The present application is a national stage of and claims priority of International patent application Serial No. PCT/EP2016/056668, filed Mar. 24, 2016, and published in English as WO/2016/151120A1.
The invention relates to a method of and a system for processing a slurry containing organic components, such as biomass, having a water contents of at least 50%, preferably at least 60%, preferably at least 70%. The invention relates in particular to a method and a system for supercritical water gasification (SCWG) of organic components in a slurry.
Feedstocks containing organic components are a tremendous potential resource for providing energy and value-added products, especially in agricultural areas where waste biomass is abundant or where dedicated energy crops can be produced cheaply and efficiently.
An improved method of and system for processing, preferably in a continuous process, a slurry containing organic components, such as biomass, to produce combustible gas, e.g. hydrogen and/or hydrocarbons is disclosed.
The method comprises:
increasing the pressure and temperature of the slurry to bring the liquid in the slurry in a supercritical state, typically by first increasing one of pressure and temperature beyond the supercritical threshold (for water: 221 bar and 374° C., respectively) and then increasing the other of pressure and temperature beyond the supercritical threshold,
converting at least a part of the organic components in the slurry, e.g. to combustible gaseous products, e.g. to hydrogen and/or hydrocarbons, such as methane, e.g. by further heating the stream in a reactor, and
separating gaseous products from the converted slurry, and
mixing fluid, e.g. liquid water, water in a (near) supercritical state and/or a liquid fuel, with the slurry before converting at least a part of the organic components in the slurry.
In an embodiment, the method comprises mixing fluid from the converted slurry with the upstream slurry, preferably after the fluid from the converted slurry has been de-pressurized and/or cooled to a pressure and/or temperature below the critical pressure and/or critical temperature and/or preferably before the liquid in the (upstream) slurry is brought in a supercritical state, preferably before the liquid in the (upstream) slurry is pressurized above critical pressure and/or heated to a temperature above the critical temperature.
In another embodiment, the fluid mixed with the slurry is taken from an external source, e.g. a neighbouring plant.
The method enables processing of feedstocks with a relatively high contents of organic components and/or solids, provides efficient heat recovery and/or enhances subsequent pumping and heat exchange by reducing viscosity of the slurry and/or enhancing mixing.
In an embodiment, the method comprises separating gaseous products and/or solids from the fluid in the converted slurry and mixing the fluid thus obtained with the upstream slurry.
In another embodiment, to further improve overall heat recovery, the method comprises exchanging heat between the (relatively hot) converted slurry and the (relatively cold) slurry before conversion, preferably after the latter has been mixed with fluid from the converted slurry.
In a refinement, heat is exchanged between the converted slurry and the upstream slurry to heat the latter to a temperature above the critical temperature.
In an embodiment, the method comprises reducing the percentage of water in the slurry, preferably by dewatering the slurry and/or by adding a substance containing less water than the initial slurry, preferably at least before mixing the slurry with fluid from the converted stream. In a refinement, the slurry is dewatered to a total solids contents of at least 20%, preferably at least 30%, preferably at least 40%. First removing liquid from the feedstock and then adding fluid from the process appeared to be an effective means to further increase process efficiency.
In an embodiment, to increase the caloric value of the slurry, the method comprises adding a fuel, e.g. a solid fuel such as (powdered) coal or a liquid fuel such as an alcohol, e.g. glycerol, or a hydrocarbon, e.g. paraffin, to the slurry, before converting at least a part of the organic components in the slurry. The fuel can double as a means to reduce the percentage of water in the slurry.
A system for processing a slurry containing organic components, such as biomass, having a water contents of at least 50%, preferably at least 60%, preferably at least 70%, includes a pump and heater or heat exchanger to bring the liquid in the slurry in a supercritical state. A reactor converts at least a part of the organic components in the slurry. A separator removes gaseous products from the converted slurry. A mixer adds fluid, preferably fluid from the converted slurry, to the slurry upstream from the reactor.
In an embodiment, the downstream end of the reactor is connected, preferably via at least a separator, to the mixer.
In another embodiment, the mixer is located upstream from at least one of the pump and the heater or heat exchanger for bringing the liquid in the slurry in a supercritical state.
In another embodiment, the system comprises a separator for removing gaseous products and/or a separator for removing solids from the fluid in the converted slurry.
In another embodiment, the system comprises a heat exchanger for transferring heat from the converted slurry to the non-converted slurry and located upstream from the reactor and preferably located downstream from the mixer.
In another embodiment, the system comprises a solid-liquid separator, a screw press, filter press, centrifuge, or dryer, to dewater the feed slurry and preferably located upstream from the mixer.
In another embodiment a system includes a pump for pressurizing the liquid in the slurry to a supercritical pressure, a heater or heat exchanger, a reactor, and a separator as specified above, wherein the pump is an hydraulic pump and comprises a circuit for a cooling medium, which circuit separates the hydraulic medium from the slurry, thus providing effective cooling and reducing the risk of contamination, in case of a leak, of the hydraulic medium with the slurry or vice versa.
Aspects of the invention will now be explained in more detail with reference to the figures, which schematically show an embodiment.
The downstream end of the reactor and optionally also of the (first) heat exchanger is connected to a solids trap 9 to remove solids, such as inorganics and/or precipitated minerals and salts, from the system.
In a first embodiment, indicated by a solid line 10 in
In a second embodiment, indicated by a dotted line 11 in
As shown in more detail in
During operation, in an example, wet biomass (manure) having a water content of 80% is dewatered by means of a screw press 2 to a water content of 70% (totals solids 30%) and the thickened and viscous slurry is fed to the tank 3. From there, the slurry is pumped (at 1000 liters/hour, 15-20 bar, and 15° C.) to the mixer 5 and mixed with water (750-1250 nL/h, 15-30 bar, and 250-300° C.) from the downstream, processed slurry, to a water content of 83-87% and a volume of 1750-2250 nL/h. The slurry is then pressurized and heated (240-250 bar, and 370-390° C.) and fed to the reactor, where the slurry is further heated (to 550-600° C.) to convert at least a part of the organic components in the slurry to gaseous product, e.g., hydrogen and methane. After conversion, solids are removed from slurry in a solids trap and the water is fed to the first heat exchanger 7 to recover high temperature heat, i.e. to heat the colder upstream slurry. After leaving the heat exchanger (at 1750-2250 nL/h, 240-250 bar, and 250-300° C.), the liquid is fed to the gas/liquid separator to allow the gaseous product to escape and to enable collection. Part of the remaining water is discharged from the system and part of the remaining water (750-1250 nL/h) is mixed with the upstream slurry.
The method and system enables processing of feedstocks with a relatively high contents of organic components and/or solids, provides efficient heat recovery and/or enhances subsequent pumping and heat exchange by reducing viscosity of the slurry and/or enhancing mixing.
The invention is not restricted to the above-described embodiments, which can be varied in a number of ways within the scope of the claims.
Number | Date | Country | Kind |
---|---|---|---|
15161194 | Mar 2015 | EP | regional |
Filing Document | Filing Date | Country | Kind |
---|---|---|---|
PCT/EP2016/056668 | 3/24/2016 | WO |
Publishing Document | Publishing Date | Country | Kind |
---|---|---|---|
WO2016/151120 | 9/29/2016 | WO | A |
Number | Name | Date | Kind |
---|---|---|---|
4113446 | Modell et al. | Sep 1978 | A |
4338199 | Modell | Jul 1982 | A |
5543057 | Whiting | Aug 1996 | A |
20060096163 | Dickinson | May 2006 | A1 |
20100287825 | Humphreys | Nov 2010 | A1 |
20110127778 | Kinney | Jun 2011 | A1 |
Number | Date | Country |
---|---|---|
101818079 | Sep 2010 | CN |
101827645 | Sep 2010 | CN |
202688157 | Jan 2013 | CN |
103936251 | Jul 2014 | CN |
104030427 | Sep 2014 | CN |
104355519 | Feb 2015 | CN |
S57-004225 | Jan 1982 | JP |
H09-511678 | Nov 1997 | JP |
2000-033355 | Feb 2000 | JP |
2001115174 | Apr 2001 | JP |
2003-106164 | Apr 2003 | JP |
2003-117597 | Apr 2003 | JP |
2004-300254 | Oct 2004 | JP |
2006021069 | Jan 2006 | JP |
2008-249207 | Oct 2008 | JP |
8103169 | Nov 1981 | WO |
2009015409 | Feb 2009 | WO |
WO-2010003655 | Jan 2010 | WO |
20160151120 | Sep 2016 | WO |
WO 2010003655 | Jan 2019 | WO |
Entry |
---|
Hong et al. (Supercritical water partial oxidation, Proceedings of the 2002 U.S. Doe Hydrogen Program Review) (Year: 2002). |
Reddy et al. (Supercritical water gasification of biomass for hydrogen production, International Journal of Hydrogen Energy, vol. 39 (2014), pp. 6912-6926) (Year: 2014). |
International Search Report dated May 23, 2016 for corresponding International Application PCT/EP2016/056668 filed Mar. 24, 2016. |
Written Opinion of the International Searching Authority dated Sep. 29, 2016 for corresponding International Application PCT/EP2016/056668, filed Mar. 24, 2016. |
Bermejo, M.D. et al. “Supercritical Water Oxidation: A Technical Review”. AlChE Journal, Nov. 2006, vol. 52, No. 11, pp. 3933-3951. |
Kruse, A., “Supercritical water gasification”, Society of Chemical Industry and John Wiley & Sons, Ltd, 2008, pp. 415-437. |
Marrone, Ph. A., “Supercritical water oxidation—Current status of full-scale commercial activity for waste destruction”, Journal of Supercritical Fluids 79 (2013), pp. 283-288. |
IBoukis, N., et al. “Biomass gasification in supercritical water. Experimental progress achieved with the VERENA pilot plant.” 15th European Biomass Conference & Exhibition 2007. |
Table 15.10 from “Innovative Wastewater Treatment and Resource Recovery Technologies” (Juan M Lema and Sonia Suarez, 2017). |
Pages 407, 409, and 618 from “Supercritical Fluid Technology for Energy and Environmental Applications” (Vladimkr Anikeev and Maohong Fan, 2014). |
Report prepared by General Atomics for the United States Department of Energy. Jan. 2005. |
European Office Action, mailed Feb. 28, 2019 for corresponding European Patent Application No. 16716832.0, filed Mar. 24, 2016. |
Russian Office Action from the Patent Office of the Russian Federation for application No. 2017134428/05 (060594), mailed May 21, 2019. |
Australian Examination Report from the Australian Patent Office for Australian patent application No. 2016238748, published Sep. 14, 2017, mailed Jun. 10, 2020. |
First Office Action from Chinese Patent Office for Chinese patent application No. 201680017560.5, Jun. 18, 2020. |
Brazilian Office Action dated Jan. 27, 2020, for corresponding Brazilian Patent Application No. 112017019837-1, filed Mar. 24, 2016. |
Notice of Reasons for Rejection for Japanese patent application No. 2017-550606, mailed Feb. 3, 2020, with English translation. |
Examination Report for Indian patent application No. 201747030214, mailed Jan. 31, 2020. |
Chinese Office Action for Chinese patent application No. 201680017560.5, mailed Mar. 5, 2021, with English translation. |
Japanese Office Action for Japanese patent application No. 2017-550606, mailed Feb. 1, 2021, with English translation. |
Number | Date | Country | |
---|---|---|---|
20180119038 A1 | May 2018 | US |