazine nanospheres

在瓶子中放入25ml去离子水和0.25g阿特拉津纳米微球,设定5℃、25℃、45℃3个温度梯度,每隔一段时间取1ml上清液用紫外分光光度法测其吸光度,并在取样后加入1ml去离子水,每组各设三个平行。Put 25ml of deionized water and 0.25g of atrazine nanospheres in the bottle, set 3 temperature gradients of 5°C, 25°C, and 45°C, and take 1ml of the supernatant at intervals and measure it by UV spectrophotometry Its absorbance, and add 1 ml of deionized water after sampling, each set three parallel.

如图5(b),不同温度下阿特拉津的累积释放浓度曲线基本一致,所以温度基本不影响阿特拉津的释放。As shown in Figure 5(b), the cumulative release concentration curves of atrazine at different temperatures are basically the same, so the temperature basically does not affect the release of atrazine.

③:不同光照条件对阿特拉津纳米微球控释效果的影响③: The effect of different light conditions on the controlled release of atrazine nanospheres

在瓶子中放入10ml去离子水和0.01g阿特拉津纳米微球,设定正常光照、避光、紫外光照3个条件,每个条件设定3个平行,每隔一段时间取其上清液用紫外分光光度法测其吸光度,并在取样后加入1ml的去离子水。Put 10ml of deionized water and 0.01g of atrazine nano-microspheres in the bottle, set 3 conditions of normal light, dark light, and ultraviolet light, and set 3 parallels for each condition, and take the top at regular intervals. The absorbance of the supernatant was measured by UV spectrophotometry, and 1 ml of deionized water was added after sampling.

如图5(c),无光照条件下阿特拉津纳米微球的累积释放率最高,正常光照次之,紫外条件下最低,但总体来说三者相差不大,因此也可以得出不同光照条件对阿特拉津的累积释放无明显作用。As shown in Figure 5(c), the cumulative release rate of atrazine nanospheres is the highest under no-light conditions, followed by normal light, and the lowest under UV conditions, but in general the three are not much different, so it can be concluded that different Light conditions had no significant effect on the cumulative release of atrazine.

实施方案4:磷的释放Embodiment 4: Release of Phosphorus

称取一定质量的纳米羟基磷灰石,含有等质量纳米羟基磷灰石的凝胶球和含有等质量纳米羟基磷灰石的农药凝胶微球。放入pH为5.5、7.0、8.5的缓冲溶液中。每隔一段时间取出溶液测定其正磷酸盐的含量,并加入等体积的缓冲溶液,每个实验组各设三个平行。Weigh a certain mass of nano-hydroxyapatite, gel spheres containing the same mass of nano-hydroxyapatite, and pesticide gel microspheres containing the same mass of nano-hydroxyapatite. Put into buffer solutions with pH 5.5, 7.0, 8.5. The solution was taken out at intervals to measure the content of orthophosphate, and an equal volume of buffer solution was added, and three parallels were set for each experimental group.

如图6,三种pH条件下均测出正磷酸盐的释放,且酸性条件下正磷酸盐的释放率大于中性和碱性。表明所制备的pH响应控释凝胶微球可以为土壤中微生物和植物提供所需磷源。As shown in Figure 6, the release of orthophosphate was measured under the three pH conditions, and the release rate of orthophosphate under acidic conditions was greater than that of neutral and alkaline conditions. It is indicated that the prepared pH-responsive controlled-release gel microspheres can provide the required phosphorus source for microorganisms and plants in soil.

Claims (4)

1. The invention discloses a preparation method of a pH response controlled release type nano pesticide based on a hydroxyapatite carrier.
2. The preparation method of the pH response controlled release type nano pesticide according to claim 1 is characterized in that:
(1) weighing nano-hydroxyapatite with the particle size of 200nm at normal temperature, and loading the atrazine solution and the prometryn solution on the nano-hydroxyapatite by stirring;
(2) sodium alginate is used for wrapping the nano-hydroxyapatite loaded with the pesticide, and a calcium chloride solution is dripped into the nano-hydroxyapatite to prepare the gel microsphere.
3. The preparation method of the pH response controlled release type nano pesticide according to claim 1 is characterized in that:
(1) the load rate of prometryn is 20.8%, and the load rate of atrazine is 8.1%;
(2) the prometryn nano microsphere can realize a pH response controlled release effect under the condition that the pH is 5.5, and the release of the prometryn nano microsphere is not influenced by the temperature. But it releases rapidly under uv light compared to darkness and normal light;
(3) the atrazine nano-microsphere can realize an intelligent controlled release effect under the condition that the pH value is 5.5, and the release process is not influenced by temperature and different illumination and is relatively stable;
(4) under normal experimental conditions, the release of orthophosphate can be measured under different pH conditions. And the release rate under the acidic condition is higher than that of neutral and alkaline.
4. The preparation method of the pH response controlled release type nano pesticide according to claim 1 is characterized in that:
(1) the nano-microspheres are characterized by means of a scanning electron microscope, energy spectrum scanning and the like, and show that the prometryn and the atrazine are successfully loaded on the nano-hydroxyapatite to successfully prepare the nano-pesticide gel microspheres.
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