CN113287628A - Red tide algae removing agent based on tannin activated persulfate and application thereof - Google Patents

Red tide algae removing agent based on tannin activated persulfate and application thereof Download PDF

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CN113287628A
CN113287628A CN202110614535.8A CN202110614535A CN113287628A CN 113287628 A CN113287628 A CN 113287628A CN 202110614535 A CN202110614535 A CN 202110614535A CN 113287628 A CN113287628 A CN 113287628A
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red tide
algae
algaecide
persulfate
tannin
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苏荣欣
车明达
黄仁亮
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Tianjin University
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    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
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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
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    • A01N25/02Biocides, 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 liquids as carriers, diluents or solvents
    • 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
    • A01N43/02Biocides, pest repellants or attractants, or plant growth regulators containing heterocyclic compounds having rings with one or more oxygen or sulfur atoms as the only ring hetero atoms
    • A01N43/04Biocides, pest repellants or attractants, or plant growth regulators containing heterocyclic compounds having rings with one or more oxygen or sulfur atoms as the only ring hetero atoms with one hetero atom
    • A01N43/14Biocides, pest repellants or attractants, or plant growth regulators containing heterocyclic compounds having rings with one or more oxygen or sulfur atoms as the only ring hetero atoms with one hetero atom six-membered rings
    • A01N43/16Biocides, pest repellants or attractants, or plant growth regulators containing heterocyclic compounds having rings with one or more oxygen or sulfur atoms as the only ring hetero atoms with one hetero atom six-membered rings with oxygen as the ring hetero atom
    • 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
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5236Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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    • CCHEMISTRY; METALLURGY
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    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/20Prevention of biofouling
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/02Specific form of oxidant
    • C02F2305/023Reactive oxygen species, singlet oxygen, OH radical

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Abstract

The invention discloses a red tide algae algaecide based on tannin activated persulfate and application thereof. The red tide algae removal agent is formed by mixing 11-69 wt% of tannin, 23-80 wt% of persulfate, 2-5 wt% of dispersing agent and 3-5 wt% of auxiliary materials, and when the red tide algae removal agent is used, the red tide algae removal agent is mixed with seawater or fresh water to prepare a solution, the solution is sprayed on the surface of a red tide water body, and the red tide is effectively removed after natural sedimentation for 3-24 hours. The efficient, green and sustainable red tide algae removal agent effectively improves the potential influence of the existing heterogeneous phase algae removal agent on the environment, inhibits the activity of red tide algae by utilizing the homogeneous phase advanced oxidation process of activating persulfate by using tannic acid, enables the algae cells to settle, and obviously improves the efficiency of treating a red tide water body through an inactivation-apoptosis-settlement algae removal mechanism.

Description

Red tide algae removing agent based on tannin activated persulfate and application thereof
Technical Field
The invention relates to a method for treating seawater red tide pollution, in particular to a red tide algae algaecide based on tannin activated persulfate and application thereof.
Background
Red tide is an ecological abnormal phenomenon that some microalgae, protozoa or bacteria are explosively proliferated or gathered to a certain level under certain environmental conditions to cause water body discoloration or harm to other organisms in the ocean. In the marine system, microalgae play an important role not only in providing food to other aquatic organisms at the bottom of the food chain, but also in the global carbon cycle, and they absorb carbon dioxide from the atmosphere through photosynthesis, thereby performing a carbon sequestration effect. However, under certain conditions, certain species proliferate explosively and accumulate or produce toxins to form harmful algal blooms, which are generally called red tides because they cause the water to appear red. In recent years, the aforementioned Harmful ecological phenomena are collectively called Harmful Algal Bloms (HAB) by the international scientific community.
In recent years, as the level of carbon dioxide rises, the global climate becomes warm, and the eutrophication degree of water body becomes more and more serious, the occurrence scale and frequency of harmful algal blooms generally tend to increase year by year. The frequently-occurring harmful algal blooms not only can cause massive death of marine organisms to reduce the yield of marine fishery on a large scale, but also can indirectly influence human health through the enrichment of red tide toxins, and can break the dynamic balance of marine ecological environment. Since the 70 s of the 20 th century, more than 3000 red tide disasters occurred in coastal waters in China, and the economic loss caused by each year is as high as billions of RMB. Therefore, the prevention and control of red tide disasters are necessary for the development of marine ecology and human health in China. Because of the great harm of red tide to the economy and human health, the treatment measures of red tide have been the focus of attention and research. The method can be roughly divided into two research directions, wherein one research direction is to reduce the occurrence frequency of the red tide by early detection and early warning before the occurrence of the red tide disaster; the other is that after a disaster occurs, the influence area of the red tide is reduced by treating red tide organisms, so that the harm of the red tide is weakened, and the treatment measures can be roughly divided into a biological method, a physical method and a chemical method. The physical method is mainly to remove algae by using mechanical equipment and applying air flotation, ultrasonic waves, stirring, adsorption and the like; biological methods use zooplankton, macrophytes, microorganisms, and filter-feeding shellfish to inhibit or eliminate microalgae; the chemical method mainly comprises a medicament killing method and a flocculation method. The flocculation sedimentation method has prominent research results, and particularly, a great deal of research is carried out at home and abroad on the flocculation aspect of the modified clay. However, the method has certain defects, and the red tide removing biological capacities of different types of clay minerals and even the same type of clay minerals are greatly different; different application modes also significantly affect the ability of clay to remove red tide organisms; the key is that the cost of spreading a large amount of clay is high, the effect is slow, and secondary rebound is possible to cause pollution.
Tannin is also called tannin, is a polyphenol derivative, is widely present in plants, is safe and nontoxic, and has strong biological and pharmacological activities. The red tide algae is a natural product with important development and utilization values by obviously inhibiting the growth of the red tide algae through the degradation effect on the red tide algae, so the red tide algae is applied to the treatment of the red tide. Persulfate is a common oxidant and has a certain killing effect on algae cells, and because persulfate has the advantages of low toxicity, low price, easiness in operation and the like, the persulfate activated by the tannic acid is used as the red tide algaecide, so that the potential application value for removing red tide algae exists, but no relevant research report exists.
Disclosure of Invention
The invention aims to provide a red tide algae removal agent based on tannin activated persulfate and an application thereof, which can effectively solve the problems of large spraying amount, large influence on environment, slow effect, easy rebound and easy secondary pollution of the existing heterogeneous red tide algae removal agent.
Therefore, the invention adopts the following technical scheme:
the red tide algae algaecide based on the tannin activated persulfate is characterized by being prepared by mixing the following components in percentage by mass:
Figure BDA0003097534580000021
wherein:
the dispersing agent is one or more of carrageenan, gelatin, alginic acid, hydroxypropyl cellulose, sodium dodecyl sulfate, polyethylene glycol, polypropylene glycol and alkyl monoglycoside;
the auxiliary materials are one or more of sodium chloride, sodium nitrate, sodium sulfate, sodium gluconate, potassium chloride, potassium nitrate and potassium sulfate.
Wherein the persulfate is sodium persulfate, potassium hydrogen persulfate or ammonium persulfate; the tannic acid is industrial grade, and the content is 85-99%.
The red tide algae algaecide is prepared into a solution and sprayed on the surface of a red tide water body, so that the concentration of the red tide algae algaecide in the red tide water body is 0.001-0.5g/L, and the red tide algae is effectively removed by natural sedimentation for 3-24 hours. Wherein the red tide algae is phaeocystis globosa, red tide yizhuan algae, Skeletonema costatum or prorocentrum donghaiense.
Compared with the prior art, the invention has the following beneficial effects:
1. the invention adopts an advanced oxidation process of activating persulfate by tannic acid, and utilizes sulfate radicals and hydroxyl radicals generated in the advanced oxidation process to inhibit the activity of red tide algae so as to inactivate and settle. Compared with the existing heterogeneous flocculation algaecide with more applications, the algaecide disclosed by the invention solves the problem that the existing algaecide only flocculates red tide algae and has small influence on activity. The risk of secondary rebound of red tide is reduced.
2. Compared with the existing algaecide, the algaecide provided by the invention inhibits the activity of red tide algae by utilizing a high-grade oxidation process, so that the effective time is shorter than that of a heterogeneous flocculation process, the effective time of the existing algaecide is more than 24 hours, and the removal efficiency of the algaecide can reach more than 80% within 10 hours
3. Compared with the existing algaecide, the algaecide of the invention has obvious advantages of 0.2g L-1The algaecide can achieve the removal effect of more than 80 percentThe dosage of the prior heterogeneous algaecide needs 0.5g L-1The above. And because the invention is a homogeneous system, the problem that the seawater environment is turbid and the aquatic environment is influenced due to large input amount of the heterogeneous system is solved.
4. In the algaecide formula content adopted by the invention, the tannin, the persulfate, the dispersing agent and the auxiliary materials have small influence on the aquatic environment, and the tannin is natural organic matters in the nature, so that the biological compatibility of the algaecide is good.
5. The red tide algae removal agent disclosed by the invention has high efficiency, greenness and sustainability, and effectively improves the potential environmental impact of the existing heterogeneous algae removal agent; the homogeneous phase advanced oxidation process of activating persulfate by using tannic acid inhibits the activity of red tide algae so as to settle algae cells; the efficiency of treating the red tide water body is obviously improved through an algae removal mechanism of inactivation, apoptosis and sedimentation.
Drawings
FIG. 1 is a graph showing the efficiency of red tide algaecide with four different formulations for removing phaeocystis globosa according to the embodiment of the present invention, wherein the initial concentration of phaeocystis globosa has a biological density of 109cells L-1The concentration of the algaecide for red tide algae in the algae liquid is 0.2g L-1
FIG. 2 is a graph showing the efficiency of red tide algaecide with different concentrations in removing red tide bent algae according to the embodiment of the present invention, wherein the initial concentration of bent algae reaches a biological density of 108cells L-1
FIG. 3 is a graph showing the efficiency of red tide algaecide with different concentrations in removing prorocentrum donghaiense with the initial concentration of the prorocentrum donghaiense with biological density of 107cells L-1
Detailed Description
The red tide algae algaecide is prepared by uniformly mixing tannic acid, persulfate, a certain amount of dispersant and auxiliary materials. In the red tide algae algaecide, the dosage of the tannin, the persulfate and the dispersant can be adjusted according to the characteristics of the water body to be applied, such as the change of salinity and biomass. Usually, the mass percent of the tannin is between 11 and 69 percent, and the mass percent of the persulfate is between 23 and 80 percentPercent, the mass percentage content of the dispersant is between 2 and 5 percent, which is the best. When in use, the red tide algae algaecide based on the tannin activated persulfate is mixed with seawater (or fresh water) to prepare a uniform solution with a certain concentration (0.001-0.5g L)-1) The red tide is sprayed on the surface of a red tide water body, and after a certain period of natural sedimentation, the red tide can be effectively removed.
The invention is further illustrated by the following examples.
Example 1
Experiment 1: uniformly mixing tannin with the mass content of 11%, 80% of sodium persulfate, 4% of polyethylene glycol and 5% of sodium chloride in 1L of seawater to obtain an algaecide solution 1;
control 2: uniformly mixing tannin with the mass content of 11%, polyethylene glycol with the mass content of 4% and sodium chloride with the mass content of 5% in 1L of seawater to obtain an algaecide solution 2;
control 3: uniformly mixing sodium persulfate with the mass content of 80%, polyethylene glycol with the mass content of 4% and sodium chloride with the mass content of 5% in 1L of seawater to obtain an algaecide solution 3;
blank 4: polyethylene glycol with the mass content of 4% and sodium chloride with the mass content of 5% are uniformly mixed in 1L of seawater to be used as algaecide solution 4.
4 parts of red tide water body with the phaeocystis globosa growing thereon, 9L of each water body are respectively sprayed with the 4 algaecide solutions, and the initial concentration biological density of the phaeocystis globosa in the algae solution reaches 109cells L-1The concentration of each algaecide in the algae liquid is 0.2g L-1. And (5) observing the density change of the spherical phaeocystis fuscus in the algae liquid after standing for 24 hours.
The algae removal efficiency of different algaecides is shown in figure 1, and the result shows that only when tannin and sodium persulfate are simultaneously contained in the algaecide, the biological density can be effectively removed to 109cells L-1The removal rate of the spherical phaeocystis fuscus can reach more than 95 percent.
Example 2
Uniformly mixing tannic acid with the mass content of 28%, potassium hydrogen peroxymonosulfate with the mass content of 67%, carrageenan with the mass content of 2% and potassium sulfate with the mass content of 3% in 1L of seawater to obtain the red tide algae algaecide solution. Taking the curve with red tide6 parts of red tide algae water body, 9L of each red tide algae water body are respectively sprayed with the red tide algae algaecide solution, and the initial concentration biological density of the red tide heterocurvula in the algae solution reaches 108cells L-1The concentrations of the algaecide for red tide algae in the algae liquid are respectively 0 and 0.08g L-1、0.16g L-1、0.24g L-1、0.32g L-1、0.40g L-1And standing for 8h, and observing the density change of the red tide heterocurvula in the algae liquid. The algae removal efficiency of the algaecide at different concentrations is shown in figure 2.
The result shows that when the concentration of the algaecide in the red tide is 0.24g L-1And above, for biological densities up to 108cells L-1The removal rate of the red tide heterocurvula can reach more than 90 percent.
Example 3
Uniformly mixing 49 mass percent of tannic acid, 46 mass percent of ammonium persulfate, 2 mass percent of hydroxypropyl cellulose and 3 mass percent of sodium gluconate in 1L of seawater to obtain the red tide algae algaecide solution. Spraying red tide water body 6 parts with prorocentrum donghaiense (9L) respectively with the above red tide algae algaecide solution, wherein the initial concentration of prorocentrum donghaiense in the algae solution has biological density of 107cells L-1The concentrations of the algaecide for red tide algae in the algae liquid are respectively 0 and 0.05g L-1、0.1g L-1、0.15g L-1、0.2g L-1、0.25g L-1And standing for 10h, and observing the density change of the prorocentrum donghaiense in the algae liquid.
The algae removal efficiency of the different algaecides is shown in FIG. 3, and the results show that when the concentration of the algaecide in the red tide is 0.15g L-1And above, for biological densities up to 107cells L-1The removal rate of prorocentrum donghaiense can reach more than 85%.
Example 4
Uniformly mixing tannin with the mass content of 69%, 23% of sodium persulfate, 4% of polypropylene glycol and 4% of sodium nitrate in 1L of seawater to obtain the red tide algae algaecide solution. Spraying red tide algae algaecide solution to 9L of red tide water body with Skeletonema costatum, wherein the initial concentration of Skeletonema costatum in algae solution has biological density of 1010cells L-1Removing red tide algae in algae liquidThe concentration of algaecide is 0.001g L-1After standing for 3h, more than 80% of skeletonema costatum can be removed.
The above description is only for the preferred embodiment of the present invention, but the scope of the present invention is not limited thereto, and any changes or substitutions that can be easily conceived by those skilled in the art within the technical scope of the present invention disclosed herein should be covered within the scope of the present invention. Therefore, the protection scope of the present invention shall be subject to the protection scope of the claims.

Claims (5)

1. The red tide algae algaecide based on the tannin activated persulfate is characterized by being prepared by mixing the following components in percentage by mass:
Figure FDA0003097534570000011
wherein:
the dispersing agent is one or more of carrageenan, gelatin, alginic acid, hydroxypropyl cellulose, sodium dodecyl sulfate, polyethylene glycol, polypropylene glycol and alkyl monoglycoside;
the auxiliary materials are one or more of sodium chloride, sodium nitrate, sodium sulfate, sodium gluconate, potassium chloride, potassium nitrate and potassium sulfate.
2. The red tide algae algaecide of claim 1, wherein the persulfate is sodium persulfate, oxone, or ammonium persulfate.
3. The red tide algae algaecide of claim 1, wherein the tannin is technical grade with a content of 85-99%.
4. Use of the red tide algae algaecide according to any one of claims 1-3, wherein: the red tide algae algaecide is prepared into a solution and sprayed on the surface of a red tide water body, so that the concentration of the red tide algae algaecide in the red tide water body is 0.001-0.5g/L, and the red tide algae is effectively removed by natural sedimentation for 3-24 hours.
5. Use according to claim 4, characterized in that: the red tide algae is spherical phaeocystis, red tide yizhuan algae, Skeletonema costatum or prorocentrum donghaiense.
CN202110614535.8A 2021-06-02 2021-06-02 Red tide algae removing agent based on tannin activated persulfate and application thereof Pending CN113287628A (en)

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Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2003031684A1 (en) * 2001-09-28 2003-04-17 Bo Shin Ro Surface treating agent for zinc or zinc alloy and method for surface treatment
CN105000655A (en) * 2015-08-05 2015-10-28 同济大学 Method for removing algae in water through oxidizing agent activated through ferrous iron
CN108946907A (en) * 2018-06-06 2018-12-07 中山大学 A kind of method that Fe (III) collaboration plant polyphenol activation persulfate system repairs organic wastewater
CN109942072A (en) * 2019-04-23 2019-06-28 天津华勘环保科技有限公司 A kind of method of natural polyphenol activation persulfate degradating chloro hydrocarbon

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2003031684A1 (en) * 2001-09-28 2003-04-17 Bo Shin Ro Surface treating agent for zinc or zinc alloy and method for surface treatment
CN105000655A (en) * 2015-08-05 2015-10-28 同济大学 Method for removing algae in water through oxidizing agent activated through ferrous iron
CN108946907A (en) * 2018-06-06 2018-12-07 中山大学 A kind of method that Fe (III) collaboration plant polyphenol activation persulfate system repairs organic wastewater
CN109942072A (en) * 2019-04-23 2019-06-28 天津华勘环保科技有限公司 A kind of method of natural polyphenol activation persulfate degradating chloro hydrocarbon

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* Cited by examiner, † Cited by third party
Title
赵钢: ""单宁酸对铜绿微囊藻抑制效果和特性分析"", 《中国优秀博硕士学位论文全文数据库(硕士) 工程科技Ⅰ辑》 *

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