The present application is a 371 of International application PCT/AT2013/050037, filed Feb. 13, 2013, which claims priority of AT A204/2012, filed Feb. 20, 2012, the priority of these applications is hereby claimed and these applications are incorporated herein by reference.
The present invention concerns a method for processing of carbon dioxide CO2 contained in an exhaust gas flow to a product suitable for energy production.
This processing is achieved according to the invention in that
The invention is further explained below with reference to the drawing in which
It is initially stated that the individual components of the employed materials and the medium present in the corresponding process steps are subject to continuous measurement 2 during the entire process, in which case material feed to the corresponding process chambers is controlled, as required or as a function of measurement results. For example, the amount of aluminum hydroxide and/or hydrated aluminum oxide to be added is controlled via a continuous pH measurement 2.
In this case the exhaust gas flow 1, for example, crude gas from an incinerator, usually with a pH value of about 4 and with a temperature in the range from 150 to 170° C., in modern incinerators below 150° C., during passage through a drying and cooling chamber 3 optionally consisting of several chamber units, which is supplied with moistened, silicate, porous material and admixed aluminum hydroxide and/or hydrated aluminum oxide 4 and/or other metal oxidizers, is cooled to a temperature of 30-50° C., in which case a basic, aqueous medium is generated and the contained carbon dioxide CO2 is destabilized. The moistened, silicate, porous material 4 is pumice, foam lava and/or perlite in granulated form with a moisture content of 15 to 30% referred to the total dry weight of the silicate material 4. The moistened, silicate, porous material 4 is then dried or its moisture absorbed by exhaust gas flow 1 so that it is cooled. The aqueous medium generated in the drying and cooling chamber 3 is brought to a pH value between 10 and 13 by means of aluminum hydroxide and/or hydrated aluminum oxide. The aqueous medium formed in the drying and cooling chamber 3, in which the destabilized carbon dioxide CO2 present in ionized form is contained, is fed to a subsequent prechamber 5, which is supplied material containing oxidizable alkaline earth and/or heavy metal, in which case oxidation of alkaline earth and/or heavy metal 6 occurs with accompanying neutralization of the aqueous medium containing ionized carbon C. The oxidizable material 6 containing alkaline earth metal, preferably calcium and/or heavy metal is used in fine-granular form as metal, for example, Fe dust, fly ash, hydrated lime, etc. An alkaline earth and/or heavy metal oxide 10 formed during neutralization is discharged subsequently as byproducts from prechamber 5, in which case oxidizable material 6 containing alkaline earth and/or heavy metal is supplied as a function of continuous measurements 2. Following prechamber 5, the medium ordinarily has a pH value of 6. The aqueous medium containing ionized carbon C is then fed to a main chamber 7 equipped with a material 8 consisting of organic carbon compounds and/or containing organic carbon compounds, in which the material 8 can be lignin, lignin derivatives, recovered paper stock and/or plastic materials, pulp or waste substances, etc. With participation of ionized carbon C polyreactions (chain lengthening) with organic carbon compounds occurs to form a carbon enriched end product 9. The polyreactions occurring in the main chamber 7 occur at temperatures between 5 and 80° C., preferably between 30-60° C. and especially 40-45° C. and under a pressure between 0.1 and 10 bar, preferably between 0.1 and 0.7 bar or 5 to 8 bar.
A temperature control arranged in the drying and cooling chamber 3 serves to separate the substances into the corresponding substance-specific state (solid, liquid, gas) in order to produce new compounds.
It is generally observed that under pressure the addition process of carbon C to the moistened silicate porous material 4 occurs more quickly and significantly greater addition also occurs. Moreover, additional substance mixtures can be fed to main chamber 7 as reaction accelerators in order to configure the reaction capacity of the substances and the temperatures in the main chamber 7 so that optimal processing of the carbon dioxide CO2 contained in the exhaust gas flow 1 occurs and a C-enriched end product 9 is formed.
The method according to the invention is further explained by means of a preferred practical example.
Wood waste is used as raw material source for the exhaust gas flow. The crude gas originating from incineration of ground wood waste, shows an average content of O2 between 11.5 and 14 vol % and a CO2 content between 7 and 9 vol %, is fed to a drying and cooling chamber with a temperature of about 150° C., in which the exhaust gas flow is cooled to a temperature of ≦40° C., preferably about 30° C. and which is supplied with pumice as porous silicate material with a moisture content to 60%, referred to the dry weight, with admixed aluminum hydroxide and/or hydrated oxide, said aluminum compounds occurring during KOH production. The exhaust gas flow absorbs the moisture of the pumice, in which case the exhaust gas flow is cooled. At the same time an aqueous medium is generated in the drying and cooling chamber to form a stable suspension of aluminum compounds in water. In the aqueous medium, which has a pH value of roughly neutral to more strongly basic, pH 10 to 13, the carbon dioxide (CO2) contained in it is ionized and destabilized, in which the aqueous medium is cooled to a temperature between 12 and 13° C. up to its output from the drying and cooling chamber.
The aqueous medium is sent from the drying and cooling chamber to a downline prechamber, which is supplied with iron shavings as oxidizable material, in which the ratio of oxidizable material to liquid of the aqueous medium is about 1:7 wt %. The iron shavings are oxidized during simultaneous neutralization of the prechamber medium by the oxygen coming from the ionized and destabilized carbon dioxide. At the output of the prechamber the aqueous medium has an average O2 content of about 16-17 vol % and a CO2 content of about 3.5-4 vol % and a value of about 6.
For further treatment the aqueous medium containing carbon is sent to a main chamber, which is equipped with materials containing organic carbon compounds. Recovered paper stock containing lignin is preferably used here, which can be equally replaced by any plastic materials, pulp and/or waste substances containing aliphatic and/or aromatic carbon compounds. With participation of the ionized carbon-containing aqueous medium, polyreactions occur in the main chamber along with polymerizations and polycondensations with the organic with the organic carbon compounds of the recovered paper stock situated in it to form a carbon-enriched end product, which has a silicate fraction of about 20-25 vol % as support skeleton. The polyreaction in the main chamber preferably occurs at a temperature between 40 and 45° C. under a pressure of 7 to 8 bar. Under these pressure and temperature conditions the silicate fraction of the carbon-rich end product is finally also separable, which represents a basic raw material that can be used in a variety of ways. Through this processing of the exhaust gas flow a pure gas is finally achieved at the output from the main chamber, which has an average O2 content of 22 vol % and a CO2 content of 0.2 vol %.
By continuous measurement of the individual process parameters, like pressure, temperature, material amounts and compositions in the individual process steps optimization of the process and result is guaranteed.
Number | Date | Country | Kind |
---|---|---|---|
A 204/2012 | Feb 2012 | AT | national |
Filing Document | Filing Date | Country | Kind |
---|---|---|---|
PCT/AT2013/050037 | 2/13/2013 | WO | 00 |
Publishing Document | Publishing Date | Country | Kind |
---|---|---|---|
WO2013/123539 | 8/29/2013 | WO | A |
Number | Name | Date | Kind |
---|---|---|---|
6387212 | Christian | May 2002 | B1 |
6387337 | Pennline | May 2002 | B1 |
6537348 | Hirano | Mar 2003 | B1 |
7247601 | Hills | Jul 2007 | B1 |
8377408 | Dickinson, III | Feb 2013 | B2 |
8828338 | Lujano | Sep 2014 | B2 |
20040219090 | Dziedzic | Nov 2004 | A1 |
20040228788 | Nagai | Nov 2004 | A1 |
20060133982 | Kinloch | Jun 2006 | A1 |
20080121105 | Schubert | May 2008 | A1 |
20090120288 | Lackner | May 2009 | A1 |
20100150802 | Gilliam | Jun 2010 | A1 |
20100229725 | Farsad | Sep 2010 | A1 |
20110256049 | Dickinson, III | Oct 2011 | A1 |
20110277670 | Self | Nov 2011 | A1 |
20120189529 | Wakimoto | Jul 2012 | A1 |
20120211421 | Self | Aug 2012 | A1 |
20120238006 | Gartner | Sep 2012 | A1 |
20140338255 | Philipp | Nov 2014 | A1 |
Number | Date | Country | |
---|---|---|---|
20150018536 A1 | Jan 2015 | US |