METHOD TO MAXIMIZE ENERGY RECOVERY IN WASTE-TO-ENERGY PROCESS
20170254228 · 2017-09-07
Assignee
Inventors
Cpc classification
F23G5/46
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
F01K25/08
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
F23G5/16
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
Y02E20/12
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
F01K13/02
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
International classification
F01K25/08
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
F23G5/46
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
F23G5/16
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
Abstract
In a fossil fuel waste incineration or plasma gasification process, waste heat generated by combustion of waste is captured by a heat transfer fluid and conveyed to an Organic Rankine Cycle (ORC) for energy recovery. In the case of a fossil fuel-fired waste incineration system, the heat transfer fluid captures waste heat from a double-walled combustion chamber, a heat exchanger being used to cool the hot process exhaust (gas cooler). In the case of a plasma waste gasification system, the heat transfer fluid captures waste heat from a plasma torch, a gasification chamber and combustion chamber cooling jackets as well as any other high-temperature components requiring cooling, and then a heat exchanger used to cool the hot process exhaust (gas cooler). The heat exchanger may take on several configurations, including plate or shell and tube configurations.
Claims
1. A fossil fuel waste incineration or plasma gasification process, wherein waste heat generated by a combustion of waste is captured by a heat transfer fluid and conveyed to an Organic Rankine Cycle (ORC) for energy recovery.
2. A process according to claim 1, wherein, in a fossil fuel-fired waste incineration system, the heat transfer fluid captures waste heat from a double-walled combustion chamber, a heat exchanger being used to cool the hot process exhaust (gas cooler).
3. A process according to claim 2, wherein the heat exchanger comprises a plate or a shell and tube configuration.
4. A process according to claim 1, wherein, in a plasma waste gasification system, the heat transfer fluid captures waste heat from at least one of a plasma torch, a gasification chamber cooling jacket and a combustion chamber cooling jacket, and a heat exchanger being then used to cool the hot process exhaust (gas cooler).
5. A process according to claim 4, wherein the heat transfer fluid further captures waste heat from any other high-temperature components requiring cooling.
6. A process according to claim 4, wherein, wherein the heat exchanger comprises a plate or a shell and tube configuration.
7. A process according to claim 1, wherein the hot heat transfer fluid exits the exhaust heat exchanger and is fed to an Organic Rankine Cycle (ORC) evaporator, the thermal energy carried thereby being transferred to the refrigerant for conversion into electricity.
8. A process according to claim 1, wherein the hot heat transfer fluid is fed to a separate, secondary heat exchanger until an appropriate temperature has been reached for proper operation of the ORC or in case of a process and ORC unit malfunction.
9. A control strategy according to claim 8, wherein the temperature of the heat transfer fluid is monitored and the fluid is fed to the ORC evaporator system or to the secondary heat exchanger system based on whether or not the temperature of the fluid falls within an operating temperature of the ORC system, allowing the heat transfer fluid to be fed to the secondary heat exchanger in case of ORC system failure thus allowing the waste destruction system to continue operating without interruption.
10. A process of operating a waste destruction system at a higher shell temperature to allow for the generation of a useful hot liquid resource, using high temperature polymeric material in plasma torch components and insulation of the hot components of the system.
11. A process according to claim 1, wherein the waste thermal energy in the process is recovered by cooling of the various thermal components with the liquid and by using the liquid to quench the hot process exhaust.
12. A process according to claim 11, wherein energy is recovered from the heated liquid following a filtration step to remove any entrapped ash.
13. A method, wherein waste thermal energy in a fossil fuel waste incineration or plasma gasification process is recovered by cooling of the various thermal components with a liquid and by using the liquid to quench the hot process exhaust.
14. A method according to claim 13, wherein energy is recovered from the heated liquid following a filtration step to remove any entrapped ash.
15. A method, wherein the waste thermal energy in a fossil fuel waste incineration or plasma gasification process is recovered by cooling of the various thermal components with a fluid and by using the fluid to indirectly cool the recirculated filtered quench water.
16. A process according to claim 1, wherein the waste thermal energy in the process is recovered by cooling of the various thermal components with a fluid and by using the fluid to indirectly cool the recirculated filtered quench water.
17. A process according to claim 1, wherein the hot liquid, containing the thermal energy recovered from heated parts of the waste destruction system, can be used as a resource for other surrounding processes.
18. A process according to claim 1, wherein the method is used as a way of preheating water for use in a boiler, if the option of steam generation is retained.
Description
BRIEF DESCRIPTION OF THE DRAWINGS
[0014] Reference will now be made to the accompanying drawings, showing by way of illustration an illustrative embodiment of the present invention, and in which:
[0015]
[0016]
[0017]
[0018]
[0019]
DESCRIPTION OF ILLUSTRATIVE EMBODIMENTS OF THE INVENTION
[0020] In order to address the issue of waste thermal energy in waste destruction systems, a method by which the majority of the waste heat is captured by a heat transfer fluid and conveyed to the ORC for energy recovery is hereby presented.
[0021] In the case of a fossil fuel-fired incineration system, as illustrated in
[0022] In the case of a plasma waste gasification system, as illustrated in
[0023] In both cases (incineration and plasma gasification systems), the heated fluid exits the exhaust heat exchanger and is fed to the ORC evaporator 26. The thermal energy it carries is transferred to the refrigerant for conversion into electricity. The heat transfer fluid returns, cooled, to the reservoir 8, 16 from which it was initially pumped.
[0024] In both cases (incineration and plasma gasification systems), the heated fluid can be alternatively fed to a separate, secondary heat exchanger 27 until the appropriate temperature has been reached for proper operation of the ORC (ORC units do, however, have a much larger operating window compared to steam Rankine cycles—better turn-down capabilities). This separate heat exchanger 27 may also be used in case of malfunction in the ORC unit or in case of a process temperature excursion (if the heated fluid temperature exceeds the design parameters of the ORC). The general control philosophy of the system is illustrated in
[0025] Given the ORC's typical hot liquid resource operating range (from 90° C. to 150° C.), the choice of heat transfer liquid increases. Water may be used as the heat transfer fluid when operating with a maximum temperature below 100° C. However, water offers little margin for error in case of process temperature excursions: should the water temperature spike above the boiling point within conduits that are not pressure-rated, the resulting pressure increase (from the phase change) could damage equipment. Alternatively, fluids such as ethylene glycol, propylene glycol or thermal oils may be used. These fluids offer significant advantages over water including higher operating temperatures, decreased corrosion and lower electrical conductivity (especially important in the case of plasma torch cooling). At higher operating temperatures, the fluid requirements for optimal ORC operation decrease. In the operating temperature range for the ORC, these fluids have comparable viscosity to that of water, thus no special considerations are required with regards to pumping (though fluid preheating is recommended at startup). There is one minor disadvantage to using such alternate fluids instead of water: their heat capacity is typically lower than that of water, thus slightly decreasing the overall efficiency of the process. in order to address this shortcoming, several methods may be applied. The heat transfer properties can be improved by using mixtures of water and the thermal fluid (if the two fluids are miscible). Also, some additives can be added to the thermal fluid to improve its thermal properties (for example, adding nanoparticles has been demonstrated to increase the thermal conductivity of the resulting fluid—a nanofluid).
[0026] This method implicitly requires operating the various thermal components of the waste destruction system at higher-than-normal temperatures. As an illustrative example, for the ORC evaporator inlet temperature to be 150° C., the temperature of the fluid when cooling the thermal components (such as the plasma torch, the combustion chamber, etc.) will be in the order of 100° C. At such a high operating temperature, some precautions must be taken into consideration: [0027] in order to meet IMO regulations (if operating on a marine vessel), the thermal sections will have to be insulated in order to maintain the system's outer surface at a temperature of 60° C. or less. The heat transfer fluid reservoir must also be insulated appropriately (e.g.: using fiberglass insulation, etc.). [0028] seals, o-rings and other gasket material must be selected appropriately to ensure that they are rated for the higher operating temperature (e.g.: graphite gaskets, viton o-rings, etc.). [0029] in the case of plasma gasification, the various electrical insulators in the plasma torch need to be constructed from high temperature polymers such as, for example, PEEK or VESPEL™. [0030] no matter what the temperature of the heat transfer fluid, the material of construction of the liquid-cooled component must be chemically compatible with the heat transfer fluid selected. For example, untreated carbon steel would be an inappropriate material choice for water cooling, given that corrosion would occur (stainless steel would be a more appropriate choice). On the other hand, a thermal fluid with corrosion-inhibiting additives (such as the DowFrost™ propylene glycol mixture) would be appropriate for use with carbon steel. [0031] also, no matter what the temperature of the heat transfer fluid, the use of a heat resistant or high-temperature alloy liner (e.g.: Inconel, Hastelloy, etc.) is used inside the combustion chamber in order to extend the lifetime of that chamber's inner wall (which would be subjected to high temperature gradients and, consequently, uneven thermal expansion and contraction).
[0032] This energy recovery method can be applied to a system in which a liquid quench is used to rapidly cool down the combustion chamber exhaust. A liquid quench is particularly important in cases where chlorinated plastics are combusted or gasified—processing such plastics can lead to the formation of toxic compounds (e.g.: dioxins, furans) if strict temperature control is not enforced. The application of this cooling method is illustrated in
[0033] In an alternate configuration, the gas is quenched with fresh cold water to provide enough heat for adiabatic cooling of the gas. This fresh water is fed to the top of the quench through pressure nozzles. Additional water is used in a recycled loop using a recirculation pump, an inline filter, either a back flush strainer or a bag type filter, and a different set of nozzles in the quench. The filter is used to remove any entrained particulates from the gas stream that have been captured by the quench water. A Venturi separator can also be used downstream of the quench to remove additional particulates from the gas stream. In this case, part of the filtered recirculated water is also injected into the Venturi through a series of nozzles. The recirculated hot water can be used to heat the ORC fluid indirectly through a heat exchanger.
[0034] Therefore, in the present method, the majority of the wasted thermal energy, typically lost to cooling water, is recovered by cooling the process thermal sections with a higher temperature fluid, which can then be fed to an ORC unit for conversion to electrical energy.
[0035] Also, in the present method, the wasted thermal energy in the process is recovered by cooling of the various thermal components with a liquid (as just above) and by using this liquid to quench the hot process exhaust. Energy is recovered from this heated liquid following a filtration step to remove entrapped ash.
[0036] Furthermore, the present method involves operating the waste destruction system at a higher shell temperature to allow for the generation of a useful hot liquid resource. This method thus requires the modification and insulation of these components to meet regulatory needs.
[0037] Moreover, in the present control strategy, the temperature of the heat transfer fluid is monitored and the fluid is fed to the ORC evaporator system or to a secondary heat exchanger system based on whether or not the temperature of the fluid falls within the operating temperature of the ORC system. The heat transfer fluid can also be fed to the secondary heat exchanger should the ORC system fail for any reason. Thus, the waste destruction system can continue to operate without interruption even if the ORC is out of range or out of order.
[0038] In addition, while the method described is used to supply a hot liquid resource to the ORC unit for energy recovery in the form of electricity, it is not limited to use with the ORC. The hot liquid, containing the thermal energy recovered from heated parts of the waste destruction system, can be used as a resource for other surrounding processes. This method can also be used as a way of preheating water for use in a boiler, if the option of steam generation is retained (particularly in the case of larger scale systems). The heated water generated when the secondary heat exchanger is in use may also be used as a hot liquid resource for other process components or space heating requirements.
[0039] Although the present invention has been described hereinabove by way of embodiments thereof, it may be modified, without departing from the nature and teachings of the subject invention as described herein.