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CN102217595B - Phytocide granule and preparation method of granule - Google Patents

Phytocide granule and preparation method of granule Download PDF

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CN102217595B
CN102217595B CN 201110098913 CN201110098913A CN102217595B CN 102217595 B CN102217595 B CN 102217595B CN 201110098913 CN201110098913 CN 201110098913 CN 201110098913 A CN201110098913 A CN 201110098913A CN 102217595 B CN102217595 B CN 102217595B
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herbicide
aqueous solution
bentonite
granule
carboxymethyl chitosan
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CN102217595A (en
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李建法
李益民
吕金红
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University of Shaoxing
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Abstract

The invention discloses a phytocide granule and a preparation method of the granule. The preparation method is characterized by including the steps of respectively adding phytocide and bentonite in carboxymethyl chitosan solution, uniformly mixing, dropping the mixed solution in cross-linking agent solution, heating to finish surface cross-linking to obtain solid particles and drying the solid particles to obtain the granular preparation of phytocide. In application, the granule can delay the release of phytocide, reduce drug consumption, prolong action time, improve utilization rate of phytocide and control the pollution of phytocide to the environment.

Description

一种除草剂颗粒剂及其制备方法A kind of herbicide granule and preparation method thereof

技术领域: Technical field:

本发明涉及一种除草剂颗粒剂及其制备方法,具体是指一种以膨润土和羧甲基壳聚糖为载体的除草剂颗粒剂及其制备方法。 The invention relates to a herbicide granule and a preparation method thereof, in particular to a herbicide granule with bentonite and carboxymethyl chitosan as carriers and a preparation method thereof.

背景技术: Background technique:

我国农田杂草面多量广,人工除草效率低、费用高,导致化学除草技术使用面积不断扩大。但是,现有除草剂以乳油等常规剂型为主,施用到植物或土壤后,大部分除草剂活性成分随地表径流流失、或者随土壤水分垂直运动淋失,进入地表或地下水体系,一方面降低了除草剂利用效率,另一方面带来严重的环境污染问题。采用缓释技术可以按照防治目标要求,合理调节除草剂活性成分的释放速度,从而提高药效、延长持效期。其次,通过控制除草剂释放量,可以减少除草剂在环境中的迁移,从源头上控制污染。 There are many weeds in my country's farmland, and the efficiency of manual weeding is low and the cost is high, which leads to the continuous expansion of the area where chemical weeding technology is used. However, the existing herbicides are mainly in conventional formulations such as emulsifiable concentrates. After being applied to plants or soil, most of the active ingredients of herbicides will be lost with the surface runoff, or leached with the vertical movement of soil moisture, and enter the surface or groundwater system. It reduces the utilization efficiency of herbicides, and on the other hand, it brings serious environmental pollution problems. The use of slow-release technology can reasonably adjust the release rate of herbicide active ingredients according to the requirements of control objectives, so as to improve the efficacy and prolong the duration of efficacy. Secondly, by controlling the release of herbicides, the migration of herbicides in the environment can be reduced and pollution can be controlled from the source.

目前,除草剂缓释技术可分为物理型缓释和化学型缓释两大类。前者主要依靠载体与除草剂活性成分之间的物理结合,除草剂活性基本不受载体影响,而且缓释剂型加工相对容易,发展较快(汪宝卿等, 应用化工, 2005, 34: 519–523)。物理型缓释技术中研究较多的主要有微胶囊包载技术和吸附材料负载技术。微胶囊技术中,首先将原药分散成微细液滴,然后用聚氨酯、脲醛树脂等高分子化合物包裹,形成膜内包载活性成分的胶囊结构,使用时随着活性成分透过膜壁向外扩散而达到缓释的目的。但是,微胶囊生产技术要求高、成型工艺复杂、囊壁易破裂从而影响缓释效果。利用吸附材料做载体制备除草剂缓释制剂,具有工艺简单、成本低的优势。其中,粘土类材料资源丰富、价格低廉、比表面积大,且容易改性,进而制备对除草剂具有良好吸附性能的改性粘土,用作除草剂制剂载体(Y El-Nahhal等, Pestic Sci, 1999, 55: 857–864)。但是,粘土类载体本身对除草剂的负载量较低,除草剂的质量含量通常在4%以下,载药量提高后缓释效果明显变差。为此,有必要在现有技术基础上开发载药量高、缓释效果好的新型除草剂制剂。 At present, herbicide slow-release technology can be divided into two categories: physical slow-release and chemical slow-release. The former mainly relies on the physical combination between the carrier and the active ingredients of the herbicide, and the herbicide activity is basically not affected by the carrier, and the slow-release dosage form is relatively easy to process and develops rapidly (Wang Baoqing et al., Applied Chemical Industry, 2005, 34: 519–523) . Among the physical sustained-release technologies, there are mainly microcapsule entrapment technology and adsorption material loading technology. In the microcapsule technology, the original drug is first dispersed into fine droplets, and then wrapped with polyurethane, urea-formaldehyde resin and other polymer compounds to form a capsule structure containing active ingredients in the membrane. When used, the active ingredients diffuse outward through the membrane wall. To achieve the purpose of slow release. However, the production technology of microcapsules is high, the molding process is complicated, and the capsule wall is easily broken, which affects the sustained-release effect. The herbicide sustained-release preparation is prepared by using the adsorption material as a carrier, which has the advantages of simple process and low cost. Among them, clay materials are rich in resources, low in price, large in specific surface area, and easy to modify, thereby preparing modified clays with good adsorption properties for herbicides and used as herbicide formulation carriers (Y El-Nahhal et al., Pestic Sci, 1999, 55: 857–864). However, the clay-based carrier itself has a low loading capacity of the herbicide, and the mass content of the herbicide is usually below 4%, and the slow-release effect becomes significantly worse after the drug loading increases. Therefore, it is necessary to develop new herbicide preparations with high drug loading and good sustained-release effect based on the existing technology.

发明内容: Invention content:

本发明的第一方面目的在于提供一种以膨润土和羧甲基壳聚糖为载体的除草剂颗粒剂,应用本发明,可延缓除草剂的释放,降低施药量、延长作用时间,提高除草剂利用率、控制除草剂对环境的污染。 The purpose of the first aspect of the present invention is to provide a kind of herbicide granule with bentonite and carboxymethyl chitosan as the carrier. Application of the present invention can delay the release of herbicide, reduce application amount, prolong action time, and improve weed control. Herbicide utilization rate, control herbicide pollution to the environment.

为了达到上述目的,本发明采取的技术方案是: In order to achieve the above object, the technical scheme that the present invention takes is:

一种除草剂颗粒剂,其特征在于:将除草剂、膨润土分别加入羧甲基壳聚糖溶液中,混合均匀,将上述混合液滴入交联剂溶液中,加热完成表面交联,得固体颗粒物,将固体颗粒物干燥即得到除草剂颗粒制剂。 A herbicide granule, which is characterized in that: the herbicide and bentonite are respectively added to the carboxymethyl chitosan solution, mixed evenly, the above mixed solution is dropped into the cross-linking agent solution, and the surface cross-linking is completed by heating to obtain a solid Granules, the solid granules are dried to obtain herbicide granules.

进一步的限定在于: Further restrictions are:

所述除草剂是指农业生产中使用的以除灭杂草、保护农作物正常生长为目的的各类天然或合成化学品。 The herbicides refer to various natural or synthetic chemicals used in agricultural production for the purpose of eliminating weeds and protecting the normal growth of crops.

所述膨润土是指以蒙脱石为主要成分的层状粘土矿物,包括为提高其对除草剂的吸附性能所制备的改性膨润土。膨润土层间可交换阳离子为钙离子或钠离子,改性膨润土是指采用现有技术由膨润土与金属阳离子、无机酸氢离子、阳离子表面活性剂等发生离子交换反应后所得到的产物。 The bentonite refers to layered clay minerals with montmorillonite as the main component, including modified bentonite prepared for improving the adsorption performance of herbicides. The exchangeable cations between the bentonite layers are calcium ions or sodium ions, and the modified bentonite refers to the product obtained by ion exchange reaction between bentonite and metal cations, inorganic acid hydrogen ions, cationic surfactants, etc. by using the prior art.

所述羧甲基壳聚糖是指壳聚糖分子结构上氨基和羟基被羧甲基取代后所得到的水溶性衍生物,其取代度在0.3~0.99之间,可通过购买市面已有产品或采用现有制备方法获取。 The carboxymethyl chitosan refers to the water-soluble derivative obtained after the amino group and the hydroxyl group on the chitosan molecular structure are substituted by carboxymethyl groups, and its degree of substitution is between 0.3 and 0.99, which can be obtained by purchasing existing products on the market Or obtain by using existing preparation methods.

所述的交联剂为多价金属阳离子如钙离子的水溶性盐类化合物,或多醛类化合物如戊二醛,或为上述两种交联剂以一定比例和形式的混合,本发明的交联剂是以水溶液的形式参与到本发明的制备方法中的。 The cross-linking agent is a water-soluble salt compound of a multivalent metal cation such as calcium ion, or a polyaldehyde compound such as glutaraldehyde, or a mixture of the above two cross-linking agents in a certain proportion and form. The crosslinking agent participates in the preparation method of the present invention in the form of aqueous solution.

本发明的以膨润土和羧甲基壳聚糖为载体的除草剂颗粒剂,利用羧甲基壳聚糖的水溶性制备能够包裹除草剂的混合液;利用羧甲基壳聚糖的快速交联反应制备成形颗粒制剂;利用交联羧甲基壳聚糖的包裹和膨润土吸附作用提高制剂的载药量,延长除草剂的释放时间;利用羧甲基壳聚糖的胺基阳离子特性,强化对含羧酸类除草剂的缓释效果。 The herbicide granule with bentonite and carboxymethyl chitosan as the carrier of the present invention uses the water solubility of carboxymethyl chitosan to prepare a mixed solution capable of wrapping the herbicide; utilizes the rapid crosslinking of carboxymethyl chitosan Reaction to prepare shaped granule preparations; using cross-linked carboxymethyl chitosan to wrap and bentonite adsorption to increase the drug loading of the preparation and prolong the release time of herbicides; Sustained-release effects of carboxylic acid-containing herbicides.

本发明的另一方面目的是提供一种上述除草剂颗粒剂的制备方法,包括以下步骤:配制羧甲基壳聚糖含量为0.5%~10%(质量百分比,下同)的水溶液,将膨润土和除草剂加入,搅拌混合均匀,其中膨润土加入量与羧甲基壳聚糖的质量比为0.2~5:1,除草剂加入量与羧甲基壳聚糖的质量比为0.1~2:1。将所得混合液滴入交联剂溶液中,加热交联1~9分钟后,得固体颗粒物,干燥得到除草剂颗粒剂。 Another object of the present invention is to provide a preparation method of the above-mentioned herbicide granules, comprising the following steps: preparing an aqueous solution with a carboxymethyl chitosan content of 0.5% to 10% (mass percentage, the same below), and mixing bentonite Add herbicide, stir and mix evenly, wherein the mass ratio of bentonite to carboxymethyl chitosan is 0.2~5:1, and the mass ratio of herbicide to carboxymethyl chitosan is 0.1~2:1 . The obtained mixed liquid is dropped into the cross-linking agent solution, heated and cross-linked for 1-9 minutes to obtain solid particles, and dried to obtain herbicide granules.

本发明的有益效果为:(1)可使除草剂的释放时间延长到300小时以上,从而延长持效期,减少了重复施用除草剂的次数和用量,有利于控制农药污染问题;(2)可得到成型的颗粒剂,提高除草剂使用的便利和安全性;(3)与单纯膨润土负载相比,提高了除草剂的载药量,延长了除草剂释放时间。 The beneficial effects of the present invention are: (1) the release time of the herbicide can be extended to more than 300 hours, thereby prolonging the effective period, reducing the frequency and dosage of repeated application of the herbicide, which is beneficial to control the problem of pesticide pollution; (2) Formed granules can be obtained, which improves the convenience and safety of herbicide use; (3) Compared with simple bentonite loading, it increases the drug loading of herbicide and prolongs the release time of herbicide.

附图说明: Description of drawings:

图1为本发明实施例1~3制备的除草剂的释放率曲线图; Fig. 1 is the release rate curve figure of the herbicide prepared by the embodiment of the present invention 1~3;

图2为本发明对比实施例1~3制备的除草剂的释放率曲线图。 Fig. 2 is a graph showing the release rate of herbicides prepared in Comparative Examples 1-3 of the present invention.

具体实施方式: Detailed ways:

实施例1: Example 1:

将5 g 羧甲基壳聚糖加入100 g水中,搅拌至其完全溶解,然后加入膨润土3 g、除草剂2,4-D丁酯(2,4-二氯苯氧乙酸丁酯)2 g,充分搅拌混合为均匀悬浮液。配制质量浓度为6%的氯化钙(交联剂)水溶液1000 mL,将上述悬浮液用蠕动泵滴加到交联剂溶液中,在60℃下反应5 分钟后得到颗粒状产物,将颗粒滤出,然后在70℃下干燥2 h,得到平均粒径约0.8 毫米的除草剂颗粒制剂。经提取分析,制剂中2,4-D丁酯的质量含量为18.2%,2,4-D丁酯的包载率为91.0%。 Add 5 g of carboxymethyl chitosan into 100 g of water, stir until it is completely dissolved, then add 3 g of bentonite, 2 g of herbicide 2,4-D-butyl (2,4-dichlorophenoxybutyl acetate) , stir thoroughly to form a homogeneous suspension. Prepare 1000 mL of calcium chloride (cross-linking agent) aqueous solution with a mass concentration of 6%, add the above suspension into the cross-linking agent solution dropwise with a peristaltic pump, and react at 60°C for 5 minutes to obtain a granular product. Filter out and then dry at 70°C for 2 h to obtain herbicide granules with an average particle size of about 0.8 mm. After extraction and analysis, the mass content of 2,4-D butyl ester in the preparation was 18.2%, and the loading rate of 2,4-D butyl ester was 91.0%.

将上述制备的除草剂制剂进行释放实验,取制剂样品100 mg放入1000 mL水中,间隔一定时间后取水样分析其中的除草剂质量,计算不同时间下除草剂的释放率(即释放到水中的除草剂质量占制剂中原有质量的百分比),结果见图1。除草剂分析方法可采用农药分析技术领域众所周知的色谱方法。 The herbicide preparation prepared above was subjected to a release experiment, and 100 mg of the preparation sample was put into 1000 mL of water. After a certain interval, water samples were taken to analyze the quality of the herbicide in it, and the release rate of the herbicide at different times was calculated (i.e., released into the water). The mass of herbicide accounts for the percentage of the original mass in the preparation), and the results are shown in Figure 1. As a herbicide analysis method, a well-known chromatographic method in the technical field of pesticide analysis can be used.

实施例2: Example 2:

取膨润土4.5 g,与10 mL质量浓度为20%的硫酸水溶液进行离子交换反应后,离心分离出固体物,经干燥得到酸活化膨润土4.0 g。 Take 4.5 g of bentonite, perform ion exchange reaction with 10 mL of sulfuric acid aqueous solution with a mass concentration of 20%, centrifuge to separate the solid, and dry to obtain 4.0 g of acid-activated bentonite.

将上述酸活化膨润土加入100 g羧甲基壳聚糖水溶液中(羧甲基壳聚糖质量含量为3%),搅拌均匀后,加入除草剂异丙甲草胺3 g,充分搅拌混合为均匀悬浮液。然后用蠕动泵滴加到如实施例1所述的交联剂溶液中,在60℃下反应3分钟后得到颗粒状产物,然后在70℃下干燥2 h,得到平均粒径约0.9毫米的除草剂制剂,其中异丙甲草胺质量含量经提取分析为26.5%,异丙甲草胺的包载率为88.3%。取该制剂样品70 mg,采用实施例1所述方法进行释放实验,得到不同时间下除草剂的释放率,结果见图1。 Add the above-mentioned acid-activated bentonite to 100 g of carboxymethyl chitosan aqueous solution (the mass content of carboxymethyl chitosan is 3%), stir evenly, add 3 g of herbicide metolachlor, fully stir and mix until uniform suspension. Then use a peristaltic pump to drop into the cross-linking agent solution as described in Example 1, react at 60°C for 3 minutes to obtain a granular product, then dry at 70°C for 2 h to obtain an average particle diameter of about 0.9 mm The herbicide preparation, wherein the mass content of metolachlor is 26.5% after extraction and analysis, and the entrapment rate of metolachlor is 88.3%. Take 70 mg of the preparation sample, adopt the method described in Example 1 to carry out the release experiment, and obtain the release rate of the herbicide at different times, the results are shown in Figure 1.

实施例3: Example 3:

取膨润土3 g,与30 mL 质量浓度为2%的十六烷基二甲基氯化铵水溶液进行离子交换反应后,离心分离出固体物,经干燥得到有机改性膨润土3.1 g。 3 g of bentonite was taken, and after ion exchange reaction with 30 mL of cetyldimethylammonium chloride aqueous solution with a mass concentration of 2%, the solid was separated by centrifugation, and 3.1 g of organically modified bentonite was obtained by drying.

配制质量含量为4%的羧甲基壳聚糖水溶液100 g,依次加入上述有机改性膨润土和除草剂甲草胺4 g,充分搅拌混合为均匀悬浮液。分别配制质量浓度为10%的氯化钙水溶液、戊二醛水溶液各500 mL,混合均匀后用作交联剂。将上述悬浮液用蠕动泵滴加到交联剂溶液中,在50℃下反应3分钟后得到颗粒状产物,将颗粒滤出,然后在70℃下干燥2 h,得到平均粒径约1.0 毫米的除草剂颗粒制剂。经提取分析,制剂中甲草胺的质量含量为33.8%,甲草胺的包载率为93.9%。取该制剂样品55 mg,采用实施例1所述方法进行释放实验,得到不同时间下除草剂的释放率,结果见图1。 Prepare 100 g of carboxymethyl chitosan aqueous solution with a mass content of 4%, add the above-mentioned organically modified bentonite and 4 g of the herbicide alachlor in sequence, and stir thoroughly to form a uniform suspension. Prepare 500 mL of calcium chloride aqueous solution and glutaraldehyde aqueous solution with a mass concentration of 10%, respectively, and use them as cross-linking agents after mixing evenly. Add the above suspension into the crosslinking agent solution dropwise with a peristaltic pump, react at 50°C for 3 minutes to obtain a granular product, filter the particles, and then dry at 70°C for 2 hours to obtain an average particle size of about 1.0 mm herbicide granules. After extraction and analysis, the mass content of alachlor in the preparation was 33.8%, and the loading rate of alachlor was 93.9%. Take 55 mg of the preparation sample, and use the method described in Example 1 to carry out the release experiment to obtain the release rate of the herbicide at different times. The results are shown in Figure 1.

对比实施例1: Comparative Example 1:

在100 g水中加入膨润土8 g、除草剂2,4-D丁酯2 g,充分搅拌混合均匀。因膨润土不能发生交联反应,故将该悬浮液离心分离出固体物,然后在70℃下干燥2 h,得到粉状的除草剂制剂。经提取分析,制剂中2,4-D丁酯的质量含量为7.8%,包载率为39.0%。取该粉状制剂200 mg,采用实施例1所述方法进行释放实验,得到不同时间下除草剂的释放率,结果见图2。 Add 8 g of bentonite and 2 g of herbicide 2,4-D butyl ester into 100 g of water, stir well and mix well. Because bentonite cannot undergo cross-linking reaction, the suspension was centrifuged to separate the solid matter, and then dried at 70 °C for 2 h to obtain a powdered herbicide preparation. After extraction and analysis, the mass content of 2,4-D butyl ester in the preparation was 7.8%, and the loading rate was 39.0%. Take 200 mg of this powdery preparation, adopt the method described in Example 1 to carry out the release experiment, and obtain the release rate of the herbicide at different times, the results are shown in Figure 2.

对比实施例2: Comparative example 2:

在100 g水中加入酸活化膨润土7 g、除草剂异丙甲草胺3 g,充分搅拌混合均匀。将所得悬浮液离心分离出固体物,然后在70℃下干燥2 h,得到粉状的除草剂制剂。经提取分析,制剂中异丙甲草胺的质量含量为10.1%,包载率为33.6%。取粉状制剂150 mg,采用实施例1所述方法进行释放实验,得到不同时间下除草剂的释放率,结果见图2。 Add 7 g of acid-activated bentonite and 3 g of herbicide metolachlor into 100 g of water, stir well and mix well. The resulting suspension was centrifuged to separate the solid matter, and then dried at 70 °C for 2 h to obtain a powdered herbicide formulation. After extraction and analysis, the mass content of metolachlor in the preparation was 10.1%, and the entrapment rate was 33.6%. Get 150 mg of powdery preparation, adopt the method described in Example 1 to carry out release experiment, obtain the release rate of herbicide under different time, the results are shown in Figure 2.

对比实施例3: Comparative example 3:

在100 g水中加入有机改性膨润土7.1 g、除草剂甲草胺4 g,充分搅拌混合均匀。将所得悬浮液离心分离出固体物,然后在70℃下干燥2 h,得到粉状的除草剂制剂。经提取分析,制剂中甲草胺的质量含量为14.9%,包载率为41.3%。取粉状制剂100 mg,采用实施例1所述方法进行释放实验,得到不同时间下除草剂的释放率,结果见图2。 Add 7.1 g of organically modified bentonite and 4 g of herbicide alachlor into 100 g of water, stir well and mix evenly. The resulting suspension was centrifuged to separate the solid matter, and then dried at 70 °C for 2 h to obtain a powdered herbicide formulation. After extraction and analysis, the mass content of alachlor in the preparation was 14.9%, and the entrapment rate was 41.3%. Take 100 mg of powdery preparation, adopt the method described in Example 1 to carry out release experiment, obtain the release rate of herbicide under different time, the results are shown in Figure 2.

效果对照: Effect comparison:

结合图1、图2可以看出,本发明采用以膨润土和羧甲基壳聚糖为载体的除草剂颗粒剂;利用交联羧甲基壳聚糖的包裹和膨润土吸附作用提高制剂的载药量,延长除草剂的释放时间;利用羧甲基壳聚糖的胺基阳离子特性,强化对含羧酸类除草剂的缓释效果;从而可使除草剂的释放时间延长到300小时以上,提高了持效期,减少了重复施用除草剂的次数和用量,有利于控制农药污染问题;而传统的单纯膨润土负载,其释放时间仅仅为70小时左右,因此,本发明与现有技术相比,提高了除草剂的载药量,延长了除草剂释放时间。 Can find out in conjunction with Fig. 1, Fig. 2, the present invention adopts the herbicide granule with bentonite and carboxymethyl chitosan as carrier; Utilize the encapsulation of cross-linked carboxymethyl chitosan and the adsorption of bentonite to improve the drug loading of preparation amount, prolong the release time of herbicides; use the amino cationic characteristics of carboxymethyl chitosan to strengthen the slow-release effect on herbicides containing carboxylic acids; thus the release time of herbicides can be extended to more than 300 hours, improving The duration of effect is improved, the number of times and the amount of repeated application of herbicides are reduced, which is beneficial to control the problem of pesticide pollution; while the traditional simple bentonite load, its release time is only about 70 hours. Therefore, compared with the prior art, the present invention has The drug loading capacity of the herbicide is increased, and the release time of the herbicide is prolonged.

Claims (3)

1.一种除草剂颗粒剂,其特征在于:将5 g 羧甲基壳聚糖加入100 g水中,搅拌至其完全溶解,然后加入膨润土3 g、除草剂2,4-D丁酯2 g,充分搅拌混合为均匀悬浮液,配制质量浓度为6%的氯化钙水溶液1000 mL,将上述悬浮液用蠕动泵滴加到氯化钙水溶液中,在60℃下反应5 分钟后得到颗粒状产物,将颗粒滤出,然后在70℃下干燥2 h,得到平均粒径约0.8 毫米的除草剂颗粒制剂。 1. A herbicide granule, characterized in that: 5 g of carboxymethyl chitosan is added to 100 g of water, stirred until it is completely dissolved, then 3 g of bentonite, 2 g of herbicide 2,4-D butyl ester are added , fully stirred and mixed into a uniform suspension, prepared 1000 mL of calcium chloride aqueous solution with a mass concentration of 6%, added the above suspension into the calcium chloride aqueous solution with a peristaltic pump, and reacted at 60°C for 5 minutes to obtain granular product, the particles were filtered out, and then dried at 70°C for 2 h to obtain a herbicide granule preparation with an average particle size of about 0.8 mm. 2.一种除草剂颗粒剂,其特征在于:取膨润土4.5 g,与10 mL质量浓度为20%的硫酸水溶液进行离子交换反应后,离心分离出固体物,经干燥得到酸活化膨润土4.0 g,将上述酸活化膨润土加入100 g羧甲基壳聚糖水溶液中,羧甲基壳聚糖质量含量为3%,搅拌均匀后,加入除草剂异丙甲草胺3 g,充分搅拌混合为均匀悬浮液,配制质量浓度为6%的氯化钙水溶液1000 mL,将上述悬浮液用蠕动泵滴加到氯化钙水溶液中,在60℃下反应3分钟后得到颗粒状产物,然后在70℃下干燥2 h,得到平均粒径约0.9毫米的除草剂制剂。 2. a herbicide granule, is characterized in that: get bentonite 4.5 g, after carrying out ion exchange reaction with 10 mL mass concentration of 20% sulfuric acid aqueous solution, centrifuge and separate solid matter, obtain acid-activated bentonite 4.0 g through drying, Add the above-mentioned acid-activated bentonite into 100 g of carboxymethyl chitosan aqueous solution, the mass content of carboxymethyl chitosan is 3%, after stirring evenly, add 3 g of herbicide metolachlor, fully stir and mix to form a uniform suspension solution, prepare 1000 mL of calcium chloride aqueous solution with a mass concentration of 6%, drop the above suspension into the calcium chloride aqueous solution with a peristaltic pump, react at 60°C for 3 minutes to obtain a granular product, and then Dry for 2 h to obtain a herbicide formulation with an average particle size of about 0.9 mm. 3.一种除草剂颗粒剂,其特征在于:取膨润土3 g,与30 mL 质量浓度为2%的十六烷基二甲基氯化铵水溶液进行离子交换反应后,离心分离出固体物,经干燥得到有机改性膨润土3.1 g;配制质量含量为4%的羧甲基壳聚糖水溶液100 g,依次加入上述有机改性膨润土和除草剂甲草胺4 g,充分搅拌混合为均匀悬浮液,分别配制质量浓度为10%的氯化钙水溶液、戊二醛水溶液各500 mL,混合均匀后用作交联剂,将上述悬浮液用蠕动泵滴加到交联剂溶液中,在50℃下反应3分钟后得到颗粒状产物,将颗粒滤出,然后在70℃下干燥2 h,得到平均粒径约1.0 毫米的除草剂颗粒制剂。 3. a herbicide granule, is characterized in that: get bentonite 3 g, after carrying out ion exchange reaction with 30 mL mass concentration of 2% hexadecyl dimethyl ammonium chloride aqueous solution, centrifugal separation solid matter, After drying, 3.1 g of organically modified bentonite was obtained; 100 g of carboxymethyl chitosan aqueous solution with a mass content of 4% was prepared, and the above-mentioned organically modified bentonite and herbicide alachlor 4 g were added in sequence, and fully stirred and mixed to form a uniform suspension , respectively prepare 500 mL of calcium chloride aqueous solution and glutaraldehyde aqueous solution with a mass concentration of 10%, and use it as a crosslinking agent after mixing evenly. The above suspension is added dropwise to the crosslinking agent solution with a peristaltic pump. After reacting at low temperature for 3 minutes, a granular product was obtained. The particles were filtered out, and then dried at 70°C for 2 hours to obtain a herbicide granule formulation with an average particle size of about 1.0 mm.
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