SK277929B6 - Method of disposal of heavy metals in soil - Google Patents
Method of disposal of heavy metals in soil Download PDFInfo
- Publication number
- SK277929B6 SK277929B6 SK1590-91A SK159091A SK277929B6 SK 277929 B6 SK277929 B6 SK 277929B6 SK 159091 A SK159091 A SK 159091A SK 277929 B6 SK277929 B6 SK 277929B6
- Authority
- SK
- Slovakia
- Prior art keywords
- soil
- limestone
- heavy metals
- silicate
- potassium
- Prior art date
Links
Classifications
-
- A—HUMAN NECESSITIES
- A62—LIFE-SAVING; FIRE-FIGHTING
- A62D—CHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
- A62D3/00—Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances
- A62D3/30—Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by reacting with chemical agents
- A62D3/33—Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by reacting with chemical agents by chemical fixing the harmful substance, e.g. by chelation or complexation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
- B09C1/08—Reclamation of contaminated soil chemically
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05D—INORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C; FERTILISERS PRODUCING CARBON DIOXIDE
- C05D3/00—Calcareous fertilisers
- C05D3/02—Calcareous fertilisers from limestone, calcium carbonate, calcium hydrate, slaked lime, calcium oxide, waste calcium products
-
- A—HUMAN NECESSITIES
- A62—LIFE-SAVING; FIRE-FIGHTING
- A62D—CHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
- A62D2101/00—Harmful chemical substances made harmless, or less harmful, by effecting chemical change
- A62D2101/40—Inorganic substances
- A62D2101/43—Inorganic substances containing heavy metals, in the bonded or free state
Landscapes
- Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Health & Medical Sciences (AREA)
- General Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- General Health & Medical Sciences (AREA)
- Toxicology (AREA)
- Engineering & Computer Science (AREA)
- Soil Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Business, Economics & Management (AREA)
- Emergency Management (AREA)
- Inorganic Chemistry (AREA)
- Organic Chemistry (AREA)
- Processing Of Solid Wastes (AREA)
- Soil Conditioners And Soil-Stabilizing Materials (AREA)
- Manufacture And Refinement Of Metals (AREA)
Abstract
Description
Oblasť technikyTechnical field
Vynález sa týka spôsobu zneškodňovania ťažkých kovov v pôde.The invention relates to a process for the disposal of heavy metals in soil.
je možné zabrániť prenikaniu ťažkých kovov do potravinového reťazca.the penetration of heavy metals into the food chain can be prevented.
Doterajší stav technikyBACKGROUND OF THE INVENTION
Ťažké kovy v pôde, kam boli zanesené umelými hnojivami alebo spádom z atmosféry, sa ľahko adsorbujú spôsobom iónovej výmeny alebo formou komplexných väzieb. Napríklad pri príprave pitnej vody 1 kg uhličitanu vápenatého zachytí až stovky miligramov nebezpečných ťažkých kovov. Samotná pôda má určitú sorpčnú schopnosť viazať ťažké kovy, avšak pri ich hromadení sa znižujú výnosy. Zvyšovaním kyslosti pôdy sa ťažké kovy ľahko uvoľňujú a prenikajú potom do potravinového reťazca. Preto sa tiež robí alkalizácia pôdy jemne mletým vápencom, prípadne zmesou s páleným práškovitým vápnom. Práškovitý vápenec podľa rôznych lokalít obsahuje až 80 až 98,5 % čistého uhličitanu vápenatého. Pri dolomitickom vápenci je obsah vápnika nižší, ale naopak je prítomný pre pôdu tiež dôležitý horčík.Heavy metals in the soil, where they have been clogged with fertilizer or dropped from the atmosphere, are easily adsorbed by ion exchange or complex bonds. For example, when preparing drinking water, 1 kg of calcium carbonate captures hundreds of milligrams of dangerous heavy metals. Soil itself has a certain sorption capacity to bind heavy metals, but yields decrease as they accumulate. By increasing the acidity of the soil, heavy metals are easily released and then penetrate the food chain. Therefore, the soil is also alkalinized with finely ground limestone or a mixture of quicklime powdered lime. Powdered limestone according to various locations contains up to 80 to 98.5% pure calcium carbonate. For dolomitic limestone, the calcium content is lower, but magnesium is also present in the soil.
Nevýhodou tohto obvyklého postupu vápnenia pôdy je skutočnosť, že ťažké kovy, obzvlášť kadmium, sa sorpčnými pochodmi vápenca iba zachytávajú. Poklesom pH sa ťažké kovy v pôde opäť ľahko uvoľňujú.A disadvantage of this conventional liming process is that heavy metals, especially cadmium, are only trapped by the limestone sorption processes. By dropping the pH, heavy metals are easily released again in the soil.
Ďalej je známe pridávať do pôdy pri pestovaní ryže kremičitan vápenatý podľa japonského patentu č. 01,132,318/89,132,318/. Nevýhodou postupu podľa tohto patentu je vysoká dávka kremičitanu vápenatého, 200 kg na 10 árov, čo činí 2000 kg na 1 hektár. Toto množstvo je však súčasne viazané na fosforečné hnojivo s obsahom 500 kg fosforu na 1 ha.Furthermore, it is known to add calcium silicate to the soil in rice cultivation according to Japanese patent no. 01,132,318 / 89,132,318 /. A disadvantage of the process of this patent is the high dose of calcium silicate, 200 kg per 10 acres, which is 2000 kg per hectare. However, this quantity is also linked to a phosphorus fertilizer containing 500 kg of phosphorus per ha.
Podstata vynálezuSUMMARY OF THE INVENTION
Uvedené nevýhody odstraňuje spôsob zneškodňovania ťažkých kovov v pôde pomocou mletého vápenca, ktorý sa podľa vynálezu uskutočňuje tak, že sa vápenec primieša do pôdy v zmesi s aspoň jedným vodorozpustným alkalickým kremičitanom v hmotnostnom pomere od 100 : 1 do 100 : 5, výhodne ešte s prísadou 50 až 200 g oxidu vápenatého na 1 kg. Príslušný prostriedok sa vyrába primiešaním kremičitanu do vápenca pri mletí, výhodne ďalej s pridaním oxidu vápenatého.The above-mentioned disadvantages are eliminated by the method of neutralizing heavy metals in the soil by ground limestone, which according to the invention is carried out by admixing the limestone into the soil in a mixture with at least one water-soluble alkali silicate in a weight ratio of 100: 1 to 100: 5. 50 to 200 g of calcium oxide per kg. The composition is produced by admixing the silicate to the limestone during grinding, preferably further with the addition of calcium oxide.
Ako alkalický kremičitan podľa vynálezu je veľmi výhodné použiť kremičitan draselný, ktorý pri praktickom použití uvoľňuje do pôdy taký potrebný draslík. Vzniká tak zmes s obsahom kremičitanu vápenatého v prekvapivo aktívnej forme, zneškodňujúcej lepšie ťažké kovy.As the alkaline silicate according to the invention, it is very advantageous to use potassium silicate, which in practice releases the necessary potassium into the soil. This results in a mixture containing calcium silicate in a surprisingly active form which destroys better heavy metals.
Z toho vyplýva tiež nižší stupeň dávkovania účinných látok pri vápnení pôdy. Tak napríklad pri kyslosti pôdy pH 5,1 až 5,5 sa použije bežná dávka mletého vápenca 2,1 tony na 1 hektár, avšak iba s 20 kg alkalického kremičitanu, čo stači viazať kovy.This also results in a lower degree of dosing of the active compounds in liming the soil. For example, at a soil acidity of pH 5.1-5.5, a conventional dose of ground limestone of 2.1 tons per hectare is used, but with only 20 kg of alkali silicate, which is sufficient to bind the metals.
Význam použitia vodorozpustného alkalického kremičitanu v zmesi podľa vynálezu spočíva v tom, že kremičitanové anióny, ktoré vytvárajú nerozpustné kremičitany ťažkých kovov, sú vo vodorozpustnej iónovej forme. Tým vykazujú vysokú reaktivitu k ťažkým kovom. Prednostne prebiehajú potom reakcie katiónov ťažkých kovov s väčšou atómovou hmotnosťou. Prebiehajúce rekcie urýchľuje dostatočná vlhkosť pôdy. TaktoThe significance of the use of the water-soluble alkali silicate in the composition according to the invention is that the silicate anions which form insoluble heavy metal silicates are in water-soluble ionic form. As a result, they show a high reactivity to heavy metals. Preferably, the reactions of heavy metal cations of greater atomic mass then take place. Ongoing reactions accelerate sufficient soil moisture. thus
Príklady uskutočnenia vynálezuDETAILED DESCRIPTION OF THE INVENTION
1. Drvený vápenec sa pred mletím pokropí vodorozpustným kremičitanom draselným v tomto pomere: 1000 hmotn. dielov vápenca, 10 hmotn. dielov kremičitanu draselného (vodné sklo draselné) s hustotou 1300 - 1400 kg.m’3 a urobí sa mletie v guľovom alebo podobnom druhu mlyna. Po dosiahnutí potrebnej jemnosti sa použije na hnojenie.1. Crushed limestone is sprinkled with water-soluble potassium silicate in the following ratio before grinding: 1000 wt. parts by weight of limestone, 10 wt. parts of potassium silicate (potassium water glass) with a density of 1300 - 1400 kg.m- 3 and grinding in a spherical or similar kind of mill. After reaching the required fineness it is used for fertilization.
2. Drvený vápenec sa pokropí pred mletím vodorozpustným kremičitanom sodným v rovnakom pomere a postupom uvedenom v príklade 1.2. The crushed limestone is sprinkled with water-soluble sodium silicate in the same ratio and grinding as described in Example 1 before grinding.
3. Drvený vápenec sa pokropí pred mletím zmesou alkalického kremičitanu draselného a sodného v pomere 1 : 1 a zachová sa postup uvedený v príklade 1.3. Spray the crushed limestone before grinding with a 1: 1 mixture of alkaline potassium silicate and sodium, following the procedure of Example 1.
4. K jemne rozomletému vápencu sa primiesi práškovitý alkalický kremičitan draselný alebo sodný v pomere: 1000 hmotn. dielov jemne mletého vápenca, 6 hmotn. dielov práškovitého kremičitanu draselného alebo sodného, prípadne ich zmesi.4. Powdered alkaline potassium or sodium silicate is added to the finely ground limestone in a ratio of: 1000 wt. parts by weight of finely ground limestone, 6 wt. parts of powdered potassium or sodium silicate, or mixtures thereof.
5. K zmesi mletého vápenca s alkalickým vodorozpustným kremičitanom sa primiesi pálené práškovité vápno v celkovom pomere: 1000 hmotn. dielov jemne mletého vápenca s kremičitanom draselným alebo sodným podľa príkladu 1 a 2, 200 hmotn. dielov práškovitého páleného vápna.5. To the mixture of ground limestone with alkaline water-soluble silicate is added quicklime powder in a total ratio of: 1000 wt. parts by weight of finely ground limestone with potassium or sodium silicate according to Examples 1 and 2, 200 wt. parts of quicklime powder.
Všetky zmesi vápenca s kremičitanom draselným alebo sodným podľa príkladu 1 - 5, pripadne i s práškovitým páleným vápnom sú bez ďalšej úpravy pripravené na použitie. Množstvo pridávaného alkalického kremičitanu k mletému vápencu sa riadi stupňom znečistenia pôdy ťažkými kovmi. Zmes mletého vápenca s alkalickým kremičitanom vykazuje synergický účinok.All mixtures of limestone with potassium or sodium silicate according to Examples 1-5, optionally with quicklime powder, are ready for use without further treatment. The amount of alkali silicate added to the ground limestone is controlled by the degree of heavy metal soil contamination. The ground alkaline silicate mixture of limestone shows a synergistic effect.
Claims (4)
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CS911590A CZ278518B6 (en) | 1991-05-28 | 1991-05-28 | Method of liquidating heavy metals in the soil |
Publications (2)
Publication Number | Publication Date |
---|---|
SK159091A3 SK159091A3 (en) | 1994-07-06 |
SK277929B6 true SK277929B6 (en) | 1995-08-09 |
Family
ID=5350668
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
SK1590-91A SK277929B6 (en) | 1991-05-28 | 1991-05-28 | Method of disposal of heavy metals in soil |
Country Status (7)
Country | Link |
---|---|
EP (1) | EP0581854B1 (en) |
AT (1) | ATE130520T1 (en) |
AU (1) | AU1887692A (en) |
CZ (1) | CZ278518B6 (en) |
DE (1) | DE59204439D1 (en) |
SK (1) | SK277929B6 (en) |
WO (1) | WO1992021409A1 (en) |
Families Citing this family (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE69220673T2 (en) * | 1992-12-07 | 1998-02-12 | Blangy Gerard De | Process and plant for treating and recycling waste materials by changing them into recyclable, non-contaminated materials |
DE4312351A1 (en) * | 1993-04-16 | 1994-10-20 | Biolipsia Gmbh Fuer Biolog Che | Process for the decontamination of soils and building rubble contaminated with heavy metals and hydrocarbons |
EP0737490A1 (en) * | 1995-04-11 | 1996-10-16 | Hard Ag | Method for immobilization of heavy metals and elements |
EP0689858A1 (en) * | 1995-04-11 | 1996-01-03 | Hard Ag | Process and product of the immobilisation of heavy metals |
DE19547271A1 (en) * | 1995-12-19 | 1997-06-26 | Environ Ingenieurgesellschaft | Method for immobilising pollutants in soil, especially heavy metals |
FR2768932B1 (en) * | 1997-09-30 | 1999-11-12 | Rhodia Chimie Sa | HEAVY METAL ELIMINATOR COMPRISING A SILICATE OR ALUMINOSILICATE COMPOUND AND A CARBONATE COMPOUND AND IN THE FORM OF A SOLUTION |
FR2768933B1 (en) * | 1997-09-30 | 1999-11-12 | Rhodia Chimie Sa | HEAVY METAL REMOVAL AGENT COMPRISING A PHOSPHATE COMPOUND |
GB9908632D0 (en) * | 1999-04-15 | 1999-06-09 | Upperforce Limited | Treatment of polluted or contaminated substrates |
EP2762455A1 (en) * | 2013-01-31 | 2014-08-06 | Vekton d.o.o. | Waste treatment process by mineralization and execution of remediation in degraded areas and landscape works by producing and use of industrial composites and artificial soils from processed mineralized waste and scrap |
Family Cites Families (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CA965966A (en) * | 1970-01-08 | 1975-04-15 | Jesse R. Conner | Land improvement with waste materials |
JPS5386364A (en) * | 1976-12-28 | 1978-07-29 | Hirose Masayuki | Soil conditioning method |
JPS5618682A (en) * | 1979-07-24 | 1981-02-21 | Onoda Cement Co Ltd | Improvement of soil contaminated with heavy metal |
DE3517645A1 (en) * | 1985-01-23 | 1986-11-20 | Marx Bergbau GmbH & Co KG, 5431 Ruppach-Goldhausen | MEANS FOR THE MELIORATION OF DAMAGED SOILS AND / OR SUBSTANCES CONTAINING POLLUTANTS |
JPH01132318A (en) * | 1987-11-19 | 1989-05-24 | Mitsubishi Mining & Cement Co Ltd | Fertilizer application to suppress heavy metal absorption |
SU1583405A1 (en) * | 1988-04-05 | 1990-08-07 | Всесоюзный научно-исследовательский институт удобрений и агропочвоведения им.Д.Н.Прянишникова | Method of producing ameliorant-fertilizer of silicate-lime type |
-
1991
- 1991-05-28 SK SK1590-91A patent/SK277929B6/en unknown
- 1991-05-28 CZ CS911590A patent/CZ278518B6/en unknown
-
1992
- 1992-05-28 DE DE59204439T patent/DE59204439D1/en not_active Expired - Fee Related
- 1992-05-28 WO PCT/CS1992/000016 patent/WO1992021409A1/en active IP Right Grant
- 1992-05-28 AT AT92910735T patent/ATE130520T1/en not_active IP Right Cessation
- 1992-05-28 EP EP92910735A patent/EP0581854B1/en not_active Expired - Lifetime
- 1992-05-28 AU AU18876/92A patent/AU1887692A/en not_active Abandoned
Also Published As
Publication number | Publication date |
---|---|
DE59204439D1 (en) | 1996-01-04 |
CZ278518B6 (en) | 1994-02-16 |
EP0581854B1 (en) | 1995-11-22 |
CZ159091A3 (en) | 1993-11-17 |
SK159091A3 (en) | 1994-07-06 |
AU1887692A (en) | 1993-01-08 |
WO1992021409A1 (en) | 1992-12-10 |
ATE130520T1 (en) | 1995-12-15 |
EP0581854A1 (en) | 1994-02-09 |
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