CN112791713A - River course water treatment agent - Google Patents

River course water treatment agent Download PDF

Info

Publication number
CN112791713A
CN112791713A CN202110128355.9A CN202110128355A CN112791713A CN 112791713 A CN112791713 A CN 112791713A CN 202110128355 A CN202110128355 A CN 202110128355A CN 112791713 A CN112791713 A CN 112791713A
Authority
CN
China
Prior art keywords
hours
water
powder
water hyacinth
heating
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN202110128355.9A
Other languages
Chinese (zh)
Inventor
卢惠娟
曹志春
徐文翔
是欢芬
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Changzhou Zhenbang Chemical Manufacturing Co ltd
Original Assignee
Changzhou Zhenbang Chemical Manufacturing Co ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Changzhou Zhenbang Chemical Manufacturing Co ltd filed Critical Changzhou Zhenbang Chemical Manufacturing Co ltd
Priority to CN202110128355.9A priority Critical patent/CN112791713A/en
Publication of CN112791713A publication Critical patent/CN112791713A/en
Pending legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/22Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
    • B01J20/24Naturally occurring macromolecular compounds, e.g. humic acids or their derivatives
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/22Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
    • B01J20/26Synthetic macromolecular compounds
    • B01J20/262Synthetic macromolecular compounds obtained otherwise than by reactions only involving carbon to carbon unsaturated bonds, e.g. obtained by polycondensation
    • 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/285Treatment of water, waste water, or sewage by sorption using synthetic organic sorbents
    • 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/286Treatment of water, waste water, or sewage by sorption using natural organic sorbents or derivatives thereof
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/02Odour removal or prevention of malodour
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/04Disinfection

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Analytical Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Agricultural Chemicals And Associated Chemicals (AREA)

Abstract

The invention provides a river course water treatment agent, cutting petioles of water hyacinth into 5-30 cm in length, putting the petioles into an oven at 70-90 ℃ for 9-11 hours, crushing to obtain powder material, putting the powder material into an aqueous solution for soaking for 2-6 hours, and then filtering, drying and crushing to obtain pretreated water hyacinth powder; dimethyl diallyl ammonium chloride and water are used as raw materials, and potassium persulfate and sodium sulfite are used as initiators; heating to 30-40 ℃ through water bath, and reacting for 0.5-1.5 hours; then heating to 50-60 ℃ for reaction for 0.5-1.5 hours; finally, heating to 65-75 ℃ and reacting for 1-3 hours to obtain poly dimethyl diallyl ammonium chloride; putting the liquid product obtained in the step S3 in an oven at 90-110 ℃ for 18-22 hours, and crushing and grinding the liquid product into powder; uniformly mixing the water hyacinth powder obtained in the step S2 with the poly dimethyl diallyl ammonium chloride obtained in the step S4 to obtain a target product; the invention can not only reduce the blue algae treatment cost, but also has high blue algae treatment efficiency.

Description

River course water treatment agent
Technical Field
The invention relates to the technical field of environmental protection, and particularly relates to a river course water treatment agent.
Background
Eutrophication is a phenomenon of water pollution caused by excessive content of nutrient substances such as nitrogen and phosphorus, and excessive nutrient elements such as nitrogen and phosphorus enter natural water bodies along with the movement of human beings, so that the water bodies are eutrophicated. The blue algae is a common algae in water and has floatability and algae odor. In summer, a large amount of blue algae can be suspended or accumulated on the surface layer of eutrophic water body, so that the water body is anoxic and a large amount of fishes die, and the water body is polluted after the blue algae die and is decomposed.
The current common methods for treating the blue algae harm comprise: 1. removing blue algae by a manual fishing method; 2. setting an artificial fence for blocking; 3. feeding algae-eating animals and plants such as fish, snails, shellfish and the like to control the eutrophication of the water body; 4. sprinkling biological preparation.
The method has certain effect on treating the blue algae in the small water body, but the effect is very limited, and the reason is that: the blue algae body is smaller and fast to propagate, and is mostly suspended on the surface layer of the water body, the blue algae piled on the bank can be salvaged, and the blue algae dispersed in the water is extremely low in salvage efficiency or cannot be salvaged at all. Although the method of fencing, putting in fish and the like is very beneficial to ecological restoration of water and reduction of the number of blue-green algae, the method has the disadvantages of large investment, large implementation difficulty and unsatisfactory algae inhibition and deodorization effects. The simple splashing of biological agents to improve water quality cannot inhibit the growth of blue algae or eliminate the odor of blue algae. The existing blue algae treatment method has great investment, but the effect is more and more successful, so the existing blue algae treatment method has obvious defects and shortcomings.
Disclosure of Invention
The invention aims to provide a river channel water treatment agent which can reduce the blue algae treatment cost and has high blue algae treatment efficiency.
The invention provides the following technical scheme:
a river course water treatment agent comprises the following specific production process:
s1, collecting fresh water hyacinth, taking the petiole of the water hyacinth, cutting the petiole into 5-30 cm long pieces, putting the cut petiole into an oven at 70-90 ℃ for 9-11 hours, and crushing the cut petiole by a crusher to obtain a water hyacinth powder material;
s2, soaking the obtained water hyacinth powder in an aqueous solution for 2 to 6 hours, and then filtering, drying and crushing to obtain pretreated water hyacinth powder;
s3, taking dimethyl diallyl ammonium chloride and water as raw materials, and taking potassium persulfate and sodium sulfite as initiators;
heating to 30-40 ℃ through water bath, and reacting for 0.5-1.5 hours;
then heating to 50-60 ℃ for reaction for 0.5-1.5 hours;
finally, heating to 65-75 ℃ and reacting for 1-3 hours to obtain poly dimethyl diallyl ammonium chloride;
and S4, putting the liquid product obtained in the step S3 in an oven at the temperature of 90-110 ℃ for 18-22 hours, and crushing and grinding the product into powder.
And S5, uniformly mixing the water hyacinth powder obtained in the S2 step with the poly dimethyl diallyl ammonium chloride obtained in the S4 step to obtain the target product.
Preferably, in the step S1, fresh water hyacinth is collected, the petiole of water hyacinth is taken, and the petiole is cut into 10 cm length, and put into an oven at 50 ℃ for 10 hours, and then crushed by a crusher to obtain the water hyacinth powder material
Preferably, in the step S2, the obtained water hyacinth powder is put into an aqueous solution to be soaked for 4 hours, and then the water hyacinth powder is filtered, dried and crushed to obtain the pretreated water hyacinth powder
Preferably, in the step S3, the temperature is raised to 35 ℃ through a water bath to react for 1 hour; then heating to 55 ℃ for reaction for 0.1 hour; and finally, heating to 70 ℃ for reaction for 2 hours to obtain the poly dimethyl diallyl ammonium chloride.
Preferably, in the step S4, the liquid product obtained in the step S3 is put in an oven at 100 degrees celsius for 20 hours, pulverized and ground into powder.
The invention has the beneficial effects that:
the invention uses organic high molecular material and natural cheap and easily available water hyacinth as adsorbent to compound and treat the blue algae in water, thereby having less investment and low implementation difficulty, having outstanding algae inhibiting and deodorizing effects, greatly reducing the blue algae treatment cost and improving the blue algae treatment efficiency.
Detailed Description
Example 1:
a river course water treatment agent comprises the following specific production process:
s1, collecting fresh water hyacinth, taking the petiole of the water hyacinth, cutting the petiole into 5 cm in length, putting the cut petiole into a 70 ℃ oven for 9 hours, and crushing the cut petiole by a crusher to obtain a water hyacinth powder material;
s2, soaking the obtained water hyacinth powder in an aqueous solution for 2 hours, and then filtering, drying and crushing to obtain pretreated water hyacinth powder;
s3, taking dimethyl diallyl ammonium chloride and water as raw materials, and taking potassium persulfate and sodium sulfite as initiators;
heating to 30 ℃ through water bath, and reacting for 0.5 hour;
then heating to 50 ℃ for reaction for 0.5 hour;
finally, heating to 65 ℃ for reaction for 1 hour to obtain poly dimethyl diallyl ammonium chloride;
and S4, putting the liquid product obtained in the step S3 in an oven at 90 ℃ for 18 hours, and crushing and grinding the liquid product into powder.
And S5, uniformly mixing the water hyacinth powder obtained in the S2 step with the poly dimethyl diallyl ammonium chloride obtained in the S4 step to obtain the target product.
Example 2:
a river course water treatment agent comprises the following specific production process:
s1, collecting fresh water hyacinth from the pond, removing roots and leaves of the fresh water hyacinth, only leaving petioles, cutting the petioles into proper lengths, putting the petioles into an oven at 80 ℃ for 10 hours, and crushing the petioles by a crusher to obtain a water hyacinth powder material;
s2, soaking the obtained water hyacinth powder in an aqueous solution, and then filtering, drying and crushing to obtain pretreated water hyacinth powder;
s3, heating dimethyl diallyl ammonium chloride and water as raw materials, heating potassium persulfate and sodium sulfite as initiators to 35 ℃ in a water bath to react for 1 hour, heating to 55 ℃ to react for 1 hour, and finally heating to 70 ℃ to react for 2 hours to obtain the poly dimethyl diallyl ammonium chloride;
s4, putting the obtained liquid product in an oven at 100 ℃ for 20 hours, and crushing and grinding the liquid product into powder.
S5, uniformly mixing the obtained water hyacinth powder and the partial dimethyl diallyl ammonium chloride to obtain the riverway water treatment agent for the algae.
Example 3:
a river course water treatment agent comprises the following specific production process:
s1, collecting fresh water hyacinth, taking the petiole of the water hyacinth, cutting the petiole into 30 cm in length, putting the petiole into a 90 ℃ oven for 11 hours, and crushing the petiole by a crusher to obtain a water hyacinth powder material;
s2, soaking the obtained water hyacinth powder in an aqueous solution for 6 hours, and then filtering, drying and crushing to obtain pretreated water hyacinth powder;
s3, taking dimethyl diallyl ammonium chloride and water as raw materials, and taking potassium persulfate and sodium sulfite as initiators;
heating to 40 ℃ through water bath, and reacting for 1.5 hours;
then heating to 60 ℃ for reaction for 1.5 hours;
finally, heating to 75 ℃ for reaction for 3 hours to obtain poly dimethyl diallyl ammonium chloride;
and S4, putting the liquid product obtained in the step S3 in an oven at the temperature of 110 ℃ for 22 hours, and crushing and grinding the product into powder.
And S5, uniformly mixing the water hyacinth powder obtained in the S2 step with the poly dimethyl diallyl ammonium chloride obtained in the S4 step to obtain the target product.
Experimental analysis: the products obtained in examples 1 to 3 were added to the river, and the specific data were as follows:
example 1:
Figure BDA0002924271560000051
example 2:
Figure BDA0002924271560000052
example 3:
Figure BDA0002924271560000061
although the present invention has been described in detail with reference to the foregoing embodiments, those skilled in the art will understand that various changes, modifications and substitutions can be made without departing from the spirit and scope of the invention as defined by the appended claims. Any modification, equivalent replacement, or improvement made within the spirit and principle of the present invention should be included in the protection scope of the present invention.

Claims (5)

1. The river water treatment agent is characterized by comprising the following production steps:
s1, collecting fresh water hyacinth, taking the petiole of the water hyacinth, cutting the petiole into 5-30 cm long pieces, putting the cut petiole into an oven at 70-90 ℃ for 9-11 hours, and crushing the cut petiole by a crusher to obtain a water hyacinth powder material;
s2, soaking the obtained water hyacinth powder in an aqueous solution for 2 to 6 hours, and then filtering, drying and crushing to obtain pretreated water hyacinth powder;
s3, taking dimethyl diallyl ammonium chloride and water as raw materials, and taking potassium persulfate and sodium sulfite as initiators;
heating to 30-40 ℃ through water bath, and reacting for 0.5-1.5 hours;
then heating to 50-60 ℃ for reaction for 0.5-1.5 hours;
finally, heating to 65-75 ℃ and reacting for 1-3 hours to obtain poly dimethyl diallyl ammonium chloride;
s4, putting the liquid product obtained in the step S3 in an oven at 90-110 ℃ for 18-22 hours, and crushing and grinding the liquid product into powder;
and S5, uniformly mixing the water hyacinth powder obtained in the S2 step with the poly dimethyl diallyl ammonium chloride obtained in the S4 step to obtain the target product.
2. The river water treatment agent according to claim 1, wherein: and S1, collecting fresh water hyacinth, taking the petiole of the water hyacinth, cutting the petiole into 10 cm, putting the petiole into a 50 ℃ oven for 10 hours, and crushing the petiole by using a crusher to obtain the water hyacinth powder material.
3. The river water treatment agent according to claim 1, wherein: and S2, soaking the obtained water hyacinth powder in an aqueous solution for 4 hours, and then filtering, drying and crushing to obtain the pretreated water hyacinth powder.
4. The river water treatment agent according to claim 1, wherein: in the step S3, heating to 35 ℃ through water bath and reacting for 1 hour; then heating to 55 ℃ for reaction for 0.1 hour; and finally, heating to 70 ℃ for reaction for 2 hours to obtain the poly dimethyl diallyl ammonium chloride.
5. The river water treatment agent according to claim 1, wherein in the step S4, the liquid product obtained in the step S3 is put in an oven at 100 ℃ for 20 hours, and is pulverized and ground into powder.
CN202110128355.9A 2021-01-29 2021-01-29 River course water treatment agent Pending CN112791713A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202110128355.9A CN112791713A (en) 2021-01-29 2021-01-29 River course water treatment agent

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202110128355.9A CN112791713A (en) 2021-01-29 2021-01-29 River course water treatment agent

Publications (1)

Publication Number Publication Date
CN112791713A true CN112791713A (en) 2021-05-14

Family

ID=75812928

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202110128355.9A Pending CN112791713A (en) 2021-01-29 2021-01-29 River course water treatment agent

Country Status (1)

Country Link
CN (1) CN112791713A (en)

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101289240A (en) * 2008-02-28 2008-10-22 中国科学院等离子体物理研究所 Novel finishing agent for removing algal tufa and treatment method
CN102701458A (en) * 2012-05-31 2012-10-03 江苏美尚生态景观股份有限公司 Method for treating excessive nitrogen phosphorus and blue-green algae in water body
CN106106143A (en) * 2016-07-06 2016-11-16 那中元 Herba Eichhorniae obtains method and the application thereof of Rhizoma Seu Herba Bergeniae Herba Eichhorniae through induction culturing
CN107162147A (en) * 2017-06-05 2017-09-15 三峡大学 A kind of preparation method and applications of modified water hyacinth alga flocculating agent

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101289240A (en) * 2008-02-28 2008-10-22 中国科学院等离子体物理研究所 Novel finishing agent for removing algal tufa and treatment method
CN102701458A (en) * 2012-05-31 2012-10-03 江苏美尚生态景观股份有限公司 Method for treating excessive nitrogen phosphorus and blue-green algae in water body
CN106106143A (en) * 2016-07-06 2016-11-16 那中元 Herba Eichhorniae obtains method and the application thereof of Rhizoma Seu Herba Bergeniae Herba Eichhorniae through induction culturing
CN107162147A (en) * 2017-06-05 2017-09-15 三峡大学 A kind of preparation method and applications of modified water hyacinth alga flocculating agent

Non-Patent Citations (7)

* Cited by examiner, † Cited by third party
Title
张跃军等: "聚二甲基二烯丙基氯化铵的合成", 《精细化工》 *
施国键等: "天然物质絮凝剂絮凝除藻研究进展", 《工业用水与废水》 *
汪多仁: "《绿色净水处理剂》", 30 November 2006 *
温孟秋等: "絮凝剂聚二甲基二烯丙基氯化铵的合成", 《广州化工》 *
贾旭等: "聚二甲基二烯丙基氯化铵的控制聚合方法", 《石油化工》 *
钟少芬等: "PDMDAAC 的清洁生产工艺合成及在微污染水源水中的应用", 《东莞理工学院学报》 *
陈新华等: "聚二甲基二烯丙基氯化铵的合成及其固色性能研究", 《南通大学学报(自然科学版)》 *

Similar Documents

Publication Publication Date Title
KR101915002B1 (en) Biological processing method for removing green algae from a river or lakes
CN107434303A (en) The processing method of eutrophication aquiculture waste water
CN105016524B (en) A kind of method for removing floating bristle algae
CN111732483B (en) Fermentation method of enteromorpha biological fertilizer
CN108423781A (en) A kind of preparation method and application of magnetic flocculant
CN101779595B (en) Method for implanting and cultivating Gracilaria bursa-pastoris in north pond
CN105417709A (en) Construction method for water body self-cleaning ecological chain
CN101397166A (en) Target loop type ecological restoration for natural water body drinking water sources and water quality improvement technique
CN105478464A (en) Method for removing heavy metal in bottom mud
CN108383243B (en) Method for enriching heavy metals in eutrophic water by utilizing configuration of submerged plants
CN105198511B (en) A kind of multifunctional organic fertilizer and its preparation method and application using tannery sludge and wood fibre
CN105309388B (en) A kind of daphnia heatproof acclimation method and the method for carrying out restoration of the ecosystem to water body using daphnia
CN112791713A (en) River course water treatment agent
CN112723557B (en) Composite ecological treating agent for treating blue-green algae and preparation method and application thereof
CN109912134A (en) A kind of freshwater aquiculture tail water treatment system
Swarup Influence of organic matter and flooding on the chemical and electrochemical properties of sodic soil and rice growth
Sadana et al. Amelioration of iron deficiency in rice and transformations of soil iron in coarse textured soils of Punjab, India
CN111747617A (en) Method for treating pond blue algae bloom
CN109924200B (en) A spirogyra sustained release inhibitor containing Cinnamomum camphora extract and its preparation method
CN107162147B (en) Preparation method and application of modified cucurbita pepo flocculant
Bretschko Annual benthic biomass distribution in a high-mountain lake (Vorderer Finstertaler See, Tyrol, Austria) With 5 figures and 1 table in the text
Singh et al. Acid sulfate soils and their management for brackishwater fishponds
KR20190044215A (en) The Treatment Method of Activated Mineral Group Solution in the shrimp farm
CN104030451B (en) A kind of method that directive breeding original inhabitants diatom is repaired water body
KR20130085858A (en) Composition for inhibiting algae bloom and fabrication method thereof

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20210514

RJ01 Rejection of invention patent application after publication