WO2013055242A2 - Method of utilization of asbestos and/or asbestos-containing products - Google Patents

Method of utilization of asbestos and/or asbestos-containing products Download PDF

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Publication number
WO2013055242A2
WO2013055242A2 PCT/PL2012/000060 PL2012000060W WO2013055242A2 WO 2013055242 A2 WO2013055242 A2 WO 2013055242A2 PL 2012000060 W PL2012000060 W PL 2012000060W WO 2013055242 A2 WO2013055242 A2 WO 2013055242A2
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WO
WIPO (PCT)
Prior art keywords
asbestos
mixture
amount
materials
products containing
Prior art date
Application number
PCT/PL2012/000060
Other languages
French (fr)
Other versions
WO2013055242A4 (en
WO2013055242A3 (en
Inventor
Maciej PAWLIKOWSKI
Łukasz WDOWCZYK
Andrzej PIETRASZ
Władysław KAMUSIŃSKI
Original Assignee
Pawlikowski Maciej
Wdowczyk Lukasz
Pietrasz Andrzej
Kamusinski Wladyslaw
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
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Application filed by Pawlikowski Maciej, Wdowczyk Lukasz, Pietrasz Andrzej, Kamusinski Wladyslaw filed Critical Pawlikowski Maciej
Publication of WO2013055242A2 publication Critical patent/WO2013055242A2/en
Publication of WO2013055242A3 publication Critical patent/WO2013055242A3/en
Publication of WO2013055242A4 publication Critical patent/WO2013055242A4/en

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Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • B09B3/0066Disposal of asbestos
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • B09B3/40Destroying solid waste or transforming solid waste into something useful or harmless involving thermal treatment, e.g. evaporation

Definitions

  • This invention relates to utilization of asbestos and/or asbestos-containing products, particularly asbestos-cement (eternit) panels, plates and pipes.
  • asbestos Because of its properties, particularly thermal insulation and substantial resistance to chemical agents, abrasion and high temperatures, asbestos has been widely used in industry, including the manufacture of fire-resistant fabrics and paints, brake linings, and production of eternit, which was used in manufacturing of non-flammable building materials (wall and roofing panels and plates, and pipes).
  • Polish patent PL188640 Known method of utilization of asbestos-cement waste, disclosed in the Polish patent PL188640, consists of crushing them to the appropriate fractions and packing into dustproof bags, which are then placed in the underground mine voids or cavities and flooded with a mixture of ash and water.
  • Another method disclosed in the Polish patent PL 197566 consists of shredding the asbestos-cement elements removed from constructions to particles no larger than 10 cm 3 , which are then neutralized with water in a sealed mechanical device, and used as material for road construction.
  • Polish patent PL201476 Another method of utilization of asbestos waste is known from the Polish patent PL201476 and it consists in placing the debris in a concrete silo specially built for this purpose.
  • Polish patent application PL359958 discloses a method of waste-free utilization of asbestos products and asbestos-containing waste, consisting of chemical etching of these materials with phosphoric acid, the process is carried out either in one-stage or two-stage procedure in strongly acidic conditions.
  • a method known from the Polish patent application PL369748 of utilization of asbestos or asbestos-containing products consists in that such products with addition of cement or portlandite are subjected to temperature and pressure for certain period of time, resulting in that hazardous to health asbestos fibrous structure disappears and new crystalline substance is created.
  • polish patent PL209165 discloses a method of utilization of asbestos- containing materials consisting of heating of these materials and conversion of fibrous, crystalline structure into fiber-free structure under the influence of electromagnetic field, which is characterized in that the asbestos-containing material is ground, then transported to the microwave reactor, and during grinding and/or transportation this material is mixed with a heating adjuvant, and resulting product of the heat treatment is then removed from the reactor, cooled and subjected to final grinding process. Examination of the products obtained by this method showed continued presence of small amounts of asbestos.
  • the methods of the asbestos utilization known in the state of the art do not lead, however, to complete elimination of asbestos fibers, and the asbestos itself remains only temporarily immobilized, but it retains carcinogenic properties.
  • the aim of the present invention is to provide a method of complete utilization of asbestos waste in a process of complete recrystallization of asbestos to other forms, i.e. conversion of existing crystalline fibrous phases into different crystalline phases free of asbestos, resulting in a product entirely free of asbestos fibers, and thus devoid of properties harmful for human body.
  • the method of utilization of asbestos and/or products containing asbestos, in particular of asbestos-cement products like panels, plates and pipes, according to the invention is characterized in that the asbestos and/or asbestos-containing products and the supplementary materials that decrease the melting temperature of the mixture are subjected to a process of grinding in a hermetically sealed crusher, to the initial fragmentation and then subjected to grinding in a ball mill until the grain sizes in the mixture fall within the range from 10 microns to 500 microns.
  • Powdered bulk material thus obtained is introduced into the tunnel or rotary kiln and subjected to a temperature, and in the first embodiment of the invention the loose material is batched to at least one flat container in a layer of real thickness not bigger than 20 cm, then the container/containers so filled up with a layer of bulk material is placed in a tunnel kiln and subjected to a temperature gradually in the range from 1000 °C to 1500 °C, for 15 to 45 minutes.
  • loose mixture of any thickness is introduced into the rotary kiln by continuous filling of powdered material and subjected to a temperature gradually in the range from 1000 °C to 1500 °C, for 15 to 45 minutes.
  • the resulting final bulk material can be further subjected to a process of cooling and drying, preferably at ambient temperature.
  • the materials from the coal dump are used, in the range from 10 to 50 wt% (weight percent) relative to the amount of the basic component in the form of asbestos and/or products containing asbestos.
  • the materials from the coal dump contain typically from 3 to 15 wt% of coal and grains of quartz, muscovite, potassium feldspar, and others.
  • the feldspar fluxes are used, especially granite, which contains potassium feldspar.
  • the fluxes are added in an amount exceeding 5 wt% relative to the amount of the basic component in the form of asbestos and/or products containing asbestos.
  • the phosphorus-containing hazardous waste of animal or human origin is used, especially bones-containing waste from hospitals or slaughterhouses. In the first variant this waste is introduced in an amount of up to 60 wt% relative to the amount of the basic component in the form of asbestos and/or products containing asbestos.
  • the waste is mixed with the debris from the coal dump, containing from 3 to 15 wt% coal, and grains of quartz, muscovite, potassium feldspar, and others, where the materials of the dump are added in an amount of from 10 to 50 wt% relative to the basic component in the form of asbestos and/or products containing asbestos, while the hazardous waste is added in an amount of up to 20% compared to the mixture of materials from the coal dump and asbestos and/or products containing asbestos.
  • this waste is added along with the feldspar fluxes, and both waste and fluxes are added in the amounts each exceeding 5 wt% relative to the amount of the basic component in the form of asbestos and/or products containing asbestos.
  • the above mentioned additives to the basic material which is asbestos and/or asbestos-containing products, decrease the melting temperature of the mixture of components, and thus reduce the cost of the invented method, and allow for use of easily available kilns.
  • the main advantage of utilization of asbestos and/or asbestos-containing products, particularly asbestos-cement plates and pipes, according to the invention is a possibility to obtain the final material, which is completely devoid of asbestos fibers extremely harmful to health and environment, and in consequence to obtain a safe material, which would not make any threat to humans and environment.
  • the material obtained in the method according to the invention may be subjected to further modification in order to obtain products of commercial value that can be used in various sectors of economy, particularly in building industry, e.g. in manufacture of concrete elements, materials for road foundation, etc.
  • the advantage of the method according to the invention is a relatively simple technology based on thermal method, and selection of appropriate additives.
  • the method according to the invention can be implemented without necessity to use more advanced treatments, such as application of pressure or special chemicals or microwave, and does not require specially constructed devices to use this method, making it possible to use well-known devices such as kilns, crushers and mixers.
  • An important advantage of invented method is also a possibility of simultaneous utilization of phosphorus-containing hazardous waste of animal or human origin, especially containing bones waste from hospital or slaughterhouse.
  • the ash which was created after combustion at high temperature of hazardous waste containing phosphorus from the bones, during rotation of the kiln was mixed with powdered eternit and milled material from the dump, and contributed to lowering the temperature of destruction of the asbestos fibers.

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  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Physics & Mathematics (AREA)
  • Thermal Sciences (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The subject of claimed invention is a method of utilization of asbestos and/or products containing asbestos, in particular of asbestos-cement products like panels, plates and pipes, comprising the stages of shredding and thermal treatment, characterized in that initially shredded asbestos and/or products containing asbestos, and the supplementary materials that decrease the melting temperature of the mixture are subjected to a process of grinding until the grain sizes in the mixture fall within the range from 10 microns to 500 microns, then obtained loose material with mentioned additives is introduced into the tunnel or rotary kiln and subjected to a temperature gradually in the range from 1000 °C to 1500 °C, for 15 to 45 minutes. The main advantage of the method according to the invention is that it leads to final material, which is completely devoid of asbestos fibers and in consequence it is safe material that would not make any threat to humans health, and which may be subjected to further modification in order to obtain products of commercial value that can be used in various sectors of economy, particularly in building industry, e.g. in manufacture of concrete elements, materials for road foundation, etc.

Description

Method of utilization of asbestos and/or asbestos-containing products
This invention relates to utilization of asbestos and/or asbestos-containing products, particularly asbestos-cement (eternit) panels, plates and pipes.
Because of its properties, particularly thermal insulation and substantial resistance to chemical agents, abrasion and high temperatures, asbestos has been widely used in industry, including the manufacture of fire-resistant fabrics and paints, brake linings, and production of eternit, which was used in manufacturing of non-flammable building materials (wall and roofing panels and plates, and pipes).
However, studies have shown harmful effects of asbestos on human body. Inhalation of asbestos fibers with microscopic sizes (20-50 microns) can lead to serious lung diseases - asbestosis. It is often followed by a complication of bronchial cancer and pleural mesothelioma. Harmfulness of asbestos fibers depends on their diameter and length. Larger fibers are not so harmful, because they are deposited mostly in the upper respiratory tract where they are removed by the cilia, while the very fine fibers are removed by the immune system. The most dangerous are the fibers of a length greater than 5 microns, but thin up to 0.01 microns, absorbed into the lower respiratory tract, which stick to the lungs where they remain, and as a result of long-term irritation of the cells cause cancers.
Because of confirmed high harmfulness of asbestos, its production and use is now prohibited. Therefore, there was also a need to seek solutions for safe removal and utilization of asbestos-containing products, particularly asbestos-cement plates. After disintegration of eternit plates the problem still persists in remaining asbestos fibers that do not undergo complete neutralization.
Known method of utilization of asbestos-cement waste, disclosed in the Polish patent PL188640, consists of crushing them to the appropriate fractions and packing into dustproof bags, which are then placed in the underground mine voids or cavities and flooded with a mixture of ash and water. Another method disclosed in the Polish patent PL 197566 consists of shredding the asbestos-cement elements removed from constructions to particles no larger than 10 cm3, which are then neutralized with water in a sealed mechanical device, and used as material for road construction.
Another method of utilization of asbestos waste is known from the Polish patent PL201476 and it consists in placing the debris in a concrete silo specially built for this purpose. Polish patent application PL359958 discloses a method of waste-free utilization of asbestos products and asbestos-containing waste, consisting of chemical etching of these materials with phosphoric acid, the process is carried out either in one-stage or two-stage procedure in strongly acidic conditions.
A method known from the Polish patent application PL369748 of utilization of asbestos or asbestos-containing products consists in that such products with addition of cement or portlandite are subjected to temperature and pressure for certain period of time, resulting in that hazardous to health asbestos fibrous structure disappears and new crystalline substance is created.
There are also known technologies of thermal neutralization of asbestos, such as technology MTT (Microwave Thermal Treatment) disclosed by C. Leonelli, P. Veronesi, D.N. Boccaccini, M.R. Rivasi, L. Barbieri, F. Andreola, I. Lancellotti, D. Rabitti and G.C. Pellacani, in "Microwave thermal inertisation of asbestos-containing waste and its recycling in traditional ceramics" (Journal of Hazardous Materials, Volume 135, Issues 1- 3, 31 July 2006, Pages 149-155). This paper deals with destruction of asbestos fibers with use of microwaves. Fiber modification technology itself is however different from the one proposed in claimed invention.
Besides, the Polish patent PL209165 discloses a method of utilization of asbestos- containing materials consisting of heating of these materials and conversion of fibrous, crystalline structure into fiber-free structure under the influence of electromagnetic field, which is characterized in that the asbestos-containing material is ground, then transported to the microwave reactor, and during grinding and/or transportation this material is mixed with a heating adjuvant, and resulting product of the heat treatment is then removed from the reactor, cooled and subjected to final grinding process. Examination of the products obtained by this method showed continued presence of small amounts of asbestos.
The methods of the asbestos utilization known in the state of the art do not lead, however, to complete elimination of asbestos fibers, and the asbestos itself remains only temporarily immobilized, but it retains carcinogenic properties. The aim of the present invention is to provide a method of complete utilization of asbestos waste in a process of complete recrystallization of asbestos to other forms, i.e. conversion of existing crystalline fibrous phases into different crystalline phases free of asbestos, resulting in a product entirely free of asbestos fibers, and thus devoid of properties harmful for human body.
The method of utilization of asbestos and/or products containing asbestos, in particular of asbestos-cement products like panels, plates and pipes, according to the invention is characterized in that the asbestos and/or asbestos-containing products and the supplementary materials that decrease the melting temperature of the mixture are subjected to a process of grinding in a hermetically sealed crusher, to the initial fragmentation and then subjected to grinding in a ball mill until the grain sizes in the mixture fall within the range from 10 microns to 500 microns.
Powdered bulk material thus obtained is introduced into the tunnel or rotary kiln and subjected to a temperature, and in the first embodiment of the invention the loose material is batched to at least one flat container in a layer of real thickness not bigger than 20 cm, then the container/containers so filled up with a layer of bulk material is placed in a tunnel kiln and subjected to a temperature gradually in the range from 1000 °C to 1500 °C, for 15 to 45 minutes.
In second embodiment of the invention loose mixture of any thickness is introduced into the rotary kiln by continuous filling of powdered material and subjected to a temperature gradually in the range from 1000 °C to 1500 °C, for 15 to 45 minutes.
In both cases the resulting final bulk material can be further subjected to a process of cooling and drying, preferably at ambient temperature.
Preferably, as the additives - the supplementary materials that decrease the melting temperature of the mixture of ingredients - the materials from the coal dump are used, in the range from 10 to 50 wt% (weight percent) relative to the amount of the basic component in the form of asbestos and/or products containing asbestos. The materials from the coal dump contain typically from 3 to 15 wt% of coal and grains of quartz, muscovite, potassium feldspar, and others.
Preferably, as the materials decreasing the melting temperature of the mixture the feldspar fluxes are used, especially granite, which contains potassium feldspar. The fluxes are added in an amount exceeding 5 wt% relative to the amount of the basic component in the form of asbestos and/or products containing asbestos. Preferably, as the materials decreasing the melting temperature of the mixture the phosphorus-containing hazardous waste of animal or human origin is used, especially bones-containing waste from hospitals or slaughterhouses. In the first variant this waste is introduced in an amount of up to 60 wt% relative to the amount of the basic component in the form of asbestos and/or products containing asbestos. In the second variant, the waste is mixed with the debris from the coal dump, containing from 3 to 15 wt% coal, and grains of quartz, muscovite, potassium feldspar, and others, where the materials of the dump are added in an amount of from 10 to 50 wt% relative to the basic component in the form of asbestos and/or products containing asbestos, while the hazardous waste is added in an amount of up to 20% compared to the mixture of materials from the coal dump and asbestos and/or products containing asbestos. In the third variant this waste is added along with the feldspar fluxes, and both waste and fluxes are added in the amounts each exceeding 5 wt% relative to the amount of the basic component in the form of asbestos and/or products containing asbestos.
The above mentioned additives to the basic material, which is asbestos and/or asbestos-containing products, decrease the melting temperature of the mixture of components, and thus reduce the cost of the invented method, and allow for use of easily available kilns.
The main advantage of utilization of asbestos and/or asbestos-containing products, particularly asbestos-cement plates and pipes, according to the invention is a possibility to obtain the final material, which is completely devoid of asbestos fibers extremely harmful to health and environment, and in consequence to obtain a safe material, which would not make any threat to humans and environment.
The material obtained in the method according to the invention may be subjected to further modification in order to obtain products of commercial value that can be used in various sectors of economy, particularly in building industry, e.g. in manufacture of concrete elements, materials for road foundation, etc.
Moreover, the advantage of the method according to the invention is a relatively simple technology based on thermal method, and selection of appropriate additives.
The method according to the invention can be implemented without necessity to use more advanced treatments, such as application of pressure or special chemicals or microwave, and does not require specially constructed devices to use this method, making it possible to use well-known devices such as kilns, crushers and mixers. An important advantage of invented method is also a possibility of simultaneous utilization of phosphorus-containing hazardous waste of animal or human origin, especially containing bones waste from hospital or slaughterhouse.
The method of utilization of asbestos and/or asbestos-containing products, particularly asbestos-cement plates and pipes, according to the invention is presented below in the examples.
Example 1
1000 kg of eternit panels were broken up initially by the crusher to pieces of size up to 5 cm, then the crushed material and 150 kg of feldspar granite were placed in a hermetically sealed crusher and then subjected to grinding in a ball mill until the grain size of received powder was of about 100 microns. Obtained mixture was poured into the flat tin forms, creating in them the powder layer with thickness of about 10 cm, which then was placed in a tunnel kiln. The mixture was kept in the kiln for 25 minutes at 1400 °C.
The process of recrystallization executed in this temperature resulted in that the asbestos fibers completely disappeared and were converted into calcium silicate resembling brown sand. The resulting loose material was then transferred into metal containers where was cooled in ambient temperature. After cooling, secure final product, free from asbestos fibers may be used in many ways.
Example 2
1000 kg of eternit pipes were broken up initially by the crusher to pieces of size up to 5 cm, then the crushed material and 350 kg of milled raw material taken from the coal dump containing up to 15 wt% of coal and grains of quartz, muscovite, potassium feldspar, and others, were placed in hermetically sealed crusher and then subjected to grinding in a ball mill until the grain size of received powder was of about 100 microns. The resulting mixture was poured continuously into the rotary kiln, where the mixture was heated for 30 minutes in a temperature of 1400 °C.
The process of recrystallization resulted in complete convertion of asbestos fibers into harmless calcium silicate resembling brown sand. The resulting loose material was then transferred into metal containers where it was cooled in ambient temperature. After cooling, secure final product, free from asbestos fibers may be used in many ways.
Example 3
1000 kg of eternit panels were broken up initially in the crusher to pieces of size up to 5 cm, then the crushed material and 200 kg of milled raw material from the coal dump, containing up to 15 wt% of coal and grains of quartz, muscovite, potassium feldspar, and others, were placed in hermetically closed crusher and then subjected to grinding in a ball mill until the grain size of received powder was of about 100 microns. The resulting mixture was poured continuously into the rotary kiln with added 100 kg of containing phosphorus, hazardous bone waste from slaughterhouse. A mixture of all components were kept in the kiln for 35 minutes in a temperature of 1350 °C. The ash, which was created after combustion at high temperature of hazardous waste containing phosphorus from the bones, during rotation of the kiln was mixed with powdered eternit and milled material from the dump, and contributed to lowering the temperature of destruction of the asbestos fibers.
As a result of proposed treatment of the material described above, the asbestos fibers have disappeared, converted to harmless silicates and phosphates resembling brown sand. After cooling, diverse use of secure, free from asbestos fibers final product is possible.

Claims

Claims
1. A method of utilization of asbestos and/or products containing asbestos, in particular of asbestos-cement products like panels, plates and pipes, comprising the stages of shredding and thermal treatment, characterized in that initially shredded asbestos and/or products containing asbestos, and the supplementary materials that decrease the melting temperature of the mixture are subjected to a process of grinding until the grain sizes in the mixture fall within the range from 10 microns to 500 microns, then obtained loose material is introduced into the tunnel or rotary kiln and subjected to a temperature gradually in the range from 1000 °C to 1500 °C, for 15 to 45 minutes, and in case of use of the tunnel kiln the loose material is batched to at least one flat container in a layer of real thickness not bigger than 20 cm, then the container/containers so filled up with a layer of bulk material is placed in a tunnel kiln, while in case of use of the rotary kiln the loose material of any thickness is introduced directly into the rotary kiln.
2. The method according to claim 1, characterized in that the supplementary materials that decrease the melting temperature of the mixture are the materials from the coal dump, taken in a range from 10 to 50 wt% relative to the amount of the basic component in the form of asbestos and/or products containing asbestos, while the materials from the coal dump contain from 3 to 15 wt% of coal and grains of quartz, muscovite, potassium feldspar, and others.
3. The method according to claim 1 , characterized in that the supplementary materials that decrease the melting temperature of the mixture are the feldspar fluxes, in an amount exceeding 5 wt% relative to the amount of the basic component in the form of asbestos and/or products containing asbestos.
4. The method according to claim 1, characterized in that the granites, which contain potassium feldspar, are taken as the feldspar fluxes.
5. The method according to claim 1 , characterized in that the supplementary materials that decrease the melting temperature of the mixture are the phosphorus-containing hazardous waste of animal or human origin, especially bones-containing waste from hospitals or slaughterhouses, in an amount of up to 60 wt% relative to the amount of the basic component in the form of asbestos and/or products containing asbestos.
6. The method according to claim 1 , characterized in that the supplementary materials that decrease the melting temperature of the mixture are the phosphorus-containing hazardous waste of animal or human origin, especially bones-containing waste from hospitals or slaughterhouses, mixed with the debris from the coal dump, containing from 3 to 15 wt% coal, and grains of quartz, muscovite, potassium feldspar, and others, where the materials of the dump are added in an amount of from 10 to 50 wt% relative to the basic component in the form of asbestos and/or products containing asbestos, while the hazardous waste is added in an amount of up to 20% compared to the mixture of materials from the coal dump and asbestos and/or products containing asbestos.
7. The method according to claim 1 , characterized in that the supplementary materials that decrease the melting temperature of the mixture are the feldspar fluxes, in an amount exceeding 5 wt% relative to the amount of the basic component in the form of asbestos and/or products containing asbestos, mixed with the phosphorus-containing hazardous waste of animal or human origin, especially bones-containing waste from hospitals or slaughterhouses, in an amount exceeding 5 wt% relative to the amount of the basic component in the form of asbestos and/or products containing asbestos.
PCT/PL2012/000060 2012-02-06 2012-07-30 Method of utilization of asbestos and/or asbestos-containing products WO2013055242A2 (en)

Applications Claiming Priority (2)

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PLP.398013 2012-02-06
PL398013A PL215074B1 (en) 2012-02-06 2012-02-06 Method for utilization of asbestos an/or asbestos containing products

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WO2013055242A2 true WO2013055242A2 (en) 2013-04-18
WO2013055242A3 WO2013055242A3 (en) 2013-06-13
WO2013055242A4 WO2013055242A4 (en) 2013-07-25

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Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
PL197566A1 (en) 1977-04-21 1978-02-27 Gorniczo Hutniczy Miedzi SYSTEM FOR THE CONTINUOUS MEASUREMENT OF THE GRAIN LEVEL OF MATERIAL, STORED IN A TANK OR ON A BANK
PL201476A1 (en) 1977-10-11 1979-05-07 Akad Medyczna MIXTURES FOR CLEANING PRECISION MECHANISMS, ESPECIALLY NOZZLES FOR HIGH PRESSURE ENGINES
PL209165A1 (en) 1978-08-22 1980-03-24 Mezoegaz Gepgyar Szolgalt Vall
PL359958A1 (en) 2003-05-05 2004-11-15 Bronisław Trefler Method for waste-free utilization of asbestos and asbestos containing products
PL188640B1 (en) 1998-08-14 2005-03-31 Przed Prod Handlowe Utex Sp Z Method of utilising asbestos and cement containing wastes
PL369748A1 (en) 2004-08-25 2006-03-06 Maciej Pawlikowski Method for the management of asbestos or the products containing asbestos

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Publication number Priority date Publication date Assignee Title
DE4330551A1 (en) * 1993-09-09 1995-03-16 Werner Prof Dr Rammensee Process for the environmentally tolerable disposal of mineral fibres and substances containing mineral fibres and their conversion into materials of value
IT1274417B (en) * 1995-05-03 1997-07-17 Enel Spa PROCEDURE FOR GLAZING COMPOSITE MATERIALS CONTAINING ASBESTOS
ITRE20080057A1 (en) * 2008-06-25 2009-12-26 Michele Carnevali '' PROCEDURE FOR MANUFACTURING OF ARTICLES ARISING FROM HAZARDOUS WASTE ''
FR2951968B1 (en) * 2009-11-05 2012-01-06 Centre Nat Rech Scient CONVERSION OF CEMENT ASBESTOS INTO A SOLID MATERIAL BASED ON AMORPHOUS SILICA

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
PL197566A1 (en) 1977-04-21 1978-02-27 Gorniczo Hutniczy Miedzi SYSTEM FOR THE CONTINUOUS MEASUREMENT OF THE GRAIN LEVEL OF MATERIAL, STORED IN A TANK OR ON A BANK
PL201476A1 (en) 1977-10-11 1979-05-07 Akad Medyczna MIXTURES FOR CLEANING PRECISION MECHANISMS, ESPECIALLY NOZZLES FOR HIGH PRESSURE ENGINES
PL209165A1 (en) 1978-08-22 1980-03-24 Mezoegaz Gepgyar Szolgalt Vall
PL188640B1 (en) 1998-08-14 2005-03-31 Przed Prod Handlowe Utex Sp Z Method of utilising asbestos and cement containing wastes
PL359958A1 (en) 2003-05-05 2004-11-15 Bronisław Trefler Method for waste-free utilization of asbestos and asbestos containing products
PL369748A1 (en) 2004-08-25 2006-03-06 Maciej Pawlikowski Method for the management of asbestos or the products containing asbestos

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
C. LEONELLI; P. VERONESI; D.N. BOCCACCINI; M.R. RIVASI; L. BARBIERI; F. ANDREOLA; I. LANCELLOTTI; D. RABITTI; G.C. PELLACANI: "Microwave thermal inertisation of asbestos-containing waste and its recycling in traditional ceramics", JOURNAL OF HAZARDOUS MATERIALS, vol. 135, no. 1-3, 31 July 2006 (2006-07-31), pages 149 - 155

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WO2013055242A4 (en) 2013-07-25
PL215074B1 (en) 2013-10-31
WO2013055242A3 (en) 2013-06-13
PL398013A1 (en) 2012-08-13

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