CN111922027A - Stabilization and solidification method and application of inorganic fluoride landfill waste - Google Patents

Stabilization and solidification method and application of inorganic fluoride landfill waste Download PDF

Info

Publication number
CN111922027A
CN111922027A CN202010559961.1A CN202010559961A CN111922027A CN 111922027 A CN111922027 A CN 111922027A CN 202010559961 A CN202010559961 A CN 202010559961A CN 111922027 A CN111922027 A CN 111922027A
Authority
CN
China
Prior art keywords
landfill
mixture
hazardous waste
inorganic fluoride
waste
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
CN202010559961.1A
Other languages
Chinese (zh)
Inventor
叶树强
胡国良
章鹏兴
肖信锦
王艳萍
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.)
Ji'an Chuangcheng Environmental Protection Technology Co Ltd
Original Assignee
Ji'an Chuangcheng Environmental Protection Technology 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 Ji'an Chuangcheng Environmental Protection Technology Co Ltd filed Critical Ji'an Chuangcheng Environmental Protection Technology Co Ltd
Priority to CN202010559961.1A priority Critical patent/CN111922027A/en
Publication of CN111922027A publication Critical patent/CN111922027A/en
Pending legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • B09B3/20Agglomeration, binding or encapsulation of solid waste
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE
    • B09B1/00Dumping solid waste

Abstract

The invention relates to a stabilization and solidification method of inorganic fluoride landfill hazardous waste and application thereof, belonging to the field of stabilization and solidification of solid waste. The method for stabilizing and solidifying inorganic fluoride hazardous waste comprises the following steps: adding a calcium chloride solution into the hazardous waste after the crushing treatment; adding cement or hydrated lime, uniformly mixing and solidifying; adding phosphoric acid solution to adjust the pH value; and after maintenance, the materials meet the entrance standard of the landfill dangerous wastes, and then the materials can be put into the field for landfill treatment. The invention can be applied to the stabilization and solidification of inorganic fluoride hazardous waste, does not cause unqualified pH value due to excessive addition of the curing agent, and has the advantages of good solidification effect, high stability, wide application range and the like.

Description

Stabilization and solidification method and application of inorganic fluoride landfill waste
Technical Field
The invention relates to the field of solid waste stabilization and solidification, in particular to a stabilization and solidification method and application of inorganic fluoride landfill waste.
Background
In the process of producing and disposing industrial wastewater containing fluorine, a large amount of dangerous waste containing inorganic fluoride, such as fluorine-containing sludge and the like, is generated, and if the dangerous waste cannot be properly disposed, fluorine ions in the dangerous waste are diffused into drinking water to cause fluorosis, so that the dangerous waste can cause serious injury to teeth, bones, nervous systems and the like of a human body.
In the hazardous waste disposal industry, the landfill hazardous waste with high inorganic fluoride content is generally disposed in a mode of solidifying firstly and then burying. Adding a proper amount of cement or hydrated lime for curing in the first step, curing the cured hazardous waste in the second step, and performing landfill treatment, wherein the leaching toxicity index of the hazardous waste after curing meets the hazardous waste landfill pollution control standard (GB18598-2019), and the content of inorganic fluoride (without calcium fluoride) is less than 120 ppm.
The method has a certain curing effect when treating the hazardous waste with low content of inorganic fluoride (the concentration of leached toxic inorganic fluoride is less than 500mg/L and no calcium fluoride), but for the hazardous waste with higher content of inorganic fluoride (the concentration of leached toxic inorganic fluoride is 1000-15000mg/L and no calcium fluoride), cement or hydrated lime is used for curing, a large amount of strong alkaline cement and hydrated lime are required to be added, so that the cost of the medicament is increased, the pH value of a cured body exceeds the standard, the leaching resistance of the cured hazardous waste is poor, the leached toxicity index is unqualified, and the disposal effect of the hazardous waste is influenced.
Disclosure of Invention
The invention aims to overcome the defects of the prior art and provide a method for stabilizing and curing inorganic fluoride landfill hazardous wastes, which has good curing effect and high stability.
In order to achieve the purpose, the invention adopts the technical scheme that:
a method for stabilizing and solidifying inorganic fluoride landfill hazardous wastes comprises the following steps:
(1) adding a calcium chloride solution into the crushed hazardous waste to obtain a mixture A;
(2) adding a curing agent into the mixture A to obtain a mixture B;
(3) adding a phosphoric acid solution to the mixture B to obtain a mixture C.
Preferably, the stabilizing and curing method further comprises the step (4): and after maintaining all indexes of the mixture C to meet the standard of landfill dangerous waste entering, performing landfill treatment.
The stabilized solidification method is used for treating inorganic fluoride (the concentration of leached toxic inorganic fluoride is 1000-15000mg/L, and calcium fluoride is not contained) landfill hazardous waste, so that the use amount of cement and hydrated lime in the traditional method can be reduced, the pH value of a solidified body can be adjusted, the stability of the solidified body is enhanced, and the requirement of the hazardous waste on entering a landfill site can be met.
Preferably, the particle size of the crushed hazardous waste is less than or equal to 60 mm.
After being crushed, the hazardous waste can be fully contacted with calcium chloride, curing agent, phosphoric acid and other components, so that the replacement rate of fluorine ions is improved.
Preferably, the weight part of the calcium chloride in the mixture A is 5-100 parts.
The addition of calcium chloride can lead the free fluoride ions in the hazardous waste to form calcium fluoride precipitate with low solubility through chemical precipitation.
Preferably, the weight part of the curing agent in the mixture B is 10-100 parts.
Preferably, the curing agent is cement or hydrated lime.
And the residual fluorine ions are cured in a wrapping manner by using cement and hydrated lime, so that the effect of the curing method is improved.
Preferably, the weight part of the phosphoric acid solution in the mixture C is 1-30 parts.
Preferably, the phosphoric acid solution contains 5% by mass of phosphoric acid.
The phosphoric acid solution can adjust the pH value of the solidified body on the premise of not influencing the stabilizing and solidifying effect, thereby enhancing the stability of the solidified body and being beneficial to the future maintenance and landfill.
Compared with the prior art, the invention has the beneficial effects that: the particle size, the stabilizing and curing effect and the pH value of the hazardous waste are comprehensively considered, and the stabilizing and curing method for the inorganic fluoride landfill hazardous waste is comprehensively considered, so that the inorganic fluoride landfill hazardous waste has the advantages of good fluorine-fixing effect, high stability, wide application range, no unqualified pH value caused by excessive addition of the curing agent and the like. And the method has unique advantages in the aspect of treating high-content inorganic fluoride landfill hazardous wastes, not only reduces the consumption of cement or hydrated lime and saves the production cost, but also ensures that the landfill body after the stabilization and solidification has better leaching resistance.
Detailed Description
In order to better illustrate the objects, technical solutions and advantages of the present invention, the present invention will be further described below by referring to examples.
Example 1:
a method for stabilizing and solidifying inorganic fluoride landfill hazardous wastes comprises the following steps:
(1) adding 5 parts by weight of a calcium chloride solution to the crushed hazardous waste to obtain a mixture A;
(2) adding 10 parts by weight of cement to the mixture A to obtain a mixture B;
(3) to the mixture B, 1 part by weight of a 5% phosphoric acid solution was added to obtain a mixture C.
(4) And after maintaining all indexes of the mixture C to meet the standard of landfill dangerous waste entering, performing landfill treatment.
Example 2:
a method for stabilizing and solidifying inorganic fluoride landfill hazardous wastes comprises the following steps:
(1) adding 10 parts by weight of a calcium chloride solution to the crushed hazardous waste to obtain a mixture A;
(2) adding 20 parts by weight of cement to the mixture A to obtain a mixture B;
(3) to the mixture B, 1 part by weight of a 5% phosphoric acid solution was added to obtain a mixture C.
(4) And after maintaining all indexes of the mixture C to meet the standard of landfill dangerous waste entering, performing landfill treatment.
Example 3:
a method for stabilizing and solidifying inorganic fluoride landfill hazardous wastes comprises the following steps:
(1) adding 60 parts by weight of a calcium chloride solution to the crushed hazardous waste to obtain a mixture A;
(2) adding 50 parts by weight of cement to the mixture A to obtain a mixture B;
(3) to the mixture B was added 12.5 parts by weight of a phosphoric acid solution to obtain a mixture C.
(4) And after maintaining all indexes of the mixture C to meet the standard of landfill dangerous waste entering, performing landfill treatment.
Example 4:
a method for stabilizing and solidifying inorganic fluoride landfill hazardous wastes comprises the following steps:
(1) adding 100 parts by weight of a calcium chloride solution to the crushed hazardous waste to obtain a mixture A;
(2) adding 100 parts by weight of cement to the mixture A to obtain a mixture B;
(3) to the mixture B was added 30 parts by weight of a 5% phosphoric acid solution to obtain a mixture C.
(4) And after maintaining all indexes of the mixture C to meet the standard of landfill dangerous waste entering, performing landfill treatment.
Effect example 1:
the sludge collected and transported by a certain client, the concentration of leached toxic inorganic fluoride (without calcium fluoride) is 326.2mg/L, the pH value is 10.3, the traditional method and the method of example 1 are respectively adopted for treatment, and the results are shown in the table 1:
table 1 waste solidification treatment results
Figure BDA0002545928970000041
Effect example 2:
the filter residue obtained by washing the filter residue collected and transported by a certain client is leached out, the concentration of toxic inorganic fluoride (without calcium fluoride) is 882mg/L, the pH value is 7.5, the traditional method and the method of example 2 are adopted for respectively processing, and the results are shown in the following table 2:
table 2 results of waste solidification treatment
Figure BDA0002545928970000042
Effect example 3:
the sludge from the wastewater treatment collected and transported by a certain client was treated by a conventional method and the method of example 3, respectively, at a leached toxic inorganic fluoride (calcium fluoride-free) concentration of 13235mg/L and a pH of 7.8, and the results are shown in Table 3:
TABLE 3 waste solidification treatment results
Figure BDA0002545928970000051
From the above examples and effect examples, it can be seen that the stabilization and solidification method for inorganic fluoride landfill hazardous waste has better effect in treating hazardous waste with different contents of inorganic fluoride (the concentration of leached toxic inorganic fluoride is 1000-15000mg/L, and no calcium fluoride), compared with the traditional method, the leached toxicity after treatment is obviously reduced, the pH value is stable, and the landfill hazardous waste is compounded to the standard of entering the field.
Although the present invention has been described in detail with reference to the preferred embodiments, it will be understood by those skilled in the art that various changes may be made and equivalents may be substituted for elements thereof without departing from the true spirit and scope of the present invention.

Claims (9)

1. A method for stabilizing and solidifying inorganic fluoride landfill waste is characterized by comprising the following steps:
(1) adding calcium chloride and water into the crushed hazardous waste to obtain a mixture A;
(2) adding a curing agent into the mixture A to obtain a mixture B;
(3) adding a phosphoric acid solution to the mixture B to obtain a mixture C.
2. The stabilized curing method according to claim 1, further comprising the step (4): and after maintaining all indexes of the mixture C to meet the standard of landfill dangerous waste entering, performing landfill treatment.
3. The stabilized solidification method of claim 1 wherein the particle size of the crushed hazardous waste is 60mm or less.
4. The stabilized curing method according to claim 1, wherein the amount of calcium chloride in the mixture A is 5 to 100 parts by weight.
5. The stabilized curing method according to claim 1, wherein the amount of the curing agent in the mixture B is 10 to 100 parts by weight.
6. The stabilized curing method of claim 5, wherein the curing agent is cement or hydrated lime.
7. The stabilized curing method according to claim 1, wherein the weight part of the phosphoric acid solution in the mixture C is 1 to 30 parts; the mass percentage of phosphoric acid in the phosphoric acid solution is 5%.
8. Use of the method for stabilizing and solidifying inorganic fluoride landfill hazardous waste according to any one of claims 1 to 7 in solidifying inorganic fluoride landfill hazardous waste.
9. The inorganic fluoride landfill hazardous waste of claim 8, wherein the inorganic fluoride landfill hazardous waste does not contain calcium fluoride.
CN202010559961.1A 2020-06-18 2020-06-18 Stabilization and solidification method and application of inorganic fluoride landfill waste Pending CN111922027A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202010559961.1A CN111922027A (en) 2020-06-18 2020-06-18 Stabilization and solidification method and application of inorganic fluoride landfill waste

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202010559961.1A CN111922027A (en) 2020-06-18 2020-06-18 Stabilization and solidification method and application of inorganic fluoride landfill waste

Publications (1)

Publication Number Publication Date
CN111922027A true CN111922027A (en) 2020-11-13

Family

ID=73317855

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202010559961.1A Pending CN111922027A (en) 2020-06-18 2020-06-18 Stabilization and solidification method and application of inorganic fluoride landfill waste

Country Status (1)

Country Link
CN (1) CN111922027A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112742844A (en) * 2020-12-14 2021-05-04 孙刚 Aluminum electrolytic cell overhaul waste residue stabilization solidified body and preparation method thereof
CN115382879A (en) * 2022-09-30 2022-11-25 贵州星河环境技术有限公司 Method and equipment for innocent treatment of overhaul residues and fly ash

Citations (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002370093A (en) * 2001-01-26 2002-12-24 Shimonoseki Mitsui Chemicals Inc High-degree treatment method for fluorine compound- containing liquid
JP2003206133A (en) * 2002-01-15 2003-07-22 Shimonoseki Mitsui Chemicals Inc Gypsum wherein eluted fluorine is reduced
JP2004025136A (en) * 2002-06-28 2004-01-29 Shimonoseki Mitsui Chemicals Inc Advanced fluorine treatment equipment
US20040024281A1 (en) * 2002-08-05 2004-02-05 Forrester Keith Edward Method for stabilization of material or waste to reduce metals and fluoride leaching potential
JP2004243192A (en) * 2003-02-13 2004-09-02 Hitachi Constr Mach Co Ltd Method and system for treating contaminated soil and contaminated soil treatment machine
JP2004305833A (en) * 2003-04-03 2004-11-04 Kawasaki Heavy Ind Ltd Method for stabilization treatment of waste
JP2008086911A (en) * 2006-10-02 2008-04-17 Kurita Water Ind Ltd Civil engineering material and its manufacturing method
JP2010207755A (en) * 2009-03-11 2010-09-24 Japan Organo Co Ltd Apparatus for treating fluorine-containing water
CN104870060A (en) * 2012-12-21 2015-08-26 力拓加铝国际有限公司 Process for reducing of leachable fluorides and controlling pH of aluminum waste products
CN105130346A (en) * 2015-09-15 2015-12-09 韩素梅 Safety treatment method for fluorine-containing solid waste
JP2019181329A (en) * 2018-04-03 2019-10-24 住友金属鉱山株式会社 Method for removing fluorine
CN110526493A (en) * 2019-08-06 2019-12-03 南京大学 A kind of combined treatment process and equipment of fluoride waste

Patent Citations (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002370093A (en) * 2001-01-26 2002-12-24 Shimonoseki Mitsui Chemicals Inc High-degree treatment method for fluorine compound- containing liquid
JP2003206133A (en) * 2002-01-15 2003-07-22 Shimonoseki Mitsui Chemicals Inc Gypsum wherein eluted fluorine is reduced
JP2004025136A (en) * 2002-06-28 2004-01-29 Shimonoseki Mitsui Chemicals Inc Advanced fluorine treatment equipment
US20040024281A1 (en) * 2002-08-05 2004-02-05 Forrester Keith Edward Method for stabilization of material or waste to reduce metals and fluoride leaching potential
JP2004243192A (en) * 2003-02-13 2004-09-02 Hitachi Constr Mach Co Ltd Method and system for treating contaminated soil and contaminated soil treatment machine
JP2004305833A (en) * 2003-04-03 2004-11-04 Kawasaki Heavy Ind Ltd Method for stabilization treatment of waste
JP2008086911A (en) * 2006-10-02 2008-04-17 Kurita Water Ind Ltd Civil engineering material and its manufacturing method
JP2010207755A (en) * 2009-03-11 2010-09-24 Japan Organo Co Ltd Apparatus for treating fluorine-containing water
CN104870060A (en) * 2012-12-21 2015-08-26 力拓加铝国际有限公司 Process for reducing of leachable fluorides and controlling pH of aluminum waste products
CN105130346A (en) * 2015-09-15 2015-12-09 韩素梅 Safety treatment method for fluorine-containing solid waste
JP2019181329A (en) * 2018-04-03 2019-10-24 住友金属鉱山株式会社 Method for removing fluorine
CN110526493A (en) * 2019-08-06 2019-12-03 南京大学 A kind of combined treatment process and equipment of fluoride waste

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112742844A (en) * 2020-12-14 2021-05-04 孙刚 Aluminum electrolytic cell overhaul waste residue stabilization solidified body and preparation method thereof
CN115382879A (en) * 2022-09-30 2022-11-25 贵州星河环境技术有限公司 Method and equipment for innocent treatment of overhaul residues and fly ash
CN115382879B (en) * 2022-09-30 2024-02-06 贵州星河环境技术有限公司 Harmless treatment method and equipment for overhaul slag and fly ash

Similar Documents

Publication Publication Date Title
US4671882A (en) Phosphoric acid/lime hazardous waste detoxification treatment process
US4698163A (en) Treatment of phosphate-containing wastewater
US4377508A (en) Process for removal of radioactive materials from aqueous solutions
CN111922027A (en) Stabilization and solidification method and application of inorganic fluoride landfill waste
CN104098237A (en) Sludge or soil treatment method and heavy metal component stabilizing agent
CN104974762A (en) Preparation of curing stabilizing agent for treating heavy metal-polluted soil and use method thereof
CN104056854A (en) United stable mineralizing repairing agent for treating soil with combined pollution of Pb, As, Cu, and Cd and application method of repairing agent
CN102381778B (en) Method for harmless treatment of drilling well waste mud
CN110683674A (en) Treatment method for synchronously removing fluorine and silicon compounds in wastewater
CN111573901A (en) Method for treating fluorine-containing wastewater
CN104478055A (en) Sewage treatment complexing agent as well as preparation method and application method thereof
CA1244152A (en) Phosphoric acid/lime hazardous waste detoxification treatment process
CN105731691A (en) Coupled stabilizing treatment method for acid wastewater and incineration ash
CN105293659B (en) A kind of emergent stabilization treatment method of the deposit of Heavy Metals in Waters pollutant
JP4338705B2 (en) Method for treating waste liquid containing borofluoride ions
CN109502826A (en) A kind of processing method of fluoride waste
CN105692831A (en) Efficient slag-based inorganic phosphorous removal flocculating agent and preparation method thereof
CN111875339B (en) Curing agent for high-pH solid waste and treatment method
CN109368753A (en) A kind of preparation method of compound frerrous chloride flocculant
KR101908090B1 (en) Method for producing inorganic flocculant for water treatment for fluorine removal
KR102116420B1 (en) Waste water treatment method of removing fluorine and cyanides
KR102567638B1 (en) Water treatment method to reduce residual aluminum
CN113003769B (en) Closed cycle treatment method for soil leaching waste liquid
JPH03186393A (en) Treatment of waste water containing fluorine
CN110404227B (en) Reduction curing stabilization method for arsenic sulfide slag

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
RJ01 Rejection of invention patent application after publication

Application publication date: 20201113