WO2023005127A1 - Algae inhibitor and preparation method therefor - Google Patents

Algae inhibitor and preparation method therefor Download PDF

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Publication number
WO2023005127A1
WO2023005127A1 PCT/CN2021/141047 CN2021141047W WO2023005127A1 WO 2023005127 A1 WO2023005127 A1 WO 2023005127A1 CN 2021141047 W CN2021141047 W CN 2021141047W WO 2023005127 A1 WO2023005127 A1 WO 2023005127A1
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preparation
algae
algae inhibitor
inhibitor
carrier
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PCT/CN2021/141047
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French (fr)
Chinese (zh)
Inventor
高静思
巫俊铭
陈菊
廖萍
罗红梅
陈海珊
陈佳旭
吴玉婵
何钟亿
谢志旋
王卫华
罗乔
赖敏
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深圳职业技术学院
吉安职业技术学院
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Publication of WO2023005127A1 publication Critical patent/WO2023005127A1/en

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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/50Treatment of water, waste water, or sewage by addition or application of a germicide or by oligodynamic treatment

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  • the invention relates to the technical field of algae control, in particular to an algae inhibitor and a preparation method thereof.
  • the eutrophication of the water body causes a large number of algae to multiply in the water, which causes the pressure of the raw water treatment of the water plant and brings risks to the safe water supply of the city.
  • the control of algae is mainly divided into two categories.
  • the first category is to solve the problem of eutrophication as the fundamental purpose, to control the nutrients necessary for the growth of algae as the main way, and to intercept pollution, control sources, and overall restoration as the core means.
  • Systematic reservoir in situ restoration program This type of technology focuses on "rectifying the source” and is the most fundamental solution to the problem from a long-term perspective. However, it has many influencing factors, takes a long time, and is slow to take effect. Some water bodies with serious endogenous pollution may need to experience ten years of treatment. It will take years or even decades of hard work to completely eliminate the risk of algal blooms.
  • the second category is in-situ short-term algae control technology, which uses various physical, chemical and biological means to inhibit the growth of algae or remove a large number of algae to ensure the safety of water bodies.
  • the physical methods include water pumping and aeration anti-algae technology, ultraviolet radiation anti-algae technology, etc.
  • the chemical method is typically represented by adding algae-inhibiting chemicals such as copper sulfate
  • the biological method mainly adopts fish stocking, microbial breeding and aquatic plant planting and other methods.
  • physical methods and traditional biological methods have the disadvantages of long operation time, difficulty and high cost; chemical methods may destroy the ecological balance and cause secondary pollution.
  • the purpose of the present invention is to provide an algae inhibitor and a preparation method thereof, which are used to solve the problems that existing algae control is likely to cause secondary pollution and destroy ecology.
  • the present invention provides a method for preparing an algae inhibitor, which includes:
  • the algae inhibitor is obtained.
  • the botanical medicinal material is selected from one or more of crane lily, reed, big weed, water sword leaf, litchi leaf, magnolia and renmianzi.
  • the carrier is selected from one of zeolite, carbon nanotube and organic framework material.
  • the step of obtaining the algae inhibitor specifically includes:
  • the semi-finished product is put into drying equipment to dry to obtain the algae inhibitor.
  • the solvent is water.
  • the filler is hydroxypropyl starch and/or hypromellose.
  • the mass ratio of the plant drug powder to the filler is 100:0.1-5.
  • the particle size of the particles is 50-100 nm.
  • an algae inhibitor is prepared by the above-mentioned preparation method.
  • the algae inhibitor wherein, the algae inhibitor also includes a base material for carrying the algae inhibitor, the base material is provided with several mesh holes, and the algae inhibitor is fixed on the inside the mesh.
  • the embodiment of the present invention provides an algae inhibitor and a preparation method, wherein the preparation method has a simple process, and each raw material component is easy to obtain, and does not involve toxic or harmful solvents.
  • the prepared algae inhibitor can effectively reproduce algae, is environmentally friendly and does not cause secondary pollution.
  • Fig. 1 is the curve diagram of the influence of the dosage of the active ingredient Craneus chinensis in the algae inhibitor on the growth of Pseudo-Anabaena;
  • Fig. 2 is the influence curve figure of the active ingredient white crane lily in the algae inhibitor on the maximum photon yield of pseudoantaba;
  • Fig. 3 is a graph showing the IR change curve of the maximum photon yield IR of Pseudomonas anabaena at the dosage of 1.02g/L;
  • Fig. 4 is a histogram of the influence of the dosage of the active ingredient Craneus japonicus in the algae inhibitor on the inhibition rate of the maximum photon yield of Anabaena pseudoantha;
  • Fig. 5 is the influence curve diagram of the initial slope of the initial slope of the active ingredient Craneus chinensis in the algae inhibitor
  • Figure 6 is a graph showing the initial slope IR change curve of Pseudo Anabaena under the dosage of 12g/L;
  • Fig. 7 is a histogram of the influence of the dosage of the active ingredient Craneus chinensis in the algae inhibitor on the initial slope;
  • Fig. 8 is a curve diagram of the influence of the dosage of the active ingredient Craneus chinensis in the algae inhibitor on the electron transfer rate of Pseudomonas anabaena;
  • Fig. 9 is a graph showing the change curve of the inhibition rate of the electron transfer rate of pseudoantha anabaena under the dosage of 1.02g/L;
  • Fig. 10 is a curve diagram of the influence of the dosage of the active ingredient Craneus japonicus in the algae inhibitor on the half-saturated light intensity
  • Fig. 11 is a graph showing the effect of the dosage of active ingredient Craneus chinensis in the algae inhibitor on the spontaneous chlorophyll fluorescence of Pseudomonas anabaena.
  • the present invention provides an algae inhibitor and a preparation method thereof.
  • the present invention will be further described in detail below. It should be understood that the specific embodiments described here are only used to explain the present invention, not to limit the present invention.
  • the embodiment of the present invention provides a preparation method of an algae inhibitor, the method comprising:
  • the carrier refers to the object used to carry the medicine that can inhibit the growth of algae.
  • the carrier can be zeolite (artificial zeolite, natural zeolite), or carbon nanotube, organic framework material, etc.
  • the carrier used For an object with a porous surface use the pores on the carrier to immobilize the drug. By attaching the medicament to the carrier with a porous surface, the local medicament concentration can be avoided from being too high, affecting the ecology of the water body, and the efficacy of the drug can also be extended appropriately.
  • the plant medicinal material powder refers to a plant that is dried and ground into a fine powder, wherein the leaves or rhizomes of the plant are selected according to different plant types.
  • the type of the plant can be floating plants, such as eye lotus, water peanut, water water lotus, Manjianghong, duckweed, purple duckweed, duckweed, Daping, etc.; Flowers, calamus, reeds, lotus, amphibian polygonum, stone calamus, red Polygonum, reed bamboo, calla lily, water chestnuts, rushes, etc.; wet herbaceous plants, such as white crane taro, mushroom grass, anthurium; submerged water plants, such as Foxtail algae, water grass, water shield grass, black algae, water sword leaf, chrysanthemum algae, charophytes, licorice genus, eye genus, hornwort algae, eczema; terrestrial plants, such as barley straw, Litchi, Magnolia, Renm
  • the Daping can effectively inhibit various cyanobacteria, green algae, golden algae, and red algae; reed can effectively inhibit the water bloom Microcystis flos-aquae, Microcystis aeruginosa, and Chlorella pyrenoidosa
  • the white crane taro can effectively suppress Microcystis aeruginosa
  • the water sword leaf can effectively suppress Microcystis aeruginosa, Nannochloropsis oculata (Nannochloropsis oculata), Nitzchia palea (Nitzchia palea), Synechococcus elongatus ( Chlorella elongata), Scenedesmus obliquus (Scenedesmus obliquus), filamentous cyanobacteria (Filamentous cyanobacteria); described lychee leaves, Magnolia japonica, Renmianzi can effectively inhibit Microcystis aeruginosa; Haematococcus pluvialis,
  • the function of the filler is mainly for molding, that is, after the herbal medicine is made into powder, it is sprayed to form mixture particles.
  • the filler may be hydroxypropyl starch or hypromellose, or a mixture of hydroxypropyl starch and hypromellose.
  • the ratios of the filler to the powder of the plant medicine are 100:0.5, 100:1, 100:2, 100:3, 100:4, 100:5. The addition of too little filling agent will affect the formation of spray particles, and the addition of too much will affect the drug effect.
  • the mixed solution can be added to a high-pressure spray device, and the mixed solution can be formed into fine particles by high-pressure spray, and the particle size of the fine particles can be 50nm to 60nm, 60nm to 70nm, 70nm to 80nm, 80nm to 90nm , 90nm to 100nm.
  • the resulting fine particles are adsorbed in the micropores on the surface of the carrier, such as in the pores on the surface of zeolite.
  • Then baked at low temperature to finally get the inhibitor that can inhibit algae. It is easy to understand that the baking can be done in an oven or in an oven on an assembly line.
  • the baking temperature can be 30 degrees Celsius.
  • an embodiment of the present invention also provides an algae inhibitor, which is prepared by the above-mentioned preparation method.
  • the algae inhibitor further includes a base material for carrying the algae inhibitor, the base material is provided with several meshes, and the algae inhibitor is fixed in the meshes.
  • plastic or foam with mesh holes on the surface can be used, and then the algae inhibitor is embedded in the mesh, and the algae inhibitor can be conveniently dispensed by embedding the algae inhibitor in the mesh.
  • the substrate can also be set at a corresponding depth according to the distribution position of the algae in the water body. For example, cyanobacteria are mostly located 6 cm away from the water surface, so the substrate can be set at a position 5 cm away from the water surface. Thereby, the cyanobacteria can be better suppressed.
  • the mixed solution is prepared into tiny particles by spraying, and the tiny particles are adsorbed on the surface of the zeolite, and baked at a low temperature to obtain an algae inhibitor.
  • the maximum light quantum yield the maximum light quantum yield of algae is measured under saturated pulse conditions after full dark adaptation, reflecting the quantum yield when all PS II reaction centers are in the open state, and is an important indicator for studying the effect of photoinhibition on photosynthesis. Under photoinhibition conditions, a decrease in the maximum photon yield indicated that the algae were stressed.
  • a certain concentration of white crane taro can stress the photosynthesis of Pseudomonas anabaena, as shown in Figure 2, at the dosage of 1.02g/L, the inhibition rate of the maximum photon yield of Pseudo Anabaena rose to 70% within 2 days or so, followed by some fluctuations, but stabilized at around 75% after the 10d.
  • the inhibition rate of the experimental group with an dosage of 0.17-0.34g/L was higher than that of the other groups.
  • the IR of the high dosage group gradually increased until the 15th day , the inhibition rate of the experimental group whose dosage was above 0.25g/L basically reached a close level, exceeding 90%, and the inhibition rate increased with the increase of dosage.
  • the effective photon yield is measured during photosynthesis under light conditions, and represents the efficiency with which excitation energy is captured by the open reaction center, reflecting the degree of photochemical limitation of PS II due to the competition of thermal energy dissipation.
  • the IR of the effective photon yield of 0.08g/L dosage is basically stable at an average level of 30%.
  • the IR gradually increased, and the IR of the dosage of 1.02g/L stabilized at about 80% after the 9th day, and the effective light quantum of the experimental groups with the dosage of 0.34 and 0.68g/L after the 9th day
  • the changes were basically the same as those in the 1.02g/L experimental group, and there was a slight increase in the 0.25g/L experimental group in the later period.
  • the inhibition rate of each experimental group was quite different, and the 0.25g/L dosage group was the highest, reaching 85.0%, followed by 0.34 and 0.17g/L, then 0.68 and 0.08g/L, and finally 1.02 and 0.04 g/L.
  • the IR of the photon yield of Anabaena pseudoannae on the 7th day is the highest, and the decrease or increase of the dosage will lead to the decline of IR.
  • the initial slope of the fast light curve of algae photosynthesis reflects the efficiency of light energy utilization by Anabaena pseudoantha.
  • Figure 5 shows the change of the initial slope of Pseudomonas anabaena under different dosages of SKRE, which is similar to the change trend of the effective photon yield, and the initial slope is also subject to the same inhibition.
  • Figures 6 and 7 the initial slope IR produced by the dosage of 0.68 and 1.02g/L was the highest during the 1-3d of the culture, and the initial slope IR produced by the dosage of 3-4g/L was the highest on the 4-9d, followed by 0.17, 0.08, 0.68, 1.02 and 0.04g/L, after the 9th day, the initial slope IR increased more regularly with the increase of dosage.
  • the IR of the initial slope of the low dosage group (0.04, 0.08g/L) and the high dosage group (0.34-1.02g/L) gradually increases; High and then down.
  • the IR of the initial slope in the early stage (0-3d), the IR of the initial slope first increased and then decreased, and then the regeneration was high; in the middle period (4-9d), the IR of the initial slope first increased and then decreased; 18d), IR increases with the increase of dosage, but the difference is not significant under the dosage of 0.25-1.02g.
  • Figure 8 is the change curve of electron transfer rate (ETR) in photosynthesis of Anabaena pseudoannae at different dosages.
  • ETR electron transfer rate
  • Figure 10 is the change curve of half-saturated light intensity of Pseudo Anabaena under different dosages of SKRE, which reflects the tolerance of Pseudo Anabaena to strong light. It can be seen that compared with the control group, the addition of SKRE has a significant effect on The change of half-saturation light intensity had no significant effect, and high concentration dosage would increase the half-saturation light intensity of Pseudomonas anabaena in the later stage of cultivation.
  • the spontaneous chlorophyll fluorescence of algae reflects the situation of algal photosynthetic primordial response to allelopathic stress.
  • Figure 11 shows the changes in the spontaneous chlorophyll fluorescence signal of Pseudo Anabaena under different SKRE dosages. It can be seen that the chlorophyll fluorescence changes in the control group were relatively stable during the growth of Pseudo Anabaena; 0.04 and 0.08g/L The change trend of chlorophyll fluorescence in the dosage group was close to that of the control group.
  • the 0.17g/L dosage group was slightly lower than the control group, and the 0.25-1.02g/L groups were significantly lower than the control group; with the growth of culture time, the 0.17-1.02g/L dosage group
  • the chlorophyll fluorescence intensity of each experimental group increased significantly, the upward trend of the 0.17-0.34g/L dosage group was the most obvious, and the 0.68g/L experimental group lagged behind, but the chlorophyll fluorescence intensity was the highest after 12 days; 1.02g
  • the increase in /L dosage group was smaller than that of other groups, but it still surpassed the control group between 9-15 days, and then declined, and it was the lowest among all experimental groups on the 18th day.

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Abstract

An algae inhibitor and a preparation method therefor. The method comprises: providing a carrier; adding plant medicinal powder and a filler into a solvent to obtain a mixed solution; and spray-coating the mixed solution on the surface of the carrier and then drying, thus obtaining the algae inhibitor. The preparation method involves a simple process, the raw material ingredients are easy to obtain, and no toxic or harmful solvents are used. The prepared algae inhibitor can effectively inhibit algae propagation, is environmentally friendly, and does not cause secondary pollution.

Description

一种藻类抑制剂及其制备方法A kind of algae inhibitor and preparation method thereof 技术领域technical field
本发明涉及藻类控制技术领域,尤其涉及一种藻类抑制剂及其制备方法。The invention relates to the technical field of algae control, in particular to an algae inhibitor and a preparation method thereof.
背景技术Background technique
水体富营养化,使得水中的藻类大量的繁殖,造成了水厂原水处理的压力,给城市安全供水带来了风险。The eutrophication of the water body causes a large number of algae to multiply in the water, which causes the pressure of the raw water treatment of the water plant and brings risks to the safe water supply of the city.
目前对藻类的控制主要分为两类,第一类是以解决富营养化问题为根本性目的,以控制藻类生长所必须的营养盐为主要途径,以截污控源、整体修复为核心手段的系统性水库原位修复方案。这类技术以“正本清源”为核心,从长远考虑是最能够从根本上解决问题的方法,但其影响因素较多,历时较长,见效较慢,有些内源污染严重的水体可能需要经历十余年甚至数十年的努力才能完全杜绝藻类暴发的风险。第二类为原位短期控藻技术,即采用各种物理、化学、生物手段抑制藻类的生长或去除大量繁殖的藻类,保障水体安全。其中物理方法包括扬水曝气抑藻技术、紫外辐照抑藻技术等;化学方法以投加抑藻化学物质如硫酸铜为典型代表;生物方法则主要采取鱼类放养、微生物养殖及水生植物种植等方法。但是,物理方法与传统生物方法具有操作时间长,难度大,费用高的缺点;化学方法则有可能破坏生态平衡,造成二次污染。At present, the control of algae is mainly divided into two categories. The first category is to solve the problem of eutrophication as the fundamental purpose, to control the nutrients necessary for the growth of algae as the main way, and to intercept pollution, control sources, and overall restoration as the core means. Systematic reservoir in situ restoration program. This type of technology focuses on "rectifying the source" and is the most fundamental solution to the problem from a long-term perspective. However, it has many influencing factors, takes a long time, and is slow to take effect. Some water bodies with serious endogenous pollution may need to experience ten years of treatment. It will take years or even decades of hard work to completely eliminate the risk of algal blooms. The second category is in-situ short-term algae control technology, which uses various physical, chemical and biological means to inhibit the growth of algae or remove a large number of algae to ensure the safety of water bodies. Among them, the physical methods include water pumping and aeration anti-algae technology, ultraviolet radiation anti-algae technology, etc.; the chemical method is typically represented by adding algae-inhibiting chemicals such as copper sulfate; the biological method mainly adopts fish stocking, microbial breeding and aquatic plant planting and other methods. However, physical methods and traditional biological methods have the disadvantages of long operation time, difficulty and high cost; chemical methods may destroy the ecological balance and cause secondary pollution.
因此,如何低成本、对环境有好地进行控制藻类是亟需解决的问题。Therefore, how to control algae in a low-cost and environmentally friendly way is an urgent problem to be solved.
发明内容Contents of the invention
鉴于上述现有技术的不足,本发明的目的在于提供一种藻类抑制剂及其制备方法,用于解决现有控制藻类易造成二次污染、破坏生态的问题。In view of the above deficiencies in the prior art, the purpose of the present invention is to provide an algae inhibitor and a preparation method thereof, which are used to solve the problems that existing algae control is likely to cause secondary pollution and destroy ecology.
第一方面,本发明提供一种藻类抑制剂制备方法,其中,包括:In a first aspect, the present invention provides a method for preparing an algae inhibitor, which includes:
提供载体;provide a carrier;
将植物药材粉末、填充剂加入到溶剂中,得到混合溶液;Adding plant medicine powder and filler to the solvent to obtain a mixed solution;
将所述混合溶液喷涂在所述载体表面干燥后,得到所述藻类抑制剂。After the mixed solution is sprayed on the surface of the carrier and dried, the algae inhibitor is obtained.
可选地,所述的制备方法,其中,所述植物药材选自白鹤芋、芦苇、大萍、水剑叶、荔枝叶、白玉兰以及人面子中的一种或多种。Optionally, in the preparation method, wherein, the botanical medicinal material is selected from one or more of crane lily, reed, big weed, water sword leaf, litchi leaf, magnolia and renmianzi.
可选地,所述的制备方法,其中,所述载体选自沸石、碳纳米管和有机框架材料中的一种。Optionally, in the preparation method, the carrier is selected from one of zeolite, carbon nanotube and organic framework material.
可选地,所述的制备方法,其中,所述将所述混合溶液喷涂在所述载体表面干燥后,得到所述藻类抑制剂的步骤,具体包括:Optionally, in the preparation method, wherein, after the mixed solution is sprayed on the surface of the carrier and dried, the step of obtaining the algae inhibitor specifically includes:
将所述混合溶液雾化形成颗粒,并将所述颗粒附着在所述载体的表面,得到半成品;Atomizing the mixed solution to form particles, and attaching the particles to the surface of the carrier to obtain a semi-finished product;
将所述半成品放入干燥设备中干燥,得到所述藻类抑制剂。The semi-finished product is put into drying equipment to dry to obtain the algae inhibitor.
可选地,所述的制备方法,其中,所述溶剂为水。Optionally, in the preparation method, the solvent is water.
可选地,所述的制备方法,其中,所述填充剂为羟丙基淀粉和/或羟丙甲纤维素。Optionally, in the preparation method, the filler is hydroxypropyl starch and/or hypromellose.
可选地,所述的制备方法,其中,所述植物药材粉末与所述填充剂的质量比为100:0.1-5。Optionally, in the preparation method, the mass ratio of the plant drug powder to the filler is 100:0.1-5.
可选地,所述的制备方法,其中,所述颗粒的粒径为50-100nm。Optionally, in the preparation method, the particle size of the particles is 50-100 nm.
第二方面,一种藻类抑制剂,其中,采用如上所述的制备方法制备得到。In the second aspect, an algae inhibitor is prepared by the above-mentioned preparation method.
可选地,所述的藻类抑制剂,其中,所述藻类抑制剂还包括用于承载所述藻类抑制剂的基材,所述基材设有若干网孔,所述藻类抑制剂固定在所述网孔内。Optionally, the algae inhibitor, wherein, the algae inhibitor also includes a base material for carrying the algae inhibitor, the base material is provided with several mesh holes, and the algae inhibitor is fixed on the inside the mesh.
有益效果:本发明实施例提供了一种藻类抑制剂及制备方法,其中,所述制备方法工艺简单,各原料组分易得,不涉及有毒有害溶剂。所制备得到的藻类抑制剂,能够有效藻类的繁殖,且对环境友好,不会造成二次污染。Beneficial effects: the embodiment of the present invention provides an algae inhibitor and a preparation method, wherein the preparation method has a simple process, and each raw material component is easy to obtain, and does not involve toxic or harmful solvents. The prepared algae inhibitor can effectively reproduce algae, is environmentally friendly and does not cause secondary pollution.
附图说明Description of drawings
图1为藻类抑制剂中的有效成分白鹤芋投加量对伪鱼腥藻生长的影响曲线图;Fig. 1 is the curve diagram of the influence of the dosage of the active ingredient Craneus chinensis in the algae inhibitor on the growth of Pseudo-Anabaena;
图2为藻类抑制剂中的有效成分白鹤芋投加量对伪鱼腥藻最大光量子产量的影 响曲线图;Fig. 2 is the influence curve figure of the active ingredient white crane lily in the algae inhibitor on the maximum photon yield of pseudoantaba;
图3为1.02g/L投加量下伪鱼腥藻最大光量子产量IR变化曲线图;Fig. 3 is a graph showing the IR change curve of the maximum photon yield IR of Pseudomonas anabaena at the dosage of 1.02g/L;
图4为藻类抑制剂中的有效成分白鹤芋投加量对伪鱼腥藻最大光量子产量抑制率的影响柱状图;Fig. 4 is a histogram of the influence of the dosage of the active ingredient Craneus japonicus in the algae inhibitor on the inhibition rate of the maximum photon yield of Anabaena pseudoantha;
图5为藻类抑制剂中的有效成分白鹤芋投加量对伪鱼腥藻初始斜率的影响曲线图;Fig. 5 is the influence curve diagram of the initial slope of the initial slope of the active ingredient Craneus chinensis in the algae inhibitor;
图6为12g/L投加量下伪鱼腥藻初始斜率IR变化曲线图;Figure 6 is a graph showing the initial slope IR change curve of Pseudo Anabaena under the dosage of 12g/L;
图7为藻类抑制剂中的有效成分白鹤芋投加量对初始斜率的影响柱状图;Fig. 7 is a histogram of the influence of the dosage of the active ingredient Craneus chinensis in the algae inhibitor on the initial slope;
图8为藻类抑制剂中的有效成分白鹤芋投加量对伪鱼腥藻电子传递速率的影响曲线图;Fig. 8 is a curve diagram of the influence of the dosage of the active ingredient Craneus chinensis in the algae inhibitor on the electron transfer rate of Pseudomonas anabaena;
图9为1.02g/L投加量下伪鱼腥藻电子传递速率抑制率变化曲线图;Fig. 9 is a graph showing the change curve of the inhibition rate of the electron transfer rate of pseudoantha anabaena under the dosage of 1.02g/L;
图10为藻类抑制剂中的有效成分白鹤芋投加量对半饱和光强的影响曲线图;Fig. 10 is a curve diagram of the influence of the dosage of the active ingredient Craneus japonicus in the algae inhibitor on the half-saturated light intensity;
图11为为藻类抑制剂中的有效成分白鹤芋投加量对伪鱼腥藻自发叶绿素荧光的影响曲线图。Fig. 11 is a graph showing the effect of the dosage of active ingredient Craneus chinensis in the algae inhibitor on the spontaneous chlorophyll fluorescence of Pseudomonas anabaena.
具体实施方式Detailed ways
本发明提供一种藻类抑制剂及其制备方法,为使本发明的目的、技术方案及效果更加清楚、明确,以下对本发明进一步详细说明。应当理解,此处所描述的具体实施例仅用以解释本发明,并不用于限定本发明。The present invention provides an algae inhibitor and a preparation method thereof. In order to make the purpose, technical scheme and effect of the present invention clearer and clearer, the present invention will be further described in detail below. It should be understood that the specific embodiments described here are only used to explain the present invention, not to limit the present invention.
除非另有定义,本文所使用的所有的技术和科学术语与属于本发明的技术领域的技术人员通常理解的含义相同。本文中在本发明的说明书中所使用的术语只是为了描述具体的实施方式的目的,不是旨在于限制本发明。Unless otherwise defined, all technical and scientific terms used herein have the same meaning as commonly understood by one of ordinary skill in the technical field of the invention. The terminology used herein in the description of the present invention is only for the purpose of describing specific embodiments, and is not intended to limit the present invention.
本发明实施例提供一种藻类抑制剂的制备方法,所述方法包括:The embodiment of the present invention provides a preparation method of an algae inhibitor, the method comprising:
S10、提供载体。S10. Provide a carrier.
具体来说,所述载体是指用于承载能够抑制藻类生长药剂的物体,所述载体可以是沸石(人造沸石、天然沸石),也可以是碳纳米管、有机框架材料等,所用到的 载体为表面具有多孔的物体,利用载体上的孔,对药剂进行固定。通过将药剂附着在表面具有多孔的载体上,可以避免局部药剂浓度过高,影响水体生态,也可以适当延长药效。Specifically, the carrier refers to the object used to carry the medicine that can inhibit the growth of algae. The carrier can be zeolite (artificial zeolite, natural zeolite), or carbon nanotube, organic framework material, etc. The carrier used For an object with a porous surface, use the pores on the carrier to immobilize the drug. By attaching the medicament to the carrier with a porous surface, the local medicament concentration can be avoided from being too high, affecting the ecology of the water body, and the efficacy of the drug can also be extended appropriately.
S20、将植物药材粉末、填充剂加入到溶剂中,得到混合溶液,其中,所述溶剂为水。S20, adding the herbal medicine powder and the filler into the solvent to obtain a mixed solution, wherein the solvent is water.
具体来说,所述植物药材粉末指得是,将植物干燥后研磨成细粉得到,其中根据植物种类的不同,选用植物的叶子或者根茎。其中,所述植物的类型可以是浮水植物,如眼莲,水花生,水浮莲,满江红,浮萍,紫萍、萍蓬草、大萍等;挺水植物,如水芹菜、香蒲、再力花、菖蒲、芦苇、莲,两栖蓼、石菖蒲、红蓼、芦竹、马蹄莲、细果荸荠、灯心草等;湿生草本植物,如白鹤芋,香菇草,红掌;沉水植物,如狐尾藻、水蕴草,水盾草、黑藻、水剑叶、川蔓藻、轮藻、苦草属、眼子菜属、金鱼藻、大茨藻;陆生植物,如大麦秸秆、荔枝,白玉兰,人面子、灰柳树等。Specifically, the plant medicinal material powder refers to a plant that is dried and ground into a fine powder, wherein the leaves or rhizomes of the plant are selected according to different plant types. Wherein, the type of the plant can be floating plants, such as eye lotus, water peanut, water water lotus, Manjianghong, duckweed, purple duckweed, duckweed, Daping, etc.; Flowers, calamus, reeds, lotus, amphibian polygonum, stone calamus, red Polygonum, reed bamboo, calla lily, water chestnuts, rushes, etc.; wet herbaceous plants, such as white crane taro, mushroom grass, anthurium; submerged water plants, such as Foxtail algae, water grass, water shield grass, black algae, water sword leaf, chrysanthemum algae, charophytes, licorice genus, eye genus, hornwort algae, eczema; terrestrial plants, such as barley straw, Litchi, Magnolia, Renmianzi, Ash Willow, etc.
示例性地,所述大萍可以有效抑制多种蓝藻、绿藻、金藻、红藻;芦苇可以有效抑制水华微囊藻(Microcystis flos-aquae),铜绿微囊藻,蛋白核小球藻;所述白鹤芋可以有效抑制铜绿微囊藻;所述水剑叶可以有效抑制铜绿微囊藻,微拟球藻(Nannochloropsis oculata),谷皮菱形藻(Nitzchia palea),细长聚球藻(Chlorella elongata),斜生栅藻(Scenedesmus obliquus),丝状蓝藻(Filamentous cyanobacteria);所述荔枝叶、白玉兰、人面子可以有效抑制铜绿微囊藻;所述细果荸荠可以有效抑制雨生红球藻(Haematococcus pluvialis),水华鱼腥藻,链状鱼腥藻(Anabaena streptococcus),弱细颤藻(Oscillatoria tenuis)。Exemplarily, the Daping can effectively inhibit various cyanobacteria, green algae, golden algae, and red algae; reed can effectively inhibit the water bloom Microcystis flos-aquae, Microcystis aeruginosa, and Chlorella pyrenoidosa The white crane taro can effectively suppress Microcystis aeruginosa; The water sword leaf can effectively suppress Microcystis aeruginosa, Nannochloropsis oculata (Nannochloropsis oculata), Nitzchia palea (Nitzchia palea), Synechococcus elongatus ( Chlorella elongata), Scenedesmus obliquus (Scenedesmus obliquus), filamentous cyanobacteria (Filamentous cyanobacteria); described lychee leaves, Magnolia japonica, Renmianzi can effectively inhibit Microcystis aeruginosa; Haematococcus pluvialis, Anabaena blooms, Anabaena streptococcus, Oscillatoria tenuis.
在本实施例中,所述填充剂的作用主要是用于成型,即在将植物药材制成粉末后,喷雾形成混合物颗粒。其中,所述填充剂可以是羟丙基淀粉或羟丙甲纤维素,也可以是羟丙基淀粉和羟丙甲纤维素的混合物。所述填充剂与所述植物药材粉末的添加比例为100:0.5,100:1,100:2,100:3,100:4,100:5。填充剂的加入量过少影响喷雾颗粒的形成,加入量过多则会影响药效。In this embodiment, the function of the filler is mainly for molding, that is, after the herbal medicine is made into powder, it is sprayed to form mixture particles. Wherein, the filler may be hydroxypropyl starch or hypromellose, or a mixture of hydroxypropyl starch and hypromellose. The ratios of the filler to the powder of the plant medicine are 100:0.5, 100:1, 100:2, 100:3, 100:4, 100:5. The addition of too little filling agent will affect the formation of spray particles, and the addition of too much will affect the drug effect.
S30、将所述混合溶液喷涂在所述载体表面干燥后,得到所述藻类抑制剂。S30. After spraying the mixed solution on the surface of the carrier and drying it, the algae inhibitor is obtained.
具体来说,可以将所述混合溶液加入到高压喷雾设备中,通过高压喷雾使混合溶液形成细小的颗粒,细小颗粒的粒径可以是50nm至60nm,60nm至70nm,70nm至80nm,80nm至90nm,90nm至100nm。所形成的细小颗粒被吸附在载体表的微孔内,如吸附在沸石表面的孔内。然后经过低温烘烤,最终得到能够抑制藻类的抑制剂。容易理解的是,烘烤可以是在烤箱内烘烤,也可以是在流水线上的烤炉内烘烤。烘烤的温度可以是30摄氏度。Specifically, the mixed solution can be added to a high-pressure spray device, and the mixed solution can be formed into fine particles by high-pressure spray, and the particle size of the fine particles can be 50nm to 60nm, 60nm to 70nm, 70nm to 80nm, 80nm to 90nm , 90nm to 100nm. The resulting fine particles are adsorbed in the micropores on the surface of the carrier, such as in the pores on the surface of zeolite. Then baked at low temperature to finally get the inhibitor that can inhibit algae. It is easy to understand that the baking can be done in an oven or in an oven on an assembly line. The baking temperature can be 30 degrees Celsius.
基于相同的发明构思,本发明实施例还提供一种藻类抑制剂,该藻类抑制剂采用上述制备方法制备得到。Based on the same inventive concept, an embodiment of the present invention also provides an algae inhibitor, which is prepared by the above-mentioned preparation method.
在本实施例中,所述藻类抑制剂还包括用于承载所述藻类抑制剂的基材,所述基材设有若干网孔,所述藻类抑制剂固定在所述网孔内。示例性地,可以采用表面具有网孔的塑料或泡沫,然后将藻类抑制剂嵌入到网孔内,通过将藻类抑制剂嵌入到网孔内可以方便投放。同时,还可以根据藻类在水体中的分布位置,将基材设置在相应的深度。如蓝藻多位于距离水面6公分的位置,因此可以将基材设置在离水面5公分的位置。从而可以更好地对蓝藻进行抑制。In this embodiment, the algae inhibitor further includes a base material for carrying the algae inhibitor, the base material is provided with several meshes, and the algae inhibitor is fixed in the meshes. Exemplarily, plastic or foam with mesh holes on the surface can be used, and then the algae inhibitor is embedded in the mesh, and the algae inhibitor can be conveniently dispensed by embedding the algae inhibitor in the mesh. At the same time, the substrate can also be set at a corresponding depth according to the distribution position of the algae in the water body. For example, cyanobacteria are mostly located 6 cm away from the water surface, so the substrate can be set at a position 5 cm away from the water surface. Thereby, the cyanobacteria can be better suppressed.
下面通过具体的实施例,对本发明所提供的藻类抑制剂做进一步的解释说明。The algae inhibitor provided by the present invention will be further explained through specific examples below.
实施例1Example 1
取成熟白鹤芋(Spathiphyllum Kochii)植株的根部干燥,研磨成粉末,按照100:0.1的比例称取羟丙基淀粉,加入到水溶液中,得到混合溶液,将所得到的混合溶液加入到高压喷雾装置中,将所述混合溶液采用喷雾的方式制备成微小颗粒,微小颗粒被吸附在沸石表面,经过低温烘烤得到藻类抑制剂。Take the root of the mature Spathiphyllum Kochii plant and dry it, grind it into powder, weigh hydroxypropyl starch according to the ratio of 100:0.1, add it to the aqueous solution to obtain a mixed solution, and add the obtained mixed solution to a high-pressure spray device In the process, the mixed solution is prepared into tiny particles by spraying, and the tiny particles are adsorbed on the surface of the zeolite, and baked at a low temperature to obtain an algae inhibitor.
将所制备得到的藻类抑制剂加入到含有伪鱼腥藻的实验箱内,按照每升水体中加入0g,0.04g,0.08g,0.17g,0.25g,0.34g,0.68g,1.02g的白鹤芋粉末的加入量进行添加,然后绘制伪鱼腥藻的生长曲线,结果如图1所示。可以看出,当按照1.02g/L的投加量则能够明显抑制伪鱼腥藻生长。其中,对伪鱼腥藻的抑制作用机理解释如下:Add the prepared algae inhibitor into the experimental box containing Pseudo-Anabaena, and add 0g, 0.04g, 0.08g, 0.17g, 0.25g, 0.34g, 0.68g, 1.02g of Siberian Crane per liter of water The addition amount of taro powder was added, and then the growth curve of Pseudo-Anabaena was drawn, and the results are shown in Figure 1. It can be seen that when the dosage is 1.02g/L, the growth of Pseudo-Anabaena can be significantly inhibited. Among them, the mechanism of inhibition of pseudoantaba is explained as follows:
最大光量子产量,藻类的最大光量子产量由充分暗适应后饱和脉冲条件下测得, 反映当所有PS II反应中心均处于开放态时的量子产量,是研究光抑制对光合作用影响的重要指标。光抑制条件下,最大光量子产量的降低表明藻类受到胁迫。The maximum light quantum yield, the maximum light quantum yield of algae is measured under saturated pulse conditions after full dark adaptation, reflecting the quantum yield when all PS II reaction centers are in the open state, and is an important indicator for studying the effect of photoinhibition on photosynthesis. Under photoinhibition conditions, a decrease in the maximum photon yield indicated that the algae were stressed.
一定浓度的白鹤芋能够对伪鱼腥藻的光合作用产生胁迫,如图2所示,如1.02g/L投加量下,伪鱼腥藻最大光量子产量的抑制率在2d内上升到70%左右,随后出现一定的波动,但在第10d之后稳定在75%左右。结合图5-3,第7d,投加量为0.17-0.34g/L的实验组抑制率相对其它组更高,随着培养时间的增长,高投加量组的IR逐渐上升,到第15d,投加量为0.25g/L以上的实验组抑制率基本达到了接近的水平,超过了90%,且抑制率随投加量的增大而升高。A certain concentration of white crane taro can stress the photosynthesis of Pseudomonas anabaena, as shown in Figure 2, at the dosage of 1.02g/L, the inhibition rate of the maximum photon yield of Pseudo Anabaena rose to 70% within 2 days or so, followed by some fluctuations, but stabilized at around 75% after the 10d. Combined with Figure 5-3, on the 7th day, the inhibition rate of the experimental group with an dosage of 0.17-0.34g/L was higher than that of the other groups. With the growth of the culture time, the IR of the high dosage group gradually increased until the 15th day , the inhibition rate of the experimental group whose dosage was above 0.25g/L basically reached a close level, exceeding 90%, and the inhibition rate increased with the increase of dosage.
有效光量子产量Effective photon yield
有效光量子产量在光照条件下光合作用进行时测得,代表激发能被开放的反应中心捕获的效率,反映了由于热能耗散的竞争作用而导致PS II的光化学受限制的程度。The effective photon yield is measured during photosynthesis under light conditions, and represents the efficiency with which excitation energy is captured by the open reaction center, reflecting the degree of photochemical limitation of PS II due to the competition of thermal energy dissipation.
如图3至图4所示,0.08g/L的投加量有效光量子产量的IR基本稳定在平均30%的水平。随着投加量的增大,IR逐渐上升,1.02g/L投加量的IR在第9d后稳定在80%左右,且0.34和0.68g/L投加量实验组在第9d后有效光量子变化情况基本与1.02g/L实验组没有差异,0.25g/L实验组在后期略有升高。第7d时,各实验组抑制率差异较大,0.25g/L投加量组最高,达到了85.0%,其次是0.34和0.17g/L,而后0.68和0.08g/L,最后是1.02和0.04g/L。结合最大光量子产量的变化情况,可以推测,0.25-0.34g/L投加量下,第7d实现的伪鱼腥藻光量子产量IR最高,投加量下降或上升都会导致IR的下降。但延长培养时间,到第9-10d后,高浓度投加量实验组IR会继续上升,但0.25-0.34g/L实验组IR会出现一定程度的下降,推测这主要是因为高浓度投加量化感物质在培养体系中存留的时间更长,实现的抑制效果也更为长效的原因。As shown in Figures 3 to 4, the IR of the effective photon yield of 0.08g/L dosage is basically stable at an average level of 30%. With the increase of the dosage, the IR gradually increased, and the IR of the dosage of 1.02g/L stabilized at about 80% after the 9th day, and the effective light quantum of the experimental groups with the dosage of 0.34 and 0.68g/L after the 9th day The changes were basically the same as those in the 1.02g/L experimental group, and there was a slight increase in the 0.25g/L experimental group in the later period. On the 7th day, the inhibition rate of each experimental group was quite different, and the 0.25g/L dosage group was the highest, reaching 85.0%, followed by 0.34 and 0.17g/L, then 0.68 and 0.08g/L, and finally 1.02 and 0.04 g/L. Combined with the change of the maximum photon yield, it can be inferred that at the dosage of 0.25-0.34g/L, the IR of the photon yield of Anabaena pseudoannae on the 7th day is the highest, and the decrease or increase of the dosage will lead to the decline of IR. However, after prolonging the culture time, after the 9th-10th day, the IR of the high-concentration dosage experimental group will continue to rise, but the IR of the 0.25-0.34g/L experimental group will decline to a certain extent. It is speculated that this is mainly due to the high-concentration dosage Quantitative substances remain in the culture system for a longer period of time, and the reason for the longer-lasting inhibitory effect is also achieved.
快速光曲线初始斜率Fast light curve initial slope
藻类光合作用快速光曲线的初始斜率反映的是伪鱼腥藻对光能的利用效率。图5为不同SKRE投加量下伪鱼腥藻初始斜率的变化情况,与有效光量子产量的变化趋 势类似,初始斜率也受到了同样的抑制作用。由图6和7可知在培养的1-3d,0.68和1.02g/L投加量产生的初始斜率IR最高,4-9d,3-4g/L投加量产生的初始斜率IR最高,其次是0.17、0.08、0.68、1.02和0.04g/L,至第9d后,初始斜率IR较为规律地随投加量的增大而增加。The initial slope of the fast light curve of algae photosynthesis reflects the efficiency of light energy utilization by Anabaena pseudoantha. Figure 5 shows the change of the initial slope of Pseudomonas anabaena under different dosages of SKRE, which is similar to the change trend of the effective photon yield, and the initial slope is also subject to the same inhibition. It can be seen from Figures 6 and 7 that the initial slope IR produced by the dosage of 0.68 and 1.02g/L was the highest during the 1-3d of the culture, and the initial slope IR produced by the dosage of 3-4g/L was the highest on the 4-9d, followed by 0.17, 0.08, 0.68, 1.02 and 0.04g/L, after the 9th day, the initial slope IR increased more regularly with the increase of dosage.
总体上,随培养时间延长,低投加量组(0.04、0.08g/L)和高投加量组(0.34-1.02g/L)初始斜率的IR逐渐升高;中间投加量组先升高后下降。随投加量增大,初期(0-3d),初始斜率的IR先升高后下降,而后再生高;中期(4-9d),初始斜率的IR先升高后下降;到后期(10-18d),IR随投加量增大而升高,但0.25-1.02g投加量下的差别不大。In general, as the culture time prolongs, the IR of the initial slope of the low dosage group (0.04, 0.08g/L) and the high dosage group (0.34-1.02g/L) gradually increases; High and then down. With the increase of dosage, in the early stage (0-3d), the IR of the initial slope first increased and then decreased, and then the regeneration was high; in the middle period (4-9d), the IR of the initial slope first increased and then decreased; 18d), IR increases with the increase of dosage, but the difference is not significant under the dosage of 0.25-1.02g.
电子传递速率electron transfer rate
图8为不同投加量下伪鱼腥藻光合作用电子传递速率(ETR)的变化曲线,ETR的抑制效果并不稳定,低投加量(0.04g/L和0.08g/L)在前期还出现了促进效果,且随投加量的增大,前期和中期抑制率没有明显的变化规律,后期0.25-1.02g/L投加量之间的抑制率差异不明显。Figure 8 is the change curve of electron transfer rate (ETR) in photosynthesis of Anabaena pseudoannae at different dosages. The inhibitory effect of ETR is not stable. There was a promotion effect, and with the increase of dosage, there was no obvious change rule in the early and mid-term inhibition rate, and there was no obvious difference in the inhibition rate between the dosage of 0.25-1.02g/L in the later period.
1.02g/L投加量对电子传递速率的影响随时间延长不断波动,如图9所示,最大抑制率可达到80%以上,但只有少数时间点达到。因此,化感抑制对伪鱼腥藻电子传递速率的抑制弱于对其光量子产量和光能利用效率的抑制。The effect of the dosage of 1.02g/L on the electron transfer rate fluctuates with time, as shown in Figure 9, the maximum inhibition rate can reach more than 80%, but only at a few time points. Therefore, the inhibition of allelopathic inhibition on the electron transport rate of pseudoantha is weaker than that on its light quantum yield and light energy utilization efficiency.
半饱和光强Half Saturation Light Intensity
图10为不同SKRE投加量下伪鱼腥藻半饱和光强的变化曲线,反应的是伪鱼腥藻对强光的耐受能力,可以看出与对照组相比,SKRE的投加对半饱和光强的变化没有显著的影响规律,高浓度投加量在培养后期会提高伪鱼腥藻的半饱和光强。Figure 10 is the change curve of half-saturated light intensity of Pseudo Anabaena under different dosages of SKRE, which reflects the tolerance of Pseudo Anabaena to strong light. It can be seen that compared with the control group, the addition of SKRE has a significant effect on The change of half-saturation light intensity had no significant effect, and high concentration dosage would increase the half-saturation light intensity of Pseudomonas anabaena in the later stage of cultivation.
藻类自发叶绿素荧光Algal Spontaneous Chlorophyll Fluorescence
藻类自发叶绿素荧光,反应藻类光合作用原初反应受化感胁迫的情况。图11为伪鱼腥藻在不同SKRE投加量下自发叶绿素荧光信号的变化情况,可以看出,对照组在伪鱼腥藻生长过程中,叶绿素荧光变化较为平稳;0.04和0.08g/L的投加量组叶绿素荧光的变化趋势接近于对照组。随着投加量增大,初期,0.17g/L投加量组略低于对照组,0.25-1.02g/L各组明显低于对照组;随培养时间增长,0.17-1.02g/L投 加量的各实验组叶绿素荧光强度均明显上升,0.17-0.34g/L投加量组的上升趋势最为明显,0.68g/L实验组有所滞后,但在12d后叶绿素荧光强度最高;1.02g/L投加量组上升幅度相对其他组较小,但仍在9-15d之间超过了对照组,随后下降,到第18d为各实验组中最低。The spontaneous chlorophyll fluorescence of algae reflects the situation of algal photosynthetic primordial response to allelopathic stress. Figure 11 shows the changes in the spontaneous chlorophyll fluorescence signal of Pseudo Anabaena under different SKRE dosages. It can be seen that the chlorophyll fluorescence changes in the control group were relatively stable during the growth of Pseudo Anabaena; 0.04 and 0.08g/L The change trend of chlorophyll fluorescence in the dosage group was close to that of the control group. With the increase of dosage, at the initial stage, the 0.17g/L dosage group was slightly lower than the control group, and the 0.25-1.02g/L groups were significantly lower than the control group; with the growth of culture time, the 0.17-1.02g/L dosage group The chlorophyll fluorescence intensity of each experimental group increased significantly, the upward trend of the 0.17-0.34g/L dosage group was the most obvious, and the 0.68g/L experimental group lagged behind, but the chlorophyll fluorescence intensity was the highest after 12 days; 1.02g The increase in /L dosage group was smaller than that of other groups, but it still surpassed the control group between 9-15 days, and then declined, and it was the lowest among all experimental groups on the 18th day.
综上可知白鹤芋对藻类的影响首先作用于藻类的光合系统,影响光合系统的光量子产量和光反应效率,但同时藻类具备应对环境胁迫的反馈机制,表现为低投加量下藻类生物量未能被抑制和自发叶绿素荧光在培养一段时间后又出现上升趋势超过对照组。进一步增大投加量才会对光合色素造成破坏,进而达到降低藻类生物量的效果。To sum up, it can be seen that the impact of Helicodium chinensis on algae first acts on the photosynthetic system of algae, affecting the photon yield and photoreaction efficiency of the photosynthetic system. Inhibited and spontaneous chlorophyll fluorescence showed an upward trend over the control group after a period of culture. Further increasing the dosage will cause damage to photosynthetic pigments, thereby achieving the effect of reducing algae biomass.
实施例2Example 2
取成熟白鹤芋(Spathiphyllum Kochii)植株的根部干燥(500g),荔枝叶去除表面的污染物干燥(200g)、芦苇的根部干燥(300g)研磨成粉末,按照100:2的比例称取羟丙基淀粉,加入到水溶液中,得到混合溶液,将所得到的混合溶液加入到高压喷雾装置中,将所述混合溶液采用喷雾的方式制备成微小颗粒,微小颗粒被吸附在沸石表面,经过低温烘烤得到藻类抑制剂。Take the dry root (500g) of the mature Spathiphyllum Kochii plant, remove the pollutants on the surface of litchi leaves (200g), dry the root of reed (300g) and grind them into powder, and weigh the hydroxypropyl group according to the ratio of 100:2. Starch is added to the aqueous solution to obtain a mixed solution, and the obtained mixed solution is added to a high-pressure spray device, and the mixed solution is prepared into tiny particles by spraying, and the tiny particles are adsorbed on the surface of the zeolite, and baked at a low temperature Get algae inhibitors.
将所得到的藻类抑制剂嵌入到塑料板上的网孔中,投放至含有伪鱼腥藻的水库中,间隔一定时间进行取样分析,经对比发现,该藻类抑制剂对蓝藻的生长有很好的抑制作用。Embed the obtained algae inhibitor into the mesh on the plastic plate, put it into the reservoir containing Pseudo-Anabaena, and carry out sampling analysis at regular intervals. After comparison, it is found that the algae inhibitor has a good effect on the growth of cyanobacteria. inhibitory effect.
应当理解的是,本发明的应用不限于上述的举例,对本领域普通技术人员来说,可以根据上述说明加以改进或变换,所有这些改进和变换都应属于本发明所附权利要求的保护范围。It should be understood that the application of the present invention is not limited to the above examples, and those skilled in the art can make improvements or transformations according to the above descriptions, and all these improvements and transformations should belong to the protection scope of the appended claims of the present invention.

Claims (10)

  1. 一种藻类抑制剂的制备方法,其特征在于,包括:A preparation method for algae inhibitor, characterized in that, comprising:
    提供载体;provide a carrier;
    将植物药材粉末、填充剂加入到溶剂中,得到混合溶液;Adding herbal medicine powder and filler to the solvent to obtain a mixed solution;
    将所述混合溶液喷涂在所述载体表面干燥后,得到所述藻类抑制剂。After the mixed solution is sprayed on the surface of the carrier and dried, the algae inhibitor is obtained.
  2. 根据权利要求1所述的制备方法,其特征在于,所述植物药材选自白鹤芋、芦苇、大萍、水剑叶、荔枝叶、白玉兰以及人面子中的一种或多种。The preparation method according to claim 1, characterized in that, the plant medicinal material is selected from one or more of crane taro, reed, Daping, water sword leaf, litchi leaf, magnolia and renmianzi.
  3. 根据权利要求1所述的制备方法,其特征在于,所述载体选自沸石、碳纳米管和有机框架材料中的一种。The preparation method according to claim 1, wherein the carrier is selected from one of zeolites, carbon nanotubes and organic framework materials.
  4. 根据权利要求3所述的制备方法,其特征在于,所述将所述混合溶液喷涂在所述载体表面干燥后,得到所述藻类抑制剂的步骤,具体包括:The preparation method according to claim 3, wherein the step of obtaining the algae inhibitor after spraying the mixed solution on the surface of the carrier and drying it specifically comprises:
    将所述混合溶液雾化形成颗粒,并将所述颗粒附着在所述载体的表面,得到半成品;Atomizing the mixed solution to form particles, and attaching the particles to the surface of the carrier to obtain a semi-finished product;
    将所述半成品放入干燥设备中干燥,得到所述藻类抑制剂。The semi-finished product is put into drying equipment to dry to obtain the algae inhibitor.
  5. 根据权利要求1所述的制备方法,其特征在于,所述溶剂为水。The preparation method according to claim 1, wherein the solvent is water.
  6. 根据权利要求1所述的制备方法,其特征在于,所述填充剂为羟丙基淀粉和/或羟丙甲纤维素。The preparation method according to claim 1, wherein the filler is hydroxypropyl starch and/or hypromellose.
  7. 根据权利要求1所述的制备方法,其特征在于,所述植物药材粉末与所述填充剂的质量比为100:0.1-5。The preparation method according to claim 1, characterized in that, the mass ratio of the plant medicinal material powder to the filler is 100:0.1-5.
  8. 根据权利要求4所述的制备方法,其特征在于,所述颗粒的粒径为50-100nm。The preparation method according to claim 4, characterized in that the particle size of the particles is 50-100nm.
  9. 一种藻类抑制剂,其特征在于,采用权利要求1-8任一所述的制备方法制备得到。An algae inhibitor, characterized in that it is prepared by the preparation method described in any one of claims 1-8.
  10. 根据权利要求9所述的藻类抑制剂,其特征在于,所述藻类抑制剂还包括用于承载所述藻类抑制剂的基材,所述基材设有若干网孔,所述藻类抑制剂固定在所述网孔内。The algae inhibitor according to claim 9, characterized in that, the algae inhibitor also includes a base material for carrying the algae inhibitor, the base material is provided with several mesh holes, and the algae inhibitor is fixed within the mesh.
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