CN109082277A - A kind of cadmium arsenic combined pollution renovation agent and the preparation method and application thereof - Google Patents

A kind of cadmium arsenic combined pollution renovation agent and the preparation method and application thereof Download PDF

Info

Publication number
CN109082277A
CN109082277A CN201810936188.9A CN201810936188A CN109082277A CN 109082277 A CN109082277 A CN 109082277A CN 201810936188 A CN201810936188 A CN 201810936188A CN 109082277 A CN109082277 A CN 109082277A
Authority
CN
China
Prior art keywords
clay
acid
humic acid
combined pollution
renovation agent
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.)
Granted
Application number
CN201810936188.9A
Other languages
Chinese (zh)
Other versions
CN109082277B (en
Inventor
谭石勇
文亚雄
谭武贵
郭帅
刘备
李雪玲
张冬雪
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.)
Hunan Heavy Metal Polluted Cultivated Land Safe And Efficient Utilization Engineering Research Center Co ltd
Original Assignee
Hunan Taigu Ecological Engineering 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 Hunan Taigu Ecological Engineering Co Ltd filed Critical Hunan Taigu Ecological Engineering Co Ltd
Priority to CN201810936188.9A priority Critical patent/CN109082277B/en
Publication of CN109082277A publication Critical patent/CN109082277A/en
Application granted granted Critical
Publication of CN109082277B publication Critical patent/CN109082277B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C09DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
    • C09KMATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
    • C09K17/00Soil-conditioning materials or soil-stabilising materials
    • C09K17/40Soil-conditioning materials or soil-stabilising materials containing mixtures of inorganic and organic compounds
    • CCHEMISTRY; METALLURGY
    • C09DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
    • C09KMATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
    • C09K2101/00Agricultural use
    • CCHEMISTRY; METALLURGY
    • C09DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
    • C09KMATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
    • C09K2109/00MATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE pH regulation

Abstract

The present invention provides a kind of cadmium arsenic combined pollution renovation agents, including with the mixed calcium carbonate in 10 ~ 30:30 of weight ratio ~ 60:10 ~ 40:1 ~ 10, silicon-calcium-magnesium fertilizer, humic acid modified clay and Fe (OH)3;Wherein, humic acid modified clay through clay acidification, acid-treated clay alkali metal ion and humic acid modified is prepared.Invention further provides a kind of preparation methods of cadmium arsenic combined pollution renovation agent.The described method includes: (1) clay acid activation;(2) acid-treated clay alkali metal ion;(3) humic acid modified clay;(4) cadmium arsenic combined pollution renovation agent is prepared.The cadmium arsenic combined pollution renovation agent that invention provides can effectively lower the activity of cadmium, influence the dissolution of arsenic;It is good and can increase the soil organism to adsorb heavy metal-passivated effect, improves soil texture, promotes plant growth.

Description

A kind of cadmium arsenic combined pollution renovation agent and the preparation method and application thereof
Technical field
The invention belongs to agricultural environment child care and recovery technique field, and in particular to a kind of cadmium arsenic combined pollution renovation agent and Preparation method and application.
Background technique
Soil acidification is a kind of form of expression of soil degradation, soil acidification not still one of soil fertility decline it is important Reason, and an important factor for restriction sustainable development of agricultural production.According to statistics, so far from the eighties in last century, China's soil Acidification situation is increasingly severe, and the land area of acidification has been expanded to 40% or more of China's cultivated area, and often has There is a situation where especially in south China, due to soil slant acidity itself, rainwater is more, and soil acidification phenomenon is more serious in flakes. Soil acidification can cause the activation of the heavy metals such as aluminium, manganese, chromium, cadmium, to influence the growth of plant, poisoning by aluminum, manganese such as occur Phenomena such as poisoning, and activate heavy metal be absorbed by crops accumulation after, pass through the health of food chain harmful to human and animal body.
Adjusting soil acidification is a problem urgently to be solved in modern agriculture environmental protection.It is given through investigation: (1) Improving soil pH can effectively reduce the activity of cadmium in soil, but when reaction is fierce, pH is excessively high, when soil pH larger fluctuation, arsenic quilt Dissolution, the validity of arsenic are enhanced;(2) humic acid is the larger molecular organics matter being widely present in nature, and humic acid divides greatly The basic structure of son is aromatic ring and alicyclic ring, and the functional groups such as carboxyl, hydroxyl, carbonyl, quinonyl, methoxyl group are connected on ring, alternative Complexation heavy metal ion is adsorbed, but humic acid is generally not soluble in water, is dissolved in alkaline solution, limits it and passivation of heavy metal is imitated Fruit;(3) organic matter can be carried on surface of clay by organically-modified by clay material, it is made to obtain preferably absorption heavy metal Effect and adsorptive selectivity, but common such as chitosan and cetyl trimethylammonium bromide (CTMAB) price are higher, technique Complexity, application are less.
Therefore, it is urgent to provide a kind of reaction milder, absorption heavy metal effect is good, validity of arsenic can be effectively reduced and The simpler soil pollution renovation agent of product processes.
Summary of the invention
In view of the shortcomings of the prior art, it is an object of that present invention to provide a kind of cadmium arsenic combined pollution renovation agents and preparation method thereof With application, cadmium arsenic combined pollution renovation agent provided by the invention can effectively lower the activity of cadmium, influence the dissolution of arsenic;Absorption passivation Heavy metal effect is good and can increase the soil organism, improves soil texture, promotes plant growth.
To achieve the goals above, The technical solution adopted by the invention is as follows:
A kind of cadmium arsenic combined pollution renovation agent, which is characterized in that including with 10~30:30 of weight ratio~60:10~40:1 ~10 mixed calcium carbonate, silicon-calcium-magnesium fertilizer, humic acid modified clay and Fe (OH)3;Wherein, humic acid modified clay is through clay acid It activation, acid-activated clay sodium and humic acid modified is prepared.
Further, the humic acid modified clay preparation method specifically comprises the following steps:
The acidification of S1 clay
Clay material is added in acid solution, is filtered after acidified processing, stay first pass filtering acid solution it is spare, and with go from Sub- water cleans filtering filter residue, until filtrate and NaOH do not generate precipitating, obtains acid-treated clay after filtering filter residue dries pulverizing;
S2 acid-treated clay alkali metal ion
Acid-treated clay obtained by S1 is added in lye, is filtered after alkali metal ionization processing, stays filtering lye spare, Alkali metal ion clay is obtained after filtering filter residue dries pulverizing;
The humic acid modified clay of S3
Alkali metal ion clay obtained by S2 is added to containing in humic acid solution, is filtered after humic acid modified processing, And filtering filter residue is cleaned with deionized water and adjusts filtering filter residue pH, humic acid modified clay is obtained after dries pulverizing.
Further, the Fe (OH)3It is prepared by following methods: ground hematite is added to the resulting first pass mistake of S1 It in acid filtering liquid, is filtered after fully reacting, takes filtrate spare;Gained filtrate is adjusted into pH to Fe with the resulting filtering lye of S23+It is complete Full precipitating, filtering drying obtain Fe (OH) after crushing3
Further, clay material described in S1 is one of sepiolite, zeolite, attapulgite, montmorillonite, kaolin etc. Or it is a variety of.
Further, clay material partial size≤75 μm.
Further, the clay material and the mass ratio of acid solution are 1:1~20, the acid strength be 0.1mol/L~ 10mol/L。
Further, the acid solution is one or more of sulfuric acid, nitric acid, hydrochloric acid.
Further, acidification temperature described in S1 is 10 DEG C~40 DEG C, and the activation processing time is 5~120min.
Further, the ratio of acid-treated clay described in S2 and the lye is 1:1~30;The concentration of lye is 0.5% ~10%.
Further, the lye is NaOH, KOH, Na2CO3、K2CO3One of or it is a variety of.
Further, the alkali metal ion treatment temperature is 10 DEG C~40 DEG C, and the alkali metal ionization handles the time For 1min~30min.
Further, alkali metal ion clay described in S3 and the ratio containing humic acid solution are 1:1~30;It is described Containing content of humic acid >=1% in humic acid solution.
Further, described containing humic acid solution is potassium humate, sodium humate, ammonium humate, one in nitro humus acid Kind or the aqueous solution of a variety of preparations.
Further, the temperature of the humic acid modified processing is 10 DEG C~40 DEG C, and the processing time is 5min~120min.
Further, the humic acid modified clay pH is 8~12.
Further, iron content >=50% in the ground hematite;The ratio of the ground hematite and first pass filtering acid solution For 1~20:100.
Further, CaCO in the calcium carbonate3Content >=90%;CaO content >=40% in the silicon-calcium-magnesium fertilizer, effectively Silicone content >=30%, content of MgO >=5%.
Based on the same inventive concept, the present invention also provides a kind of preparation method of cadmium arsenic combined pollution renovation agent, It is characterized in that, includes the following steps:
The acidification of S1 clay
Clay material is added in acid solution, is filtered after acidified processing, stay first pass filtering acid solution it is spare, and with go from Sub- water cleans filtering filter residue, until filtrate and NaOH do not generate precipitating, obtains acid-treated clay after filtering filter residue dries pulverizing;
S2 acid-treated clay alkali metal ion
Acid-activated clay obtained by S1 is added in lye, is filtered after the processing of clay alkali metal ionization, stays filtering alkali Liquid is spare, obtains alkali metal ion clay after filtering filter residue dries pulverizing;
The humic acid modified clay of S3
Alkali metal ionization obtained by S2 is added containing in humic acid solution, is filtered after humic acid modified processing, and to go Ionized water cleaning filtering filter residue simultaneously adjusts filtering filter residue pH, obtains humic acid modified clay after dries pulverizing;
S4 prepares cadmium arsenic combined pollution renovation agent
By humic acid modified clay, Fe (OH) obtained by calcium carbonate, silicon-calcium-magnesium fertilizer, S33With weight ratio 10~30:30~60: 10~40:1~10 mix up to cadmium arsenic combined pollution renovation agent.
Further, the Fe (OH)3It is prepared by following methods: ground hematite is added to the resulting first pass mistake of S1 It in acid filtering liquid, is filtered after fully reacting, takes filtrate spare;Gained filtrate is adjusted into pH to Fe with the resulting filtering lye of S23+It is complete Full precipitating, filtering drying obtain Fe (OH) after crushing3
Further, in the preparation method, clay material described in S1 be sepiolite, zeolite, attapulgite, montmorillonite, One of kaolin etc. is a variety of.Clay material partial size≤75 μm.The clay material and the mass ratio of acid solution are 1:1 ~20, the acid strength is 0.1mol/L~10mol/L.The acid solution is one or more of sulfuric acid, nitric acid, hydrochloric acid. Acidification temperature described in S1 is 10 DEG C~40 DEG C, and the activation processing time is 5~120min.Acid-treated clay described in S2 and institute The ratio for stating lye is 1:1~30;The concentration of lye is 0.5%~10%.The lye is NaOH, KOH, Na2CO3、 K2CO3One of or it is a variety of.The alkali metal ion treatment temperature is 10 DEG C~40 DEG C, the alkali metal ionization processing Time is 1min~30min.Alkali metal ion clay described in S3 and the ratio containing humic acid solution are 1:1~30; It is described to contain content of humic acid >=1% in humic acid solution.The humic acid solution that contains is potassium humate, sodium humate, humic acid One of ammonium, nitro humus acid or the aqueous solution of a variety of preparations.The temperature of the humic acid modified processing is 10 DEG C~40 DEG C, The processing time is 5min~120min.The humic acid modified clay pH is 8~12.Iron content in the ground hematite >= 50%;The ratio of the ground hematite and first pass filtering acid solution is 1~20:100.CaCO in the calcium carbonate3Content >= 90%;CaO content >=40% in the silicon-calcium-magnesium fertilizer, available silicon content >=30%, content of MgO >=5%.
Based on the same inventive concept, the present invention also provides the application for having crossed a kind of above-mentioned cadmium arsenic combined pollution renovation agent, The cadmium arsenic combined pollution renovation agent is applied to adjust acidification soil, especially adjusting acidification paddy soils and drought soil.It is preferred that , the pH of the acidification soil is 4.5-6.0;Preferably, when the cadmium arsenic combined pollution renovation agent adjusts acid soil again Amount of application be 100-200kg/ mus, preferably 150kg/ mus.
The research of the invention finds that improving soil pH can effectively reduce the activity of cadmium in soil, but when pH is excessively high, arsenic is molten Out, the validity of arsenic is improved, therefore salt of weak acid is selected to promote soil pH, reaction speed is slower, the influence fluctuation to soil pH It is smaller.In addition, the oxide and hydroxide of iron have single-minded adsorptivity to arsenic, the validity of arsenic can effectively reduce.Humic acid It is a kind of macromolecular substances, alternative absorption complexation heavy metal ion.But humic acid is generally not soluble in water, and it is molten to be dissolved in alkalinity Liquid limits its passivation effect to heavy metal.In addition, total amount of humic acid is surprisingly big, number is of the invention former in terms of trillion tons The preferable source of material.
The invention has the benefit that
The present invention provides a kind of cadmium arsenic combined pollution renovation agent, advantages are as follows: (1) improves soil pH value, influence arsenic Dissolution: calcium carbonate, calcium silicate fertilizer, modified humic acid clay in the present invention are alkaline matter and contain various nutrient elements, such as Alkali displacement capacity can be improved in calcium, magnesium, silicon etc., so that soil pH value be made to increase, but reacts mild, not will cause soil pH compared with Great fluctuation process reduces the validity of arsenic to influence the dissolution of arsenic;(2) heavy metal-passivated, reduce heavy metal validity: the present invention In alkaline matter the free acid in soil can be neutralized by basic mineral, displace the hydrogen ion on manosil AS, and pass through It supplements activated silica and increases absorption of the soil to cation, then promote the coprecipitated of anion and heavy metal by improving soil pH value It forms sediment, reduces the biological effectiveness of heavy metal;Modified humic acid clay can Absorptive complex wave heavy metal, reduce its validity;Fe(OH)3 Can obligate arsenic-adsorbing, can effectively reduce the validity of arsenic;(3) increase the soil organism, improve soil texture, promote plant raw Long: modified humic acid clay can be improved soil organic matter content in the present invention, reduce the soil weight, improve soil texture;Separately Outside, it can promote plant growth containing various nutrient elements such as K, Ca, Mg needed for plant in the present invention.
Invention further provides a kind of preparation method of cadmium arsenic combined pollution renovation agent, advantages are as follows: (1) prepares Humic acid modified adsorption by clay performance is good, easily settled, easy recycling, and prepares industry simply, low in cost: right first in this method Clay carries out acidification, removes the cation between crystals of clay, increases clay specific surface area and micropore size, recycles alkali heat Condition makes clay material adsorb humic acid molecule, is surface modified to clay, makes humic acid modified clay to heavy metal ion With adsorption selectivity and higher adsorption capacity;Prepared humic acid Modified clay mineral adsorbent absorption property is good, easily Sedimentation, easily recycling are suitable for Industrial Wastewater Treatment and soil remediation, and preparation industry is simple, low in cost;(2) present invention system Standby Fe (OH)3Method advantage are as follows: using the lower Iron Ore Powder for the treatment of cost of waste liquor in production process to produce Fe (OH)3, increase Add purity, improve its validity, and achievees the effect that waste utilization and reduce cost;(3) calcium carbonate, silicon-calcium-magnesium in this method Fertile, humic acid modified clay and Fe (OH)3Compound prescription ratio obtained through testing repeatedly, and each component cooperate, collaboration It plays a role.
Invention further provides a kind of cadmium arsenic combined pollution renovation agents to adjust the application on acidification soil, especially It is to adjust acidification paddy soils and drought soil.It is tested in application effect of the cadmium arsenic combined pollution renovation agent of the present invention to pollution rice field In, cadmium arsenic combined pollution renovation agent provided by the invention can effectively improve soil pH value, while reduce the cadmium in rice, arsenic Content.In addition, also known by this experiment, it is compound to add 100~200kg cadmium arsenic of the present invention in acid soil per acre Pollution amelioration agent is advisable;Preferably, cadmium arsenic combined pollution renovation agent described in 150kg is added in acid soil per acre.
Specific embodiment
The following examples are used to illustrate the present invention, but are not intended to limit the scope of the present invention..It is not specified in embodiment specific Technology or conditions person, described technology or conditions according to the literature in the art, or carried out according to product description.It is used Production firm person is not specified in reagent or instrument, is the conventional products that can be commercially available by regular distributor.
1 cadmium arsenic combined pollution renovation agent of embodiment
1) ratio by attapulgite with mass ratio for 1:10 is added in the sulfuric acid of 1mol/L, is activated at 25 DEG C 30min is filtered after activation, stays first pass filtering acid solution spare, and gained filter residue is cleaned repeatedly with deionized water, until Gained washing lotion and NaOH do not generate precipitating (being washed till non-metallic ion), and dries pulverizing obtains acidification attapulgite;
2) viscous ratio of the attapulgite with mass ratio for 1:10 will be acidified to be added in the NaOH solution that concentration is 4%, Modified 30min, is filtered after modified at 25 DEG C, stays filtering lye spare, filters filter residue dries pulverizing up to alkali metal ion Change attapulgite;
3) ratio by alkali metal ion attapulgite with mass ratio for 1:20 is added to the potassium humate that concentration is 5% In solution, modified 60min, is filtered after modified at 25 DEG C, is cleaned gained filter residue with deionized water, is adjusted pH to 10, dry Dry grinding is up to humic acid modified attapulgite.
4) ratio by ground hematite with mass ratio for 8:100 is added in the resulting first pass filtering acid solution of step 1), It is spare that filtrate is filtered to take after fully reacting;
5) to filter lye regulating step 4 obtained by step 2)) in filtrate pH to Fe3+Precipitating completely, filtering drying crush It obtains Fe (OH)3
6) by calcium carbonate, silicon-calcium-magnesium fertilizer, humic acid modified attapulgite, Fe (OH)3With the weight ratio of 20:50:25:5 Mixing is to get cadmium arsenic combined pollution renovation agent.
2 cadmium arsenic combined pollution renovation agent of embodiment
1) ratio by attapulgite with mass ratio for 1:10 is added in the sulfuric acid of 1mol/L, is activated at 25 DEG C 30min is filtered after activation, stays first pass filtering acid solution spare, and gained filter residue is cleaned repeatedly with deionized water, until Gained washing lotion and NaOH do not generate precipitating (being washed till non-metallic ion), and dries pulverizing must be acidified attapulgite;
2) ratio of the attapulgite with mass ratio for 1:10 will be acidified to be added in the NaOH solution that concentration is 4%, 25 Modified 30min, is filtered after modified at DEG C, stays filtering lye spare, filters filter residue dries pulverizing up to alkali metal ion Attapulgite.
3) ratio by alkali metal ion attapulgite with mass ratio for 1:20 is added to the potassium humate that concentration is 5% In solution, modified 60min, is filtered after modified at 25 DEG C, is cleaned gained filter residue with deionized water, is adjusted pH to 10, dry Dry grinding is up to humic acid modified attapulgite.
4) ratio by ground hematite with mass ratio for 8:100 is added in the resulting first pass filtering acid solution of step 1), It is spare that filtrate is filtered to take after fully reacting;
5) to filter lye regulating step 4 obtained by step 2)) in filtrate pH to Fe3+Precipitating completely, filtering drying crush It obtains Fe (OH)3
6) by calcium carbonate, silicon-calcium-magnesium fertilizer, humic acid modified attapulgite, Fe (OH)3With the weight ratio of 30:50:15:5 Mixing is to get cadmium arsenic combined pollution renovation agent.
3 cadmium arsenic combined pollution renovation agent of embodiment
1) ratio by attapulgite with mass ratio for 1:10 is added in the sulfuric acid of 1mol/L, is activated at 25 DEG C 30min is filtered after activation, stays first pass filtering acid solution spare, and gained filter residue is cleaned repeatedly with deionized water, until Gained washing lotion and NaOH do not generate precipitating (being washed till non-metallic ion), and dries pulverizing must be acidified attapulgite;
2) ratio of the attapulgite with mass ratio for 1:10 will be acidified to be added in the NaOH solution that concentration is 4%, 25 Modified 30min, is filtered after modified at DEG C, stays filtering lye spare, filters filter residue dries pulverizing up to alkali metal ion Attapulgite.
3) ratio by alkali metal ion attapulgite with mass ratio for 1:20 is added to the potassium humate that concentration is 5% In solution, modified 60min, is filtered after modified at 25 DEG C, is cleaned gained filter residue with deionized water, is adjusted pH to 10, dry Dry grinding is up to humic acid modified attapulgite.
4) ratio by ground hematite with mass ratio for 8:100 is added the resulting first pass of step 1) and filters in acid solution, instead It is spare that filtrate is filtered to take after answering completely;
5) to filter lye regulating step 4 obtained by step 2)) in filtrate pH to Fe3+Precipitating completely, filtering drying crush It obtains Fe (OH)3
6) by calcium carbonate, silicon-calcium-magnesium fertilizer, humic acid modified attapulgite, Fe (OH)3With the weight ratio of 24:50:25:1 Mixing is to get cadmium arsenic combined pollution renovation agent.
4 cadmium arsenic combined pollution renovation agent of embodiment
1) ratio by attapulgite with mass ratio for 1:10 is added in the hydrochloric acid of 0.1mol/L, is activated at 25 DEG C 30min is filtered after activation, stays first pass filtering acid solution spare, and gained filter residue is cleaned repeatedly with deionized water, until Gained washing lotion and NaOH do not generate precipitating (being washed till non-metallic ion), and dries pulverizing obtains acidification attapulgite;
2) viscous ratio of the attapulgite with mass ratio for 1:10 will be acidified to be added in the NaOH solution that concentration is 1%, Modified 30min, is filtered after modified at 25 DEG C, stays filtering lye spare, filters filter residue dries pulverizing up to alkali metal ion Change attapulgite;
3) ratio by alkali metal ion attapulgite with mass ratio for 1:20 is added to the potassium humate that concentration is 1% In solution, modified 60min, is filtered after modified at 25 DEG C, is cleaned gained filter residue with deionized water, is adjusted pH to 10, dry Dry grinding is up to humic acid modified attapulgite.
4) ratio by ground hematite with mass ratio for 8:100 is added in the resulting first pass filtering acid solution of step 1), It is spare that filtrate is filtered to take after fully reacting;
5) to filter lye regulating step 4 obtained by step 2)) in filtrate pH to Fe3+Precipitating completely, filtering drying crush It obtains Fe (OH)3
6) by calcium carbonate, silicon-calcium-magnesium fertilizer, humic acid modified attapulgite, Fe (OH)3With the weight ratio of 20:50:25:5 Mixing is to get cadmium arsenic combined pollution renovation agent.
5 cadmium arsenic combined pollution renovation agent of embodiment
1) ratio by attapulgite with mass ratio for 1:10 is added in the sulfuric acid of 1mol/L, is activated at 25 DEG C 30min is filtered after activation, stays first pass filtering acid solution spare, and gained filter residue is cleaned repeatedly with deionized water, until Gained washing lotion and NaOH do not generate precipitating (being washed till non-metallic ion), and dries pulverizing obtains acidification attapulgite;
2) viscous ratio of the attapulgite with mass ratio for 1:10 will be acidified to be added in the NaOH solution that concentration is 4%, Modified 30min, is filtered after modified at 25 DEG C, stays filtering lye spare, filters filter residue dries pulverizing up to alkali metal ion Change attapulgite;
3) ratio by alkali metal ion attapulgite with mass ratio for 1:20 is added to the potassium humate that concentration is 5% In solution, modified 60min, is filtered after modified at 25 DEG C, is cleaned gained filter residue with deionized water, is adjusted pH to 10, dry Dry grinding is up to humic acid modified attapulgite.
6) by calcium carbonate, silicon-calcium-magnesium fertilizer, humic acid modified attapulgite, ground hematite with the weight ratio of 20:50:25:5 Mixing is to get cadmium arsenic combined pollution renovation agent.
The application effect of experimental example cadmium arsenic combined pollution renovation agent of the present invention is tested
The cadmium arsenic combined pollution renovation agent that Example 1,2,3 provides is tested.
1, test site: xiangtan, hunan province county Yang Jia bridge town.
2, test period: in June, 2017~2017 year October.
3, field experimental design: selection size is close, and the field that water system is independent of each other is tested.Test sets 6 processing, Be respectively as follows: (1) control treatment 1: uncontaminated rice field does not deal with measure;;(2) control treatment 2: pollution rice field does not deal with and arranges It applies;(3) test process 1: pollution rice field, 10 days 50kg/ mus of combined pollution renovation agent of the application cadmium arsenic before rice transplanting;(4) it tries Test processing 2: pollution rice field, 10 days 100kg/ mus of combined pollution renovation agent of the application cadmium arsenic before rice transplanting;(5) test process 3: Pollute rice field, 10 days 150kg/ mus of combined pollution renovation agent of the application cadmium arsenic before rice transplanting.(6) test process 4: pollution rice Field, 10 days 200kg/ mus of combined pollution renovation agent of the application cadmium arsenic before rice transplanting.Each processing is normally ploughed by local Rice Cropping It manages.After rice harves, rice yield, soil pH, rice arsenic content, rice cadmium content are measured.
4, test result:
Example 1,2,3,4,5 provide cadmium arsenic combined pollution renovation agent tested, be as a result shown in Table respectively 1, table 2, Table 3, table 4, table 5.
Improved effect of 1 embodiment of table, the 1 cadmium arsenic combined pollution renovation agent to soil and rice
Improved effect of 2 embodiment of table, the 2 cadmium arsenic combined pollution renovation agent to soil and rice
Improved effect of 3 embodiment of table, the 3 cadmium arsenic combined pollution renovation agent to soil and rice
Improved effect of 4 embodiment of table, the 4 cadmium arsenic combined pollution renovation agent to soil and rice
Improved effect of 5 embodiment of table, the 5 cadmium arsenic combined pollution renovation agent to soil and rice
As table 1, table 2, table 3, table 4, shown in experimental result it is found that cadmium arsenic combined pollution renovation agent provided by the invention can To effectively improve soil pH value, rice yield is improved, while reducing the cadmium in rice, arsenic content.In addition, also by this experiment It is found that being advisable with adding 100~200kg cadmium arsenic combined pollution renovation agent of the present invention in acid soil per acre;Preferably, Cadmium arsenic combined pollution renovation agent described in 150kg is added in acid soil per acre.It also knows, reduces Fe (OH) from table 33Ratio, As a result visible rice arsenic handles high (embodiment 1,2 and 4) compared with other);As known from Table 5, Fe (OH)3There is better reparation than miberal powder Effect.
Although above having used general explanation, specific embodiment and test, the present invention is made to retouch in detail It states, but on the basis of the present invention, it can be made some modifications or improvements, this is apparent to those skilled in the art 's.Therefore, these modifications or improvements without departing from theon the basis of the spirit of the present invention, belong to claimed Range.

Claims (10)

1. a kind of cadmium arsenic combined pollution renovation agent, which is characterized in that including with 10~30:30 of weight ratio~60:10~40:1~ 10 mixed calcium carbonate, silicon-calcium-magnesium fertilizer, humic acid modified clay and Fe (OH)3;Wherein, humic acid modified clay is through clay acid Change, acid-treated clay alkali metal ion and humic acid modified be prepared.
2. cadmium arsenic combined pollution renovation agent according to claim 1, which is characterized in that the humic acid modified clay preparation Method specifically comprises the following steps:
The acidification of S1 clay
Clay material is added in acid solution, is filtered after acidified processing, stays first pass filtering acid solution spare, and with deionized water Filtering filter residue is cleaned, until filtrate and NaOH do not generate precipitating, obtains acid-treated clay after filtering filter residue dries pulverizing;
S2 acid-treated clay alkali metal ion
Acid-treated clay obtained by S1 is added in lye, is filtered after alkali metal ionization processing, stays filtering lye spare, filtering Alkali metal ion clay is obtained after filter residue dries pulverizing;
The humic acid modified clay of S3
Alkali metal ion clay obtained by S2 is added to containing in humic acid solution, is filtered after humic acid modified processing, and with Deionized water cleaning filtering filter residue simultaneously adjusts filtering filter residue pH, obtains humic acid modified clay after dries pulverizing.
3. cadmium arsenic combined pollution renovation agent according to claim 2, which is characterized in that the Fe (OH)3By following methods system It is standby to form: ground hematite being added in the resulting first pass filtering acid solution of S1, is filtered after fully reacting, takes filtrate spare;It will Gained filtrate adjusts pH to Fe with the resulting filtering lye of S23+Precipitating completely, filtering drying obtain Fe (OH) after crushing3
4. cadmium arsenic combined pollution renovation agent according to claim 2, it is characterised in that: clay material described in S1 is Hai Pao One of stone, zeolite, attapulgite, montmorillonite, kaolin etc. are a variety of;
Clay material partial size≤75 μm and/or;
And/or the clay material and the mass ratio of acid solution are 1:1~20, the acid strength is 0.1mol/L~10mol/ L;
And/or the acid solution is one or more of sulfuric acid, nitric acid, hydrochloric acid;
And/or acidification temperature described in S1 is 10 DEG C~40 DEG C, the activation processing time is 5~120min.
5. cadmium arsenic combined pollution renovation agent according to claim 2, it is characterised in that: acid-treated clay described in S2 with it is described The ratio of lye is 1:1~30;The concentration of lye is 0.5%~10%;
And/or the lye is NaOH, KOH, Na2CO3、K2CO3One of or it is a variety of;
And/or the alkali metal ion treatment temperature is 10 DEG C~40 DEG C, the alkali metal ionization processing time is 1min ~30min.
6. cadmium arsenic combined pollution renovation agent according to claim 2, it is characterised in that: alkali metal ionization described in S3 is viscous The native and ratio containing humic acid solution is 1:1~30;It is described to contain content of humic acid >=1% in humic acid solution;
And/or the humic acid solution that contains is one of potassium humate, sodium humate, ammonium humate, nitro humus acid or more The aqueous solution that kind is prepared;
And/or the temperature of the humic acid modified processing is 10 DEG C~40 DEG C, the processing time is 5min~120min;
And/or the humic acid modified clay pH is 8~12.
7. cadmium arsenic combined pollution renovation agent according to claim 3, which is characterized in that iron content in the ground hematite >= 50%;The ratio of the ground hematite and first pass filtering acid solution is 1~20:100.
8. a kind of preparation method of cadmium arsenic combined pollution renovation agent, which comprises the steps of:
The acidification of S1 clay
Clay material is added in acid solution, is filtered after acidified processing, stays first pass filtering acid solution spare, and with deionized water Filtering filter residue is cleaned, until filtrate and NaOH do not generate precipitating, obtains acid-treated clay after filtering filter residue dries pulverizing;
S2 acid-treated clay alkali metal ion
Acid-treated clay obtained by S1 is added to containing in soda lye, is filtered after alkali metal ionization processing, stays filtering lye spare, Alkali metal ion clay is obtained after filtering filter residue dries pulverizing;
The humic acid modified clay of S3
Alkali metal ion clay obtained by S2 is added containing in humic acid solution, is filtered after humic acid modified processing, and to go Ionized water cleaning filtering filter residue simultaneously adjusts filtering filter residue pH, obtains humic acid modified clay after dries pulverizing;
S4 prepares cadmium arsenic combined pollution renovation agent
By humic acid modified clay, Fe (OH) obtained by calcium carbonate, silicon-calcium-magnesium fertilizer, S33With 10~30:30 of weight ratio~60:10~ 40:1~10 mix up to cadmium arsenic combined pollution renovation agent.
9. a kind of preparation method of cadmium arsenic combined pollution renovation agent according to claim 1, which is characterized in that the Fe (OH)3It is prepared: ground hematite being added in the resulting first pass filtering acid solution of S1, mistake after fully reacting by following methods Filter, takes filtrate spare;Gained filtrate is adjusted into pH to Fe with the resulting filtering lye of S23+Precipitating completely, after filtering drying crushes It obtains Fe (OH)3
10. any one of a kind of described in any item cadmium arsenic combined pollution renovation agents of the claim 1-7 or claim 8-9 side The application of cadmium arsenic combined pollution renovation agent made from method, it is characterised in that: the cadmium arsenic combined pollution renovation agent is for adjusting acid Property soil, especially adjusting acidification paddy soils and drought soil;Preferably, the pH of the acidification soil is 4.5-6.0;It is preferred that , the amount of application when cadmium arsenic combined pollution renovation agent adjusts acid soil again is 100-200kg/ mus, preferably 150kg/ Mu.
CN201810936188.9A 2018-08-16 2018-08-16 Cadmium-arsenic composite pollution remediation agent and preparation method and application thereof Active CN109082277B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810936188.9A CN109082277B (en) 2018-08-16 2018-08-16 Cadmium-arsenic composite pollution remediation agent and preparation method and application thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810936188.9A CN109082277B (en) 2018-08-16 2018-08-16 Cadmium-arsenic composite pollution remediation agent and preparation method and application thereof

Publications (2)

Publication Number Publication Date
CN109082277A true CN109082277A (en) 2018-12-25
CN109082277B CN109082277B (en) 2020-12-04

Family

ID=64793634

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810936188.9A Active CN109082277B (en) 2018-08-16 2018-08-16 Cadmium-arsenic composite pollution remediation agent and preparation method and application thereof

Country Status (1)

Country Link
CN (1) CN109082277B (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109909291A (en) * 2019-04-03 2019-06-21 陈泽欣 A kind of prosthetic device and restorative procedure of cadmium pollution soil
CN110016351A (en) * 2019-05-06 2019-07-16 湖南泰谷生态工程有限公司 The preparation method and applications of cadmium arsenic combined pollution renovation agent based on natural macromolecular organic matter
CN110194956A (en) * 2019-05-10 2019-09-03 湖南泰谷生态工程有限公司 Organic type cadmium arsenic combined pollution renovation agent and the preparation method and application thereof
CN111269722A (en) * 2020-03-02 2020-06-12 中南林业科技大学 Slow-release type repairing agent for treating cadmium-arsenic composite polluted paddy soil and preparation method thereof
CN112355041A (en) * 2020-09-27 2021-02-12 清华大学 Preparation method and application of hyperstable mineralizer for treating arsenic pollution
CN114014429A (en) * 2021-09-08 2022-02-08 铜陵晟泽环保科技有限公司 Organic-inorganic heavy metal ion trapping agent and preparation method thereof
CN114410310A (en) * 2021-12-29 2022-04-29 武汉市秀谷科技有限公司 Foliar blocking agent for reducing cadmium in rice and preparation method thereof
CN114774130A (en) * 2022-04-15 2022-07-22 哈尔滨工业大学 Modified clay mineral for repairing arsenic-lead-antimony composite contaminated soil and preparation method and application thereof

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101805617A (en) * 2009-02-16 2010-08-18 中国科学院沈阳应用生态研究所 Soil heavy metal passivant for facilities vegetable field and preparation method thereof
CN104479683A (en) * 2014-12-15 2015-04-01 湖南省土壤肥料研究所 Soil conditioner capable of being used for soil acidification conditioning and cadmium pollution repair and preparation method thereof
CN104804747A (en) * 2015-04-27 2015-07-29 衡阳保地环境科技有限公司 Calcium-based heavy metal soil repairing agent and preparation method
CN106947488A (en) * 2017-04-27 2017-07-14 安徽皖东农业科技有限公司 A kind of mineral matter Vegetable Soil modifying agent and preparation method thereof
CN107446588A (en) * 2017-08-29 2017-12-08 湖南泰谷生物科技股份有限公司 Humic acid type acidic soil conditioner and preparation method and application

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101805617A (en) * 2009-02-16 2010-08-18 中国科学院沈阳应用生态研究所 Soil heavy metal passivant for facilities vegetable field and preparation method thereof
CN104479683A (en) * 2014-12-15 2015-04-01 湖南省土壤肥料研究所 Soil conditioner capable of being used for soil acidification conditioning and cadmium pollution repair and preparation method thereof
CN104804747A (en) * 2015-04-27 2015-07-29 衡阳保地环境科技有限公司 Calcium-based heavy metal soil repairing agent and preparation method
CN106947488A (en) * 2017-04-27 2017-07-14 安徽皖东农业科技有限公司 A kind of mineral matter Vegetable Soil modifying agent and preparation method thereof
CN107446588A (en) * 2017-08-29 2017-12-08 湖南泰谷生物科技股份有限公司 Humic acid type acidic soil conditioner and preparation method and application

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
吴玉俊等: "组配改良剂对污染稻田中Pb、Cd、Cu和Zn钝化效果持续性比较", 《环境科学》 *
商平等编著: "《环境矿物材料》", 31 January 2008, 化学工业出版社 *
李剑睿等: "农田重金属污染原位钝化修复研究进展", 《生态环境学报》 *

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109909291A (en) * 2019-04-03 2019-06-21 陈泽欣 A kind of prosthetic device and restorative procedure of cadmium pollution soil
CN110016351A (en) * 2019-05-06 2019-07-16 湖南泰谷生态工程有限公司 The preparation method and applications of cadmium arsenic combined pollution renovation agent based on natural macromolecular organic matter
CN110016351B (en) * 2019-05-06 2021-03-16 湖南泰谷生态工程有限公司 Preparation method and application of cadmium-arsenic composite pollution repairing agent based on natural macromolecular organic matter
CN110194956A (en) * 2019-05-10 2019-09-03 湖南泰谷生态工程有限公司 Organic type cadmium arsenic combined pollution renovation agent and the preparation method and application thereof
CN111269722A (en) * 2020-03-02 2020-06-12 中南林业科技大学 Slow-release type repairing agent for treating cadmium-arsenic composite polluted paddy soil and preparation method thereof
CN111269722B (en) * 2020-03-02 2021-04-13 中南林业科技大学 Slow-release type repairing agent for treating cadmium-arsenic composite polluted paddy soil and preparation method thereof
CN112355041A (en) * 2020-09-27 2021-02-12 清华大学 Preparation method and application of hyperstable mineralizer for treating arsenic pollution
CN114014429A (en) * 2021-09-08 2022-02-08 铜陵晟泽环保科技有限公司 Organic-inorganic heavy metal ion trapping agent and preparation method thereof
CN114410310A (en) * 2021-12-29 2022-04-29 武汉市秀谷科技有限公司 Foliar blocking agent for reducing cadmium in rice and preparation method thereof
CN114774130A (en) * 2022-04-15 2022-07-22 哈尔滨工业大学 Modified clay mineral for repairing arsenic-lead-antimony composite contaminated soil and preparation method and application thereof

Also Published As

Publication number Publication date
CN109082277B (en) 2020-12-04

Similar Documents

Publication Publication Date Title
CN109082277A (en) A kind of cadmium arsenic combined pollution renovation agent and the preparation method and application thereof
CN111100652A (en) Heavy metal contaminated soil remediation agent and preparation method and application method thereof
Lugo-Lugo et al. Biosorption of Cr (III) and Fe (III) in single and binary systems onto pretreated orange peel
CN110194956A (en) Organic type cadmium arsenic combined pollution renovation agent and the preparation method and application thereof
Wang et al. Zeolite-supported manganese oxides decrease the Cd uptake of wheat plants in Cd-contaminated weakly alkaline arable soils
CN106147778A (en) Passivator, preparation method and applications for repairing heavy metal in soil combined pollution
CN110591728B (en) Conditioner for mercury-polluted soil and preparation method thereof
CN103965919A (en) Heavy metal composite passivant suitable for northern farmland soil and preparing and using method thereof
CN104946262A (en) Acidic farmland soil heavy metal cadmium pollution in situ passivation conditioner and preparation method thereof
CN107779196A (en) A kind of preparation and application of soil heavy metal combined passivator
CN102614834A (en) Method for adsorbing and recovering heavy metals of lead and copper by persimmon tannin-containing metal adsorbent
CN108727117A (en) A kind of Selenium in Soil element activator and preparation method thereof
CN104338743A (en) Composite modifying agent for repairing paddy field soil Cd pollution and preparation method and application method thereof
CN114276817B (en) Soil restoration agent and preparation method and application thereof
CN107699249A (en) A kind of passivator of farmland soil heavy metals pollution and its preparation method and application
CN106929030A (en) A kind of soil passivation modifying agent and preparation method and application
Bashir et al. The role of different organic amendments to improve maize growth in wastewater irrigated soil
He et al. Application of chitosan-and alginate-modified biochars in promoting the resistance to paddy soil acidification and immobilization of soil cadmium
Li et al. Preparation of wheat bran-titanium dioxide (TiO2) composite and its application for selenium adsorption
Hasan et al. Nanomaterials and soil health for agricultural crop production: current status and future prospects
CN106833651A (en) Active medical stone soil heavy mental ion adsorption passivator and preparation method thereof
CN113999684A (en) Soil conditioning composition and preparation method thereof
JP4822586B2 (en) Method for producing agropolymer and method for using the agropolymer for purification of contaminated water or contaminated water containing metal or ions
CN115637151B (en) Acid soil conditioner and preparation method thereof
CN111348964B (en) Conditioner for treating farmland cadmium-polluted soil based on momordica grosvenori waste materials and preparation method of conditioner

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
GR01 Patent grant
GR01 Patent grant
TR01 Transfer of patent right

Effective date of registration: 20210401

Address after: Room 310-3, headquarters building, Changsha Zhongdian Software Park Co., Ltd., No. 39, Jianshan Road, Changsha hi tech Development Zone, Changsha, Hunan 410000

Patentee after: Hunan Huigu Agricultural Ecology Research Institute Co.,Ltd.

Address before: 1504, 1505, luguyuyuan venture building, 27 Wenxuan Road, high tech Development Zone, Changsha, Hunan 410000

Patentee before: HUNAN TAIGU ECOLOGICAL ENGINEERING Co.,Ltd.

TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20230410

Address after: 410000 room 601a06, entrepreneurship building, Hunan University Science Park, No. 186, Guyuan Road, Changsha high tech Development Zone, Changsha, Hunan Province

Patentee after: Hunan heavy metal polluted cultivated land safe and efficient utilization Engineering Research Center Co.,Ltd.

Address before: Room 310-3, headquarters building, Changsha Zhongdian Software Park Co., Ltd., No. 39, Jianshan Road, Changsha hi tech Development Zone, Changsha, Hunan 410000

Patentee before: Hunan Huigu Agricultural Ecology Research Institute Co.,Ltd.

TR01 Transfer of patent right