WO2007104368A1 - Method for treating the sludge produced by the stone cutting and polishing process - Google Patents
Method for treating the sludge produced by the stone cutting and polishing process Download PDFInfo
- Publication number
- WO2007104368A1 WO2007104368A1 PCT/EP2006/067286 EP2006067286W WO2007104368A1 WO 2007104368 A1 WO2007104368 A1 WO 2007104368A1 EP 2006067286 W EP2006067286 W EP 2006067286W WO 2007104368 A1 WO2007104368 A1 WO 2007104368A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- sludge
- drying
- thermal energy
- thermal
- equipment
- Prior art date
Links
- 239000010802 sludge Substances 0.000 title claims abstract description 51
- 238000005520 cutting process Methods 0.000 title claims abstract description 21
- 238000007517 polishing process Methods 0.000 title claims abstract description 18
- 239000004575 stone Substances 0.000 title claims abstract description 13
- 238000000034 method Methods 0.000 title claims description 45
- 238000001035 drying Methods 0.000 claims abstract description 36
- 239000007788 liquid Substances 0.000 claims description 16
- 238000005057 refrigeration Methods 0.000 claims description 13
- 239000007787 solid Substances 0.000 claims description 11
- 239000000567 combustion gas Substances 0.000 claims description 9
- 239000004579 marble Substances 0.000 claims description 7
- 239000000725 suspension Substances 0.000 claims description 7
- 238000010521 absorption reaction Methods 0.000 claims description 6
- 238000002207 thermal evaporation Methods 0.000 claims description 5
- 239000012530 fluid Substances 0.000 claims description 3
- 239000010438 granite Substances 0.000 claims description 3
- 230000007613 environmental effect Effects 0.000 abstract description 5
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 18
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 description 14
- 229910000019 calcium carbonate Inorganic materials 0.000 description 7
- 238000001914 filtration Methods 0.000 description 7
- 229910052500 inorganic mineral Inorganic materials 0.000 description 6
- 239000011707 mineral Substances 0.000 description 6
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 5
- 239000001301 oxygen Substances 0.000 description 5
- 229910052760 oxygen Inorganic materials 0.000 description 5
- 239000002245 particle Substances 0.000 description 5
- 239000007789 gas Substances 0.000 description 4
- 238000004519 manufacturing process Methods 0.000 description 4
- 239000000463 material Substances 0.000 description 4
- 238000005498 polishing Methods 0.000 description 4
- 239000000126 substance Substances 0.000 description 4
- 239000000654 additive Substances 0.000 description 3
- 238000002485 combustion reaction Methods 0.000 description 3
- 238000009833 condensation Methods 0.000 description 3
- 230000005494 condensation Effects 0.000 description 3
- 230000005611 electricity Effects 0.000 description 3
- 239000000446 fuel Substances 0.000 description 3
- 239000000203 mixture Substances 0.000 description 3
- 150000003839 salts Chemical class 0.000 description 3
- MYMOFIZGZYHOMD-UHFFFAOYSA-N Dioxygen Chemical compound O=O MYMOFIZGZYHOMD-UHFFFAOYSA-N 0.000 description 2
- ATUOYWHBWRKTHZ-UHFFFAOYSA-N Propane Chemical compound CCC ATUOYWHBWRKTHZ-UHFFFAOYSA-N 0.000 description 2
- 230000000996 additive effect Effects 0.000 description 2
- JYYOBHFYCIDXHH-UHFFFAOYSA-N carbonic acid;hydrate Chemical compound O.OC(O)=O JYYOBHFYCIDXHH-UHFFFAOYSA-N 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000001704 evaporation Methods 0.000 description 2
- 230000008020 evaporation Effects 0.000 description 2
- 238000010438 heat treatment Methods 0.000 description 2
- 238000009434 installation Methods 0.000 description 2
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 2
- JTJMJGYZQZDUJJ-UHFFFAOYSA-N phencyclidine Chemical class C1CCCCN1C1(C=2C=CC=CC=2)CCCCC1 JTJMJGYZQZDUJJ-UHFFFAOYSA-N 0.000 description 2
- 239000000047 product Substances 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- 238000011084 recovery Methods 0.000 description 2
- 239000002699 waste material Substances 0.000 description 2
- 238000004065 wastewater treatment Methods 0.000 description 2
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- 239000000853 adhesive Substances 0.000 description 1
- 230000001070 adhesive effect Effects 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 239000003225 biodiesel Substances 0.000 description 1
- 239000001273 butane Substances 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 239000004568 cement Substances 0.000 description 1
- 239000000701 coagulant Substances 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 239000002537 cosmetic Substances 0.000 description 1
- 238000010908 decantation Methods 0.000 description 1
- -1 diesel Substances 0.000 description 1
- 238000006073 displacement reaction Methods 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 230000009977 dual effect Effects 0.000 description 1
- 229920001971 elastomer Polymers 0.000 description 1
- 238000000605 extraction Methods 0.000 description 1
- 239000008394 flocculating agent Substances 0.000 description 1
- 239000000295 fuel oil Substances 0.000 description 1
- 238000001033 granulometry Methods 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- IJDNQMDRQITEOD-UHFFFAOYSA-N n-butane Chemical compound CCCC IJDNQMDRQITEOD-UHFFFAOYSA-N 0.000 description 1
- OFBQJSOFQDEBGM-UHFFFAOYSA-N n-pentane Natural products CCCCC OFBQJSOFQDEBGM-UHFFFAOYSA-N 0.000 description 1
- 239000003345 natural gas Substances 0.000 description 1
- 239000003973 paint Substances 0.000 description 1
- 239000000123 paper Substances 0.000 description 1
- 239000004033 plastic Substances 0.000 description 1
- 229920003023 plastic Polymers 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 239000001294 propane Substances 0.000 description 1
- 239000003507 refrigerant Substances 0.000 description 1
- 239000005060 rubber Substances 0.000 description 1
- 239000000565 sealant Substances 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000010454 slate Substances 0.000 description 1
- 239000011343 solid material Substances 0.000 description 1
- 239000012265 solid product Substances 0.000 description 1
- 238000004901 spalling Methods 0.000 description 1
- 238000005507 spraying Methods 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/121—Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering
- C02F11/127—Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering by centrifugation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B28—WORKING CEMENT, CLAY, OR STONE
- B28D—WORKING STONE OR STONE-LIKE MATERIALS
- B28D1/00—Working stone or stone-like materials, e.g. brick, concrete or glass, not provided for elsewhere; Machines, devices, tools therefor
- B28D1/02—Working stone or stone-like materials, e.g. brick, concrete or glass, not provided for elsewhere; Machines, devices, tools therefor by sawing
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/13—Treatment of sludge; Devices therefor by de-watering, drying or thickening by heating
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F26—DRYING
- F26B—DRYING SOLID MATERIALS OR OBJECTS BY REMOVING LIQUID THEREFROM
- F26B23/00—Heating arrangements
- F26B23/001—Heating arrangements using waste heat
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F26—DRYING
- F26B—DRYING SOLID MATERIALS OR OBJECTS BY REMOVING LIQUID THEREFROM
- F26B25/00—Details of general application not covered by group F26B21/00 or F26B23/00
- F26B25/005—Treatment of dryer exhaust gases
- F26B25/006—Separating volatiles, e.g. recovering solvents from dryer exhaust gases
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F26—DRYING
- F26B—DRYING SOLID MATERIALS OR OBJECTS BY REMOVING LIQUID THEREFROM
- F26B5/00—Drying solid materials or objects by processes not involving the application of heat
- F26B5/08—Drying solid materials or objects by processes not involving the application of heat by centrifugal treatment
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F26—DRYING
- F26B—DRYING SOLID MATERIALS OR OBJECTS BY REMOVING LIQUID THEREFROM
- F26B7/00—Drying solid materials or objects by processes using a combination of processes not covered by a single one of groups F26B3/00 and F26B5/00
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/10—Nature of the water, waste water, sewage or sludge to be treated from quarries or from mining activities
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F26—DRYING
- F26B—DRYING SOLID MATERIALS OR OBJECTS BY REMOVING LIQUID THEREFROM
- F26B2200/00—Drying processes and machines for solid materials characterised by the specific requirements of the drying good
- F26B2200/18—Sludges, e.g. sewage, waste, industrial processes, cooling towers
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P70/00—Climate change mitigation technologies in the production process for final industrial or consumer products
- Y02P70/10—Greenhouse gas [GHG] capture, material saving, heat recovery or other energy efficient measures, e.g. motor control, characterised by manufacturing processes, e.g. for rolling metal or metal working
Definitions
- the present invention relates to a method for treating the sludge produced by the stone cutting and polishing process that comprises thermal drying of said sludge .
- Sludges are waste products produced during an industrial process and/or a wastewater treatment process, basically characterised in that their composition presents a very high liquid fraction, often exceeding 80%, which hinders their handling and subsequent treatment.
- the sludge obtained from the natural stone cutting and polishing processes is treated physically and chemically to reduce its water content.
- the liquid fraction that is obtained from said physico-chemical treatment still contains a high proportion of mineral in suspension and dissolved salts that hugely hinders its reutilisation in the cutting and polishing process, since it has a highly adverse effect both on the useful life and the maintenance of the machinery used in the treatment facilities.
- the thermal energy required for carrying out the thermal drying of sludges can be obtained using cogeneration equipment that produces, and at the same time uses, both electricity and heat.
- sludge-treatment processes are known that make use of the thermal energy coming from the high- temperature (400 0 C to 600 0 C) combustion and post- combustion gases from the cogeneration equipment to carry out the drying of said sludges.
- the objective of the present invention is to resolve the disadvantages mentioned by developing a method for treating the sludge produced in the stone cutting and polishing process that has high energy efficiency and makes it possible valorization of said sludge.
- the method of the present invention includes thermal drying of said sludge, using for the purpose thermal energy provided from cogeneration equipment, and is characterised in that the steam from drying of said sludge is condensed, also by using for this condensation the thermal energy from said cogeneration equipment. Thanks to these characteristics, the method of the present invention has a very high energy efficiency, exceeding 95%, since in addition to the electrical energy produced during cogeneration, use is also made of practically all the thermal energy generated by the equipment that carries out said cogeneration.
- Another advantage of the sludge treatment process itself lies in condensation of the steam produced by the sludge drying, enabling a by-product to be obtained which, in most cases, can be reutilised in industry without any need to be submitted to subsequent additional conversion processes .
- the process of the present invention has the advantage of enabling valorization of the sludges produced in the stone polishing and cutting process, all this with very high energy efficiency and nil environmental impact.
- said steam is condensed by means of absorption refrigeration equipment that uses said thermal energy .
- absorption refrigeration equipment some of the thermal energy from the cogeneration equipment can be used directly to vaporise the refrigerant of said equipment and produce cold.
- the thermal energy from the cogeneration equipment itself the refrigeration energy needed to condense the steam from drying of the sludge is also obtained.
- the thermal energy that said refrigeration equipment uses comes from the fluid employed to refrigerate the cogeneration equipment.
- the warm fluid from the refrigeration system for the components of the cogeneration equipment can be used as a source of heat for the absorption refrigeration equipment.
- said thermal drying is instantaneous, and the thermal energy used for the drying comes from the high-temperature combustion gases of the cogeneration equipment .
- Instantaneous drying has the advantage of allowing a solid product of very low humidity content to be obtained, directly using for the purpose the hot combustion gases from the cogeneration equipment itself, which gases are injected into the dryer.
- the temperature of the combustion gases can be increased by post-combustion of said gases through an additional supply of oxygen.
- This additional supply of oxygen can be provided either by injecting a mixture of air and oxygen or by injecting pure oxygen.
- Post-combustion gases are thus obtained at an approximate temperature of 600 0 C that is very efficient for drying.
- said instantaneous drying is carried out using a turbodryer.
- Such an appliance combines turbulence and vacuum effects with high-speed displacement of moist and dispersed solid particles.
- the turbodryer has the advantage of enabling an intense drying action with minimum heating of the solid.
- a stage is carried out in which the liquid fraction proportion of the sludge is reduced.
- said reduction of liquid fraction is carried out by means of a centrifuge that permits efficient separation of a large proportion of solid particles.
- said liquid fraction is treated in order to reduce its content of solids in suspension.
- said treatment is carried out by equipment that uses a filtering process.
- the effluent proceeding from the filtering of said liquid fraction is treated in order to reduce its content of dissolved solids.
- said treatment is carried out by means of a thermal evaporation process that uses thermal energy from the cogeneration equipment.
- the residual fraction of sludge from the treatment of said liquid fraction or effluent is recirculated for drying, thus once again avoiding generating a moist residue of high environmental impact.
- said natural stone is marble or granite .
- Application of the process of the invention to the sludge from the cutting and polishing of the marble enables obtaining, on the one hand water free from materials in suspension and dissolved salts, which can be reutilised in the process without causing the machinery any kind of problem, and on the other hand dry calcium carbonate that can be reutilised as a raw material or additive in another type of industry.
- sludge shall be taken to mean an inorganic substance proceeding from the stone cutting and polishing process, whose liquid fraction can be evaporated, totally or partially, by means of the thermal energy produced by cogeneration equipment.
- Cogeneration is taken to mean the simultaneous production and use of electricity and heat, by means of cogeneration equipment with motor generators, gas turbines, steam turbines, fuel cells, or any other system or equipment capable of generating electricity and heat from a fuel .
- the sludge produced by the process is entirely collected into a decanting silo, having been passed first through a spalling basket and lifting pumps.
- Said silo is equipped with a chemical additives preparation system (flocculants and/or coagulants) that are added to the sludge to improve the decantation efficacy.
- the sludge has an approximate proportion of 80% water and 20% calcium carbonate. From the silo, the sludges are pumped to a centrifuge in order to reduce their proportion of water.
- the liquid fraction of sludge from the centrifuge is subsequently treated by means of filtering equipment that allows the solids in suspension that this fraction still contains, basically calcium carbonate, to be removed.
- Downstream of the filtering equipment is a second piece of equipment that treats the effluent from the filtering stage by thermal evaporation in order to remove the solids or dissolved salts.
- This evaporation process employs the thermal energy of the hot water from the refrigeration system of the cogeneration equipment.
- the effluent from the thermal evaporation process is a high- quality condensed technical water that can be reutilised without the least problem in the cutting and polishing process itself.
- the residual fraction of sludge from the dual filtering and thermal evaporation treatment applied to the liquid fraction coming from the centrifuge is recirculated to the fraction of centrifuged sludge and taken, along with that fraction, to the installation where the instantaneous drying is carried out .
- the instantaneous drying installation of the embodiment described comprises a turbodryer and a set of cyclones and sleeve filters.
- the drying chamber of the turbodryer is fed with the fraction of sludge to be dried, the high-temperature combustion gases from the cogeneration motors and warm compressed air.
- the sludge fraction is introduced into the dryer by means of spraying nozzles, in the case of suspensions and solutions, and by means of an alveolar valve or endless conveyor belt in the case of moist solids.
- the warm compressed air introduced into the turbodryer drying chamber has the main function of breaking down the sludge, thus increasing its surface area in order to facilitate the drying action with minimum heating of the sludge, which action is basically carried out by the combustion gases that are at an approximate temperature of 400 0 C.
- the temperature of the combustion gases from the cogeneration motors can be increased to approximately 600 0 C by means of an additional supply of oxygen and by carrying out post- combustion of the aforesaid gases.
- Said additional supply can be carried out by means of atmospheric air, an oxygen and air mixture or pure oxygen.
- the turbodryer has a system of recirculation and control of aspiration of particles that permits the moistest particles and/or agglomerates to be sent back to the drying chamber.
- the dry and disintegrated particles of mineral material are taken along with the water vapour produced during the drying to the set of cyclones and sleeve filters, where they are separated from vapour.
- the water vapour from the drying of the sludge is condensed in the condenser of the absorption refrigeration equipment that uses the thermal energy of the hot water (9O 0 C to 95 0 C) from the refrigeration of the cogeneration equipment motors.
- the result is a high-quality technical water that can be reutilised in the cutting and polishing process without causing any problem to the equipment, while at the same time permitting a major saving of the increasingly scarce resource that is water.
- the dry micronised mineral from the dryer which is calcium carbonate in the case of the embodiment described
- this is graded in a classifier and, optionally, ground in order to obtain a uniform granulometry suitable for the requirements of the markets in which it has a high value as a raw material or as an additive (lime markets, cement industries, paper, paints, plastics, adhesives, sealants, pharmaceuticals and cosmetics, manufacturing of carpets, rubbers, construction pre-manufactures, agricultural use, and so forth) .
- the method of the present invention enables valorization of the inorganic sludge produced in the stone cutting and polishing process, by means of a cogeneration appliance or system that provides the entire electrical and thermal/refrigeration energy requirements of the process and ensures total recovery of the components of said sludge.
- the method of the present invention has the advantage of possessing very high energy efficiency, since practically all the energy of the fuel (natural gas, propane, butane, diesel, fuel oil, biodiesel, etc.) used in the cogeneration equipment is made use of in the form of electrical energy and thermal energy.
- the electrical energy generated sufficiently meets the process needs, while the thermal energy generated is basically used to carry out thermal drying of the sludge and to meet the needs of the absorption refrigeration equipment that condenses the steam produced by the process.
- the method of the present invention has the advantage of enabling valorization of the components of the sludge produced in the stone cutting and polishing process.
- the table inserted below shows by way of example the balance of materials of the method of the present invention applied to a marble cutting and polishing facility that produces some 12,000 Kg/h of sludge containing 80% water and 20% calcium carbonate.
- the method of the present invention enables recovery of all the components of the sludge, water and calcium carbonate.
- the conditions under which said components are recovered are optimum for ensuring that use is made of them.
- Table 1 Balance of materials of the method of the present invention applied to a marble cutting and polishing facility .
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- Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- Life Sciences & Earth Sciences (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Chemical & Material Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Health & Medical Sciences (AREA)
- Mining & Mineral Resources (AREA)
- Molecular Biology (AREA)
- Sustainable Development (AREA)
- Treatment Of Sludge (AREA)
Abstract
Includes the thermal drying of said sludge, using for this purpose thermal energy from cogeneration equipment, and is characterised in that the steam from the drying of said sludge is condensed by also using the thermal energy from said cogeneration equipment. This enables valorization of the sludges from the stone cutting and polishing process, all this with very high energy efficiency and nil environmental impact.
Description
METHOD FOR TREATING THE SLUDGE PRODUCED BY THE STONE CUTTING AND POLISHING PROCESS
The present invention relates to a method for treating the sludge produced by the stone cutting and polishing process that comprises thermal drying of said sludge .
BACKGROUND OF THE INVENTION
Sludges are waste products produced during an industrial process and/or a wastewater treatment process, basically characterised in that their composition presents a very high liquid fraction, often exceeding 80%, which hinders their handling and subsequent treatment.
The extraction and production industries for natural stone such as marble, granite and slate use a large flow of water to carry out the cutting and polishing of the stone. The abundant water used, together with the micronised mineral in suspension generated by the cutting and polishing process, give rise to a waste called sludge.
The sludge obtained from the natural stone cutting and polishing processes is treated physically and chemically to reduce its water content. However, given the nature of the solid material that the aforesaid sludge (micronised mineral) contains, the liquid fraction that is obtained from said physico-chemical treatment still contains a high proportion of mineral in suspension and dissolved salts that hugely hinders its reutilisation in the cutting and polishing process, since it has a highly adverse effect both on the useful life and the maintenance of the machinery used in the treatment facilities.
As regards the dewatered sludge fraction emerging from the aforesaid physico-chemical treatment, this is eliminated by transporting it to a landfill tip, with a
very high environmental cost owing to the fact that it is technical-economically impossible separating the micronised mineral from the wastewater fraction that the said dehydrated sludge fraction still contains. Processes for the treatment of sludges are known, such as those for treating the sludges produced by wastewater treatment, which include a stage of drying said sludge with thermal energy in order to reduce its water content by vaporising the water into the atmosphere. Once the sludge is dry, i.e. once its humidity content has been reduced to below 10%, the sludge can be incinerated or processed in order to convert it.
The thermal energy required for carrying out the thermal drying of sludges can be obtained using cogeneration equipment that produces, and at the same time uses, both electricity and heat.
Indeed, sludge-treatment processes are known that make use of the thermal energy coming from the high- temperature (4000C to 6000C) combustion and post- combustion gases from the cogeneration equipment to carry out the drying of said sludges.
The cogeneration facilities known to date for the drying of sludges nevertheless have the disadvantage of having a very low output, and the products obtained from drying of the sludge need to go through subsequent conversion processes to allow them to be reutilised or taken advantage of. Furthermore, the environmental impact of such cogeneration facilities is usually high, particularly as regards odours and other toxic gaseous emissions, which leads to a high economic cost in impact- correction measures and, frequently, considerable public rejection by the inhabitants of zones close to the cogeneration facilities.
DESCRIPTION OF THE INVENTION
The objective of the present invention is to resolve the disadvantages mentioned by developing a method for treating the sludge produced in the stone cutting and polishing process that has high energy efficiency and makes it possible valorization of said sludge.
In accordance with this objective, the method of the present invention includes thermal drying of said sludge, using for the purpose thermal energy provided from cogeneration equipment, and is characterised in that the steam from drying of said sludge is condensed, also by using for this condensation the thermal energy from said cogeneration equipment. Thanks to these characteristics, the method of the present invention has a very high energy efficiency, exceeding 95%, since in addition to the electrical energy produced during cogeneration, use is also made of practically all the thermal energy generated by the equipment that carries out said cogeneration.
Another advantage of the sludge treatment process itself lies in condensation of the steam produced by the sludge drying, enabling a by-product to be obtained which, in most cases, can be reutilised in industry without any need to be submitted to subsequent additional conversion processes .
Surprisingly, the process of the present invention has the advantage of enabling valorization of the sludges produced in the stone polishing and cutting process, all this with very high energy efficiency and nil environmental impact.
Preferably, said steam is condensed by means of absorption refrigeration equipment that uses said thermal energy . Thanks to the absorption refrigeration equipment,
some of the thermal energy from the cogeneration equipment can be used directly to vaporise the refrigerant of said equipment and produce cold. Thus, with the thermal energy from the cogeneration equipment itself, the refrigeration energy needed to condense the steam from drying of the sludge is also obtained.
Advantageously, the thermal energy that said refrigeration equipment uses comes from the fluid employed to refrigerate the cogeneration equipment. Thus, the warm fluid from the refrigeration system for the components of the cogeneration equipment can be used as a source of heat for the absorption refrigeration equipment.
Preferably, said thermal drying is instantaneous, and the thermal energy used for the drying comes from the high-temperature combustion gases of the cogeneration equipment .
Instantaneous drying has the advantage of allowing a solid product of very low humidity content to be obtained, directly using for the purpose the hot combustion gases from the cogeneration equipment itself, which gases are injected into the dryer.
Advantageously, the temperature of the combustion gases can be increased by post-combustion of said gases through an additional supply of oxygen. This additional supply of oxygen can be provided either by injecting a mixture of air and oxygen or by injecting pure oxygen.
Post-combustion gases are thus obtained at an approximate temperature of 6000C that is very efficient for drying. Also preferably, said instantaneous drying is carried out using a turbodryer. Such an appliance combines turbulence and vacuum effects with high-speed displacement of moist and dispersed solid particles. The turbodryer has the advantage of enabling an intense drying action with minimum heating of the solid.
Again preferably, prior to the thermal drying a stage is carried out in which the liquid fraction proportion of the sludge is reduced. Advantageously, said reduction of liquid fraction is carried out by means of a centrifuge that permits efficient separation of a large proportion of solid particles.
According to a preferred embodiment, said liquid fraction is treated in order to reduce its content of solids in suspension. Advantageously, said treatment is carried out by equipment that uses a filtering process.
According to the same preferred embodiment, the effluent proceeding from the filtering of said liquid fraction is treated in order to reduce its content of dissolved solids. Advantageously, said treatment is carried out by means of a thermal evaporation process that uses thermal energy from the cogeneration equipment.
Preferably, in the aforesaid preferred embodiment, the residual fraction of sludge from the treatment of said liquid fraction or effluent is recirculated for drying, thus once again avoiding generating a moist residue of high environmental impact.
Advantageously, said natural stone is marble or granite . Application of the process of the invention to the sludge from the cutting and polishing of the marble enables obtaining, on the one hand water free from materials in suspension and dissolved salts, which can be reutilised in the process without causing the machinery any kind of problem, and on the other hand dry calcium carbonate that can be reutilised as a raw material or additive in another type of industry.
In the present invention, sludge shall be taken to mean an inorganic substance proceeding from the stone cutting and polishing process, whose liquid fraction can
be evaporated, totally or partially, by means of the thermal energy produced by cogeneration equipment.
Cogeneration is taken to mean the simultaneous production and use of electricity and heat, by means of cogeneration equipment with motor generators, gas turbines, steam turbines, fuel cells, or any other system or equipment capable of generating electricity and heat from a fuel .
DESCRIPTION OF A PREFERRED EMBODIMENT
Described below is a preferred embodiment of the method of the present invention applied to the sludge produced in the marble cutting and polishing process. This is an inorganic residue that contains water and calcium carbonate as its majority components.
In the embodiment described, the sludge produced by the process is entirely collected into a decanting silo, having been passed first through a spalling basket and lifting pumps. Said silo is equipped with a chemical additives preparation system (flocculants and/or coagulants) that are added to the sludge to improve the decantation efficacy.
At the output from the silo, the sludge has an approximate proportion of 80% water and 20% calcium carbonate. From the silo, the sludges are pumped to a centrifuge in order to reduce their proportion of water.
The liquid fraction of sludge from the centrifuge is subsequently treated by means of filtering equipment that allows the solids in suspension that this fraction still contains, basically calcium carbonate, to be removed. Downstream of the filtering equipment is a second piece of equipment that treats the effluent from the filtering stage by thermal evaporation in order to remove the solids or dissolved salts. This evaporation process
employs the thermal energy of the hot water from the refrigeration system of the cogeneration equipment. The effluent from the thermal evaporation process is a high- quality condensed technical water that can be reutilised without the least problem in the cutting and polishing process itself.
In the embodiment described the residual fraction of sludge from the dual filtering and thermal evaporation treatment applied to the liquid fraction coming from the centrifuge is recirculated to the fraction of centrifuged sludge and taken, along with that fraction, to the installation where the instantaneous drying is carried out .
The instantaneous drying installation of the embodiment described comprises a turbodryer and a set of cyclones and sleeve filters.
The drying chamber of the turbodryer is fed with the fraction of sludge to be dried, the high-temperature combustion gases from the cogeneration motors and warm compressed air.
The sludge fraction is introduced into the dryer by means of spraying nozzles, in the case of suspensions and solutions, and by means of an alveolar valve or endless conveyor belt in the case of moist solids. The warm compressed air introduced into the turbodryer drying chamber has the main function of breaking down the sludge, thus increasing its surface area in order to facilitate the drying action with minimum heating of the sludge, which action is basically carried out by the combustion gases that are at an approximate temperature of 4000C.
As noted in the description of the invention, the temperature of the combustion gases from the cogeneration motors can be increased to approximately 6000C by means of an additional supply of oxygen and by carrying out post-
combustion of the aforesaid gases. Said additional supply can be carried out by means of atmospheric air, an oxygen and air mixture or pure oxygen.
The turbodryer has a system of recirculation and control of aspiration of particles that permits the moistest particles and/or agglomerates to be sent back to the drying chamber. The dry and disintegrated particles of mineral material are taken along with the water vapour produced during the drying to the set of cyclones and sleeve filters, where they are separated from vapour.
The water vapour from the drying of the sludge is condensed in the condenser of the absorption refrigeration equipment that uses the thermal energy of the hot water (9O0C to 950C) from the refrigeration of the cogeneration equipment motors. The result is a high-quality technical water that can be reutilised in the cutting and polishing process without causing any problem to the equipment, while at the same time permitting a major saving of the increasingly scarce resource that is water. As regards the dry micronised mineral from the dryer, which is calcium carbonate in the case of the embodiment described, this is graded in a classifier and, optionally, ground in order to obtain a uniform granulometry suitable for the requirements of the markets in which it has a high value as a raw material or as an additive (lime markets, cement industries, paper, paints, plastics, adhesives, sealants, pharmaceuticals and cosmetics, manufacturing of carpets, rubbers, construction pre-manufactures, agricultural use, and so forth) . Surprisingly, the method of the present invention enables valorization of the inorganic sludge produced in the stone cutting and polishing process, by means of a cogeneration appliance or system that provides the entire electrical and thermal/refrigeration energy requirements of the process and ensures total recovery of the
components of said sludge.
The method of the present invention has the advantage of possessing very high energy efficiency, since practically all the energy of the fuel (natural gas, propane, butane, diesel, fuel oil, biodiesel, etc.) used in the cogeneration equipment is made use of in the form of electrical energy and thermal energy. The electrical energy generated sufficiently meets the process needs, while the thermal energy generated is basically used to carry out thermal drying of the sludge and to meet the needs of the absorption refrigeration equipment that condenses the steam produced by the process.
Again surprisingly, the method of the present invention has the advantage of enabling valorization of the components of the sludge produced in the stone cutting and polishing process.
The table inserted below shows by way of example the balance of materials of the method of the present invention applied to a marble cutting and polishing facility that produces some 12,000 Kg/h of sludge containing 80% water and 20% calcium carbonate.
As the aforesaid table shows, the method of the present invention enables recovery of all the components of the sludge, water and calcium carbonate. The conditions under which said components are recovered are optimum for ensuring that use is made of them.
Table 1: Balance of materials of the method of the present invention applied to a marble cutting and polishing facility .
CENTRIFUGING, THERMAL DRYING AND SLUDGE CONDENSATION
FILTERING AND EVAPORATION OF THE LIQUID FRACTION FROM THE
CENTRIFUGE
Claims
1. Method for treating the sludge produced by the stone cutting and polishing process, which includes the thermal drying of said sludge, using for the purpose thermal energy from cogeneration equipment, characterised in that the steam from the drying of said sludge is condensed, also using for this process the thermal energy from said cogeneration equipment.
2. Method according to claim 1, characterised in that said steam is condensed by means of absorption refrigeration equipment that uses said thermal energy.
3. Method according to claim 2, characterised in that the thermal energy used by said refrigeration equipment comes from the fluid used to refrigerate said cogeneration equipment.
4. Method according to any of the preceding claims, characterised in that said thermal drying is instantaneous, and the thermal energy used for said drying comes from the high-temperature combustion gases from said cogeneration equipment.
5. Method according to claim 4, characterised in that said instantaneous drying is carried out by means of a turbodryer.
6. Method according to claim 1, characterised in that prior to the thermal drying, a stage is carried out in which the proportion of liquid fraction of said sludge is reduced.
7. Method according to claim 6, characterised in that said reduction of liquid fraction is carried out by means of a centrifuge.
8. Method according to claim 6, characterised in that said liquid fraction is treated to reduce its content of solids in suspension.
9. Method according to claim 8, characterised in that the effluent from the treatment of said liquid fraction is treated to reduce its content of dissolved solids .
10. Method according to claim 9, characterised in that said treatment to reduce the content of dissolved solids is carried out by means of a thermal evaporation process that uses thermal energy from the cogeneration equipment .
11. Method according to either of claims 8 and 9, characterised in that the residual fraction of sludge from the treatment of said liquid fraction or effluent is recirculated to be dried.
12. Method according to claim 1, characterised in that said sludges are residues produced during the marble cutting and polishing process.
13. Method according to claim 1, characterised in that said sludges are residues produced during the granite cutting and polishing process.
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
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ESP-200600648 | 2006-03-14 | ||
ES200600648A ES2281295B1 (en) | 2006-03-14 | 2006-03-14 | PROCEDURE FOR THE TREATMENT OF THE MUD FROM THE PROCESS OF POLISHING AND CUTTING OF STONE. |
Publications (1)
Publication Number | Publication Date |
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WO2007104368A1 true WO2007104368A1 (en) | 2007-09-20 |
Family
ID=37561247
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
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PCT/EP2006/067286 WO2007104368A1 (en) | 2006-03-14 | 2006-10-11 | Method for treating the sludge produced by the stone cutting and polishing process |
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Country | Link |
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ES (1) | ES2281295B1 (en) |
WO (1) | WO2007104368A1 (en) |
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2009033943A1 (en) * | 2007-09-10 | 2009-03-19 | Dario Toncelli | Process and plant for treating sludges resulting from the machining of articles of agglomerated stone material |
ITTV20090039A1 (en) * | 2009-03-12 | 2010-09-13 | Dario Toncelli | PROCEDURE AND PLANT FOR THE TREATMENT OF MUDS PROCESSING OF ARTICLES OF STONE-MADE AGGLOMERATE MATERIAL. |
ITBG20090053A1 (en) * | 2009-10-13 | 2011-04-14 | Fil Tec S R L | SYSTEM AND METHOD FOR FILTERING THE WASTE WATER DERIVING FROM THE CUTTING OF BLOCKS AND POLISHING OF MARBLES, GRANITES AND SIMILARS. |
ITBA20110056A1 (en) * | 2011-10-13 | 2013-04-14 | Antonio Ninivaggi | PROCEDURE FOR THE TRANSFORMATION OF SLUDGES BY SAGAGUE PROCESSING, BASIC COMPONENT FOR PASTA PRODUCTION OF: STUCCHI, ADHESIVES, WATERPROOFINGS. |
EP3653310A1 (en) | 2018-11-14 | 2020-05-20 | Cosentino Research & Development, S.L. | Mixture for use as artificial soil comprising stone and/or ceramic machining sludges, method for preparation and uses thereof |
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DE19654093A1 (en) * | 1996-12-23 | 1998-06-25 | Klein Alb Gmbh Co Kg | Low-temperature sewage sludge drying process and assembly uses ambient air |
JP2005288414A (en) * | 2004-04-05 | 2005-10-20 | Takuma Co Ltd | Freezing and thawing system and freezing and thawing method |
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JPS55165197A (en) * | 1979-06-11 | 1980-12-23 | Takeo Sasaki | Sludge drying method |
ES2048091B1 (en) * | 1992-02-03 | 1994-10-01 | Ahlstroem Oy | METHOD AND APPARATUS FOR HEAT SLUDGE HEAT TREATMENT: |
ES2140353B1 (en) * | 1998-07-23 | 2000-08-16 | Gomez Luis Castro | METHOD OF SAWING GRANITES. |
DE10058191A1 (en) * | 2000-11-23 | 2002-07-11 | Baker Hughes De Gmbh | Process and plant for producing storage-stable pellets from sewage sludge |
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- 2006-03-14 ES ES200600648A patent/ES2281295B1/en not_active Expired - Fee Related
- 2006-10-11 WO PCT/EP2006/067286 patent/WO2007104368A1/en active Application Filing
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
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DE19654093A1 (en) * | 1996-12-23 | 1998-06-25 | Klein Alb Gmbh Co Kg | Low-temperature sewage sludge drying process and assembly uses ambient air |
JP2005288414A (en) * | 2004-04-05 | 2005-10-20 | Takuma Co Ltd | Freezing and thawing system and freezing and thawing method |
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2009033943A1 (en) * | 2007-09-10 | 2009-03-19 | Dario Toncelli | Process and plant for treating sludges resulting from the machining of articles of agglomerated stone material |
ITTV20090039A1 (en) * | 2009-03-12 | 2010-09-13 | Dario Toncelli | PROCEDURE AND PLANT FOR THE TREATMENT OF MUDS PROCESSING OF ARTICLES OF STONE-MADE AGGLOMERATE MATERIAL. |
WO2010103445A1 (en) | 2009-03-12 | 2010-09-16 | Dario Toncelli | Method and plant for treating sludges from the machining of articles of agglomerated stone material |
ITBG20090053A1 (en) * | 2009-10-13 | 2011-04-14 | Fil Tec S R L | SYSTEM AND METHOD FOR FILTERING THE WASTE WATER DERIVING FROM THE CUTTING OF BLOCKS AND POLISHING OF MARBLES, GRANITES AND SIMILARS. |
ITBA20110056A1 (en) * | 2011-10-13 | 2013-04-14 | Antonio Ninivaggi | PROCEDURE FOR THE TRANSFORMATION OF SLUDGES BY SAGAGUE PROCESSING, BASIC COMPONENT FOR PASTA PRODUCTION OF: STUCCHI, ADHESIVES, WATERPROOFINGS. |
EP3653310A1 (en) | 2018-11-14 | 2020-05-20 | Cosentino Research & Development, S.L. | Mixture for use as artificial soil comprising stone and/or ceramic machining sludges, method for preparation and uses thereof |
WO2020099501A1 (en) | 2018-11-14 | 2020-05-22 | Cosentino Research & Development, S.L. | Mixture for use as artificial soil comprising stone and/or ceramic machining sludges, method for preparation and uses thereof |
Also Published As
Publication number | Publication date |
---|---|
ES2281295B1 (en) | 2008-09-01 |
ES2281295A1 (en) | 2007-09-16 |
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