Method and system for cogenerating gas-steam based on gasification and methanation of biomass
10113125 ยท 2018-10-30
Assignee
Inventors
Cpc classification
F22G1/02
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
C10L2200/0469
CHEMISTRY; METALLURGY
Y02E20/18
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
F22B27/14
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
C10L2290/10
CHEMISTRY; METALLURGY
Y02E20/16
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
Y02E50/30
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
F22B1/18
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
Y02P20/129
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
International classification
F22B27/14
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
F22B1/18
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
Abstract
A system for cogenerating gas-steam based on gasification and methanation of biomass, the system including a gasification unit, a shift unit, a purification unit, a methanation unit, and a methane concentration unit. A waste heat boiler is provided in an upper part of a gasifier of the gasification unit. The methanation unit includes a first primary methanation reactor, a second primary methanation reactor, a first secondary methanation reactor, and a second secondary methanation reactor connected in series. An outlet of the second primary methanation reactor is provided with two bypasses, one of which is connected to an inlet of the first primary methanation reactor, the other of which is connected to the first secondary methanation reactor. The second secondary methanation reactor is connected to the methane concentration unit.
Claims
1. A system for cogenerating gas-steam based on gasification and methanation of biomass, the system comprising: a gasification unit comprising a gasifier, the gasifier comprising an upper part that is disposed higher with respect to the ground than the remaining parts of the gasifier, a waste heat boiler, an external thermostatic heater, and an outlet segment; a shift unit; a purification unit; a methanation unit; and a methane concentration unit; wherein: the gasifier is adapted to yield a crude gasified gas; the waste heat boiler is connected to the upper part; the waste heat boiler is adapted to recycle waste heat of the crude gasified gas to yield a first intermediate pressure superheated steam; the external thermostatic heater is disposed at the outlet segment to keep a gasification temperature within the gasifier at 1,500-1,800 C.; and the purification unit is adapted to purify the crude gasified gas to yield a purified syngas.
2. The system of claim 1, wherein the methanation unit comprises a primary methanation unit and a secondary methanation unit; the primary methanation unit comprises a first primary methanation reactor comprising a first outlet and an inlet and a second primary methanation reactor comprising a second outlet, and the first primary methanation reactor and the second primary methanation reactor are connected in series; the secondary methanation unit comprises a first secondary methanation reactor and a second secondary methanation reactor connected in series; the second outlet is provided with two bypasses: one of the two bypasses is connected to the inlet of the first primary methanation reactor to yield a first mixed gas; the other of the two bypasses is connected to the secondary methanation unit to yield a second mixed gas; and the second secondary methanation reactor is connected to the methane concentration unit.
3. The system of claim 2, further comprising a first waste heat boiler, a first steam superheater, a second waste heat boiler, and a second steam superheater, wherein the first waste heat boiler and the first steam superheater are adapted to recycle reaction heat of the first mixed gas at the first outlet to generate a second intermediate pressure superheated steam; and the second waste heat boiler and the second steam superheater are adapted to recycle reaction heat of the second mixed gas at the second outlet to generate a third intermediate pressure superheated steam.
Description
BRIEF DESCRIPTION OF THE DRAWINGS
(1)
(2)
(3)
DETAILED DESCRIPTION OF THE EMBODIMENTS
(4) The invention is further illustrated in more detail in the light of the drawings and embodiments, which are not intended to define the protection scope of the invention.
(5) As shown in
(6) Step 1): Rice straw, crop stalk and other biomass were dried, crushed and sorted. Biomass raw material with the diameter or maximum length below 2 mm was directly transported to the gasifier of the high-temperature airflow bed through a screw feeder. The pressure in the gasifier was 1-3 MPa. An external thermostatic heater was provided in the outlet segment of the gasified gas of the biomass gasifier to keep the gasification temperature within the gasifier at 1,500-1,800 C., and guarantee the gasification intensity, gasified gas quality and strengthened heat transfer process. As the gasification agent, superheated water vapor and oxygen were premixed, and then fully mixed with the treated biomass. The mixture was injected into the gasifier with a special nozzle at a rate of 100-120 m/s for gasification by way of parallel flow. Due to small particle size and strong heat transfer ability of the airflow bed, raw material was heated to the furnace temperature as soon as it entered the furnace. Almost at the same time, there was moisture evaporation, volatile matter decomposition, tar cracking, carbon combustion and gasification. Alkali-containing metal ash was converted to liquid slag, and then directly discharged. Small biomass particles were retained in the reaction zone for less than 3s, rapidly gasified before melting, and respectively separated by the high-speed gas flow without the phenomenon of bonding and cohesion etc. Crude gasified gas from the side top of the gasifier was controlled at a temperature of 1,200-1,500 C. The upper part of the gasifier was provided with a waste heat boiler. The crude gasified gas from the gasifier entered the waste heat boiler to recover waste heat, and produced a lot of steam. After heat recovery, the gasified gas temperature dropped to 220-280 C. Then most dust and water vapor in the gasified gas were purified and cooled through two stage cyclone separators and a washing tower, so as to reduce the gasified gas temperature to about 50-55 C., reduce dust content to below 50 mg/m.sup.3, and generate the gasified gas mainly containing CO, H.sub.2 and N.sub.2.
(7) Step 2): After washing and dust removal, crude gasified gas entered the sulfur-tolerant shift process, the ratio of H.sub.2, CO and CO.sub.2 therein was adjusted to the hydrogen/carbon ratio of 3:1, and the vast majority of organic sulfur therein was converted into inorganic sulfur. Then the gas was purified, and washed with methanol at low temperature, so that methanol was used to remove unwanted CO.sub.2 and all sulfides from methanation reaction of the process gas, and the process gas composition achieved the methane production requirements. Methanol rich in CO.sub.2, H.sub.2S and COS was recycled by flash evaporation under reduced pressure and nitrogen stripping etc. and the cooling capacity therein was recovered for re-use.
(8) Step 3) methanation: The purified syngas in step 2) at adjusted hydrogen/carbon ratio can be divided into two approximately equal streams, which respectively entered the first primary methanation reactor and the second primary methanation reactor. Feed gas entering the first methanation reactor was first mixed with the recycle gas. The mixed gas at 300-330 C. entered the catalytic bed of the adiabatic reactor, wherein the exothermic methanation reaction occurred. Outlet temperature of the hot gas was about 600-630 C., and the hot gas was used to produce intermediate pressure superheated steam in the first waste heat boiler and superheat intermediate pressure superheated steam in the first superheater. The process gas from the first superheater was mixed with another stream of fresh feed gas. The mixed gas at 300-330 C. entered the second methanation reactor for further methanation reaction.
(9) Outlet temperature of the gas of the second primary methanation reactor was about 600-630 C., which was used to produce steam in the second waste heat boiler and preheat recycle gas in the second superheater. Hot process gas from the second waste heat boiler was divided into two streams: one stream accounted for 30-40%, and flowed to the first primary methanation reactor via a recycle compressor; another stream accounted for 60-70%, and entered the first secondary methanation reactor.
(10) Inlet temperature of the feed gas of the second secondary methanation reactor was 270-290 C., and further methanation reaction occurred in the second secondary methanation reactor, in order to achieve the specification of SNG product. Intermediate pressure superheated steam generated from the methanation reaction was transported to the steam turbine.
(11) Pressure of the intermediate pressure superheated steam that was generated by the waste heat boiler and steam superheater using the recycling reaction heat in the primary methanation reaction stage was 4.5-5 MPa.
(12) The methanation was carried out with high-load nickel as the catalyst, at the reaction temperature of 270-630 C., under the pressure of 1-3 MPa, and following
CO+3H.sub.2.fwdarw.CH.sub.4+H.sub.2O H.sub.0.sup.=206 kJ/mol.
(13) Step 4) Methane concentration: After methane was concentrated through pressure swing adsorption of crude natural gas, substituent natural gas following national standard was obtained. In general, the natural gas enters the urban gas pipeline as domestic gas, and may also enter the gas turbine to generate electricity in case of power shortage.
(14) As shown in
(15) As shown in
(16) As shown in
(17) Reaction heat of the mixed gas at the outlet of the first primary methanation reactor is recycled by the first waste heat boiler and the steam superheater, and that of the mixed gas at the outlet of the second primary methanation reactor is recycled by the second waste heat boiler and the steam superheater. The intermediate pressure superheated steam generated therefrom is transported to the steam turbine.
EXAMPLE 1
(18) Calculation of the overall system performance under the basic load with 1,000 tons/day raw material biomass.
(19) Dry rice straw is used as the gasification biomass in Example 1. Its ingredients and calorific value are shown in Table 1.
(20) TABLE-US-00001 TABLE 1 Ingredients and calorific value of biomass Items Content Unit Rice straw calorific value Qar, net MJ/kg 11.346 Elements Carbon Car % 37.162 Hydrogen Har % 2.748 Oxygen Oar % 35.136 Nitrogen Nar % 0.905 Sulfur Sar % 0.029
(21) In example 1, biomass 1000 tons/day, and the gasification agent comprising 93 vol. % of oxygen is employed for gasification.
(22) TABLE-US-00002 TABLE 2 Material balance and performance parameters of gas product Example 1 Gasified gas Shift gas Syngas Gas product Rate of flow Nm.sup.3/h 43960 53320 29300 7350 Percentage vol. % CO 43.41% 12.03% 20.36% 0.01% H.sub.2 16.42% 37.30% 67.53% 0.30% N.sub.2 5.77% 4.76% 8.04% 1.17% CO.sub.2 21.19% 41.23% 1.88% 1.13% CH.sub.4 1.92% 1.59% 2.16% 96.13% H.sub.2O 9.29% 1.45% 0.03% 1.26% C.sub.2C.sub.4 1.92% 1.59% 0.00% 0.00% Caloric value of syngas kcal/m.sup.3 2579 8227 Yield of syngas m.sup.3/d 176400 Chemical synthesis efficiency from biomass to syngas 47% (chemical energy of SNG/biomass chemical energy of biomass) Steam from methanation 450 C., 4.7 MPa (t/h) 21.45
EXAMPLE 2
(23) Biomass 1000 tons/day, and the gasification agent comprising 98 vol. % of oxygen is employed for gasification.
(24) TABLE-US-00003 TABLE 3 Material balance and performance parameters of gas product Example 2 Gasified gas Shift gas Syngas Gas product Rate of flow Nm.sup.3/h 51140 64640 39670 10190 Percentage vol. % CO 52.10% 14.46% 21.91% 0.01% H.sub.2 22.81% 44.81% 72.66% 0.20% N.sub.2 2.02% 1.60% 2.48% 2.00% CO.sub.2 12.55% 36.70% 1.79% 0.28% CH.sub.4 1.17% 0.92% 1.13% 96.47% H.sub.2O 9.27% 1.45% 0.02% 1.03% C.sub.2C.sub.4 0.02% 0.01% 0.00% 0.00% Caloric value of syngas kcal/m.sup.3 2672 8256 Yield of syngas m.sup.3/d 244560 Chemical synthesis efficiency from biomass to syngas 64% (chemical energy of SNG/biomass chemical energy of biomass) Steam from methanation 450 C., 4.7 MPa (t/h) 30.90