CN205850588U - A kind of biogas dry method desulfuration system - Google Patents

A kind of biogas dry method desulfuration system Download PDF

Info

Publication number
CN205850588U
CN205850588U CN201620595613.9U CN201620595613U CN205850588U CN 205850588 U CN205850588 U CN 205850588U CN 201620595613 U CN201620595613 U CN 201620595613U CN 205850588 U CN205850588 U CN 205850588U
Authority
CN
China
Prior art keywords
desulfurizing tower
pipe
biogas
dry method
saturator
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
CN201620595613.9U
Other languages
Chinese (zh)
Inventor
龚立人
李星勇
林顺富
邵云龙
洪俊杰
陈天富
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Songming Run Agricultural Environmental Protection Technology Co Ltd
Original Assignee
Songming Run Agricultural Environmental Protection Technology Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Songming Run Agricultural Environmental Protection Technology Co Ltd filed Critical Songming Run Agricultural Environmental Protection Technology Co Ltd
Priority to CN201620595613.9U priority Critical patent/CN205850588U/en
Application granted granted Critical
Publication of CN205850588U publication Critical patent/CN205850588U/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Gas Separation By Absorption (AREA)

Abstract

The utility model discloses a kind of biogas dry method desulfuration system, including saturator, desulfurizing tower A, desulfurizing tower B and decontaminating separator, the low side of saturator is provided with biogas input pipe, high-end it is provided with escape pipe, the escape pipe of saturator air inlet pipe with desulfurizing tower A and desulfurizing tower B low side respectively is connected, desulfurizing tower A and the high-end of desulfurizing tower B are provided with exhaustor, the low side of decontaminating separator is provided with purification gas inlet tube, high-end it is provided with clean gas outlet pipe, it is connected with purification gas inlet tube again after the exhaustor parallel connection of desulfurizing tower A and desulfurizing tower B, purify gas inlet tube to be connected with clean gas outlet pipe by the 4th bypass pipe.It is short that this utility model provides a kind of flow process, and simply, work device structure continuous-stable, and desulfuration efficiency is high, the biogas dry method desulfuration system that gas purification degree is high.

Description

A kind of biogas dry method desulfuration system
Technical field
This utility model belongs to desulfurization by dry method field, is specifically related to a kind of biogas dry method desulfuration system.
Background technology
Yunnan Province is the big province of growing vegetables, and vegetable can produce discarded fruit and vegerable in plantation, sales section, only has little portion at present Divide discarded fruit and vegerable to be used as feedstuff, remaining utilization the most not yet in effect, be arbitrarily discarded in village, field, bring serious environmental problem. In order to solve numerous environmental problems that local discarded fruit and vegerable bring, discarded fruit and vegerable are turned waste into wealth, people using discarded fruit and vegerable as Raw materials for production, prepare biogas by dry anaerobic fermentation, biogas by bioanalysis desulfurization, decarburization, be dried, pressurization after as car Supply market with compressed natural gas (or CNG), comprehensively solve local environment and pollute and industrial gas problem, and periphery is saved City's agricultural waste utilization, energy development will play good demonstration and guiding function.During wherein biogas desulfurization is this technique One the most key link, desulfurization processes bad, environment can be caused secondary pollution, be unfavorable for environmental protection.The most conventional place Reason method has wet desulphurization and biological desulphurization.What wet desulphurization used that sodium carbonate, ammonia and alkanolamine solution etc. absorb hydrogen sulfide is Chemical absorption method;With cold methanol absorb hydrogen sulfide for Physical Absorption method;Employing alkaline solution is absorbent, and adds oxygen carrier For desulfurizing agent, absorb hydrogen sulfide.Biological desulphurization is by being imported by a certain amount of air in the biogas containing hydrogen sulfide, utilizes raw The process of thing reaction biological removal hydrogen sulfide.All there are long flow path, installations and facilities bulky complex, operation fiber crops in both sulfur methods Tired, and be only suitable for processing the higher flue gas of sulfur content or combustion gas.But for using discarded fruit and vegerable as anaerobic fermentation raw material, send out For the biogas that after ferment, the sulfur content in biogas is relatively low, there will be desulfuration efficiency according to wet method and biological two kinds of sulfur methods low Under, desulfurized effect is poor, purifies halfway problem.Therefore, developing a kind of flow process short, device structure is simple, and work continuous-stable, Desulfuration efficiency is high, and the biogas dry method desulfuration system that gas purification degree is high is desirability.
Utility model content
The purpose of this utility model is to provide a kind of flow process short, and device structure is simple, and work continuous-stable, desulfuration efficiency Height, the biogas dry method desulfuration system that gas purification degree is high.
The purpose of this utility model is achieved in that and includes saturator, desulfurizing tower A, desulfurizing tower B and decontaminating separator, The low side of saturator is provided with biogas input pipe, the high-end escape pipe that is provided with, and is provided with between biogas input pipe and escape pipe Bypass line, the escape pipe of saturator air inlet pipe with desulfurizing tower A and desulfurizing tower B low side respectively is connected, desulfurizing tower A and desulfurizing tower The high-end exhaustor that is provided with of B, the low side of decontaminating separator is provided with purification gas inlet tube, high-end is provided with clean gas outlet Pipe, is connected with purification gas inlet tube after the two exhaustor parallel connections of desulfurizing tower A and desulfurizing tower B, the exhaustor of desulfurizing tower A and desulfurization again The air inlet pipe of tower B is connected by the second bypass pipe, and the exhaustor of desulfurizing tower B passes through the 3rd bypass pipe with the air inlet pipe of desulfurizing tower A Connect, purify gas inlet tube and be connected with clean gas outlet pipe by the 4th bypass pipe.
The exhaustor of desulfurizing tower A is connected with the air inlet pipe of desulfurizing tower B by this utility model by the second bypass pipe, desulfurizing tower Exhaustor the 3rd bypass pipe of B passes through to be connected with the air inlet pipe of desulfurizing tower A.Two towers are conducive in process of production after so connecting Phase double replacement, it is ensured that the seriality of desulfurization process.This is because the desulfurizing agent in desulfurizing tower is after the regeneration of 3~5 times, desulfurization Agent chemism is substantially reduced, and needs the desulfurizing agent more renewed.After so arranging when changing the desulfurizing agent of arbitrary tower in two towers, All ensure that what desulfurization worked is normally carried out continuously, will not influence each other.It addition, this utility model arranges saturated in two tower front ends Tower, can make biogas be introduced into after saturator reaches water saturation and enter back into desulfurizing tower, so be conducive to accelerating desulphurization reaction, improves Desulfuration efficiency.Meanwhile, this utility model also arranges decontaminating separator at the afterbody of two desulfurizing towers, so can remove clean further The desulfurization dust carried in activating QI body, the purity making purification gas is higher.Therefore, this utility model is that a kind of flow process is short, equipment Simple in construction, work continuous-stable, and desulfuration efficiency is high, and the biogas dry method desulfuration system that gas purification degree is high is worth of widely use.
Accompanying drawing explanation
Fig. 1 is overall structure schematic diagram of the present utility model;
In figure: 1-biogas input pipe, 2-the first bypass pipe, 3-saturator, 4-diffuses house steward, 5-escape pipe, 6-air inlet pipe, 7-diffuses arm, 8-ladder, 9-operating platform, 10-desulfurizing agent lifting device, 11-desulfurizing tower A, 12-exhaustor, 13-desulfurization Tower B, 14-decontaminating separator, 15-clean gas outlet pipe, 16-purifies gas inlet tube, 17-blow down branch, 18-blowdown main, 19- 4th bypass pipe, 20-the 3rd bypass pipe, 21-the second bypass pipe.
Detailed description of the invention
Below in conjunction with the accompanying drawings this utility model is further described, but never in any form to this utility model in addition Limit, any change made based on this utility model training centre or improvement, belong to protection domain of the present utility model.
As it is shown in figure 1, this utility model includes saturator 3, desulfurizing tower A11, desulfurizing tower B13 and decontaminating separator 14, full The low side of tower 3 is provided with biogas input pipe 1, the high-end escape pipe 5 that is provided with, is provided with between biogas input pipe 1 and escape pipe 5 First bypass pipe 2, the escape pipe 5 of saturator 3 air inlet pipe 6 with desulfurizing tower A11 and desulfurizing tower B13 low side respectively is connected, desulfurization The high-end exhaustor 12 that is provided with of tower A11 and desulfurizing tower B13, the low side of decontaminating separator 14 is provided with purification gas inlet tube 16, The high-end clean gas outlet pipe 15 that is provided with, after exhaustor 12 parallel connection of desulfurizing tower A11 and desulfurizing tower B13 again with purify gas inlet tube 16 connect, and the exhaustor 12 of desulfurizing tower A11 is connected by the second bypass pipe 21 with the air inlet pipe 6 of desulfurizing tower B13, desulfurizing tower B13 The air inlet pipe 6 of exhaustor 12 and desulfurizing tower A11 be connected by the 3rd bypass pipe 20, purify gas inlet tube 16 by the 4th bypass Pipe 19 is connected with clean gas outlet pipe 15.
Further, each on biogas input pipe 1, saturator 3, desulfurizing tower A11, desulfurizing tower B13 and decontaminating separator 14 Diffuse arm 7 from being provided with, respectively diffuse arm 7 connection and diffuse house steward 4.So that people at repair apparatus or carry out special operational Time, the gas remained in each equipment can be emptied, it is ensured that the safety of staff.
Further, in order to get rid of each device interior residual sewage, saturator 3, desulfurizing tower A11, desulfurizing tower B13 and The bottom of decontaminating separator 14 is each provided with blow down branch 17, and each blow down branch 17 connects blowdown main 18.
Further, in order to ensure that whole desulphurization system works the most in an orderly manner, biogas input pipe 1, diffuse house steward 4, put Dissipate arm 7, air inlet pipe 6, escape pipe 5, exhaustor 12, clean gas outlet pipe 15, purify gas inlet tube 16, blow down branch 17, row All it is each provided with and manages on dirty house steward the 18, the 4th bypass pipe the 19, the 3rd bypass pipe the 20, second bypass pipe the 21, first bypass pipe 2 The valve that subtype number is suitable.
Further, operation when two desulfurizing towers change desulfurizing agent or add catalyst for convenience, at desulfurizing tower A11, take off The top of sulfur tower B13 is provided with operating platform 9, operating platform 9 be provided above desulfurizing agent lifting device 10, operating platform 9 Lower section be provided with ladder 8.
The method that this utility model uses double tower in parallel carries out desulfurization, and double tower includes desulfurizing tower A11 and desulfurizing tower B13, In two towers, filling desulfurizing agent, is added with multiple catalysts in desulfurizing agent, its active component and H in biogas2S contact, at normal temperatures There is chemical reaction, thus remove the H in gas2S.Owing in marsh gas raw materials, water content is an important ginseng of impact reaction Number, the gas that water content is low, its desulphurization reaction speed is the lowest.The speed wanting to improve desulphurization reaction just requires that marsh gas water content reaches To saturated or close to saturated.Therefore, this utility model is provided with saturator 3 in the front end of two desulfurizing towers.Unstripped gas is made to enter full Enter back into desulfurizing tower after reaching water saturation with tower 3 to react.The desulfurization dust that gas after desulfurization still carries, needs to pass through Could remove after cleansing filter.Therefore, this utility model is provided with decontaminating separator 14 at two desulfurizing tower ends, enters one with this Step improves the purity purifying gas.

Claims (5)

1. a biogas dry method desulfuration system, it is characterised in that: include saturator (3), desulfurizing tower A(11), desulfurizing tower B(13) and Decontaminating separator (14), the low side of saturator (3) is provided with biogas input pipe (1), high-end is provided with escape pipe (5), and biogas is defeated Enter pipe (1) and escape pipe (5) between be provided with the first bypass pipe (2), the escape pipe (5) of saturator (3) respectively with desulfurizing tower A (11) and desulfurizing tower B(13) air inlet pipe (6) of low side connects, desulfurizing tower A(11) and desulfurizing tower B(13) high-end be provided with aerofluxus Pipe (12), the low side of decontaminating separator (14) is provided with purification gas inlet tube (16), high-end is provided with clean gas outlet pipe (15), Desulfurizing tower A(11) and desulfurizing tower B(13) exhaustor (12) parallel connection after again with purify gas inlet tube (16) be connected, desulfurizing tower A (11) exhaustor (12) and desulfurizing tower B(13) air inlet pipe (6) be connected by the second bypass pipe (21), desulfurizing tower B(13) Exhaustor (12) and desulfurizing tower A(11) air inlet pipe (6) is connected by the 3rd bypass pipe (20), purification gas inlet tube (16) is passed through 4th bypass pipe (19) is connected with clean gas outlet pipe (15).
A kind of biogas dry method desulfuration system the most according to claim 1, it is characterised in that: at biogas input pipe (1), saturated Tower (3), desulfurizing tower A(11), desulfurizing tower B(13) and decontaminating separator (14) on be each provided with diffusing arm (7), respectively diffuse House steward (4) is diffused in pipe (7) connection.
A kind of biogas dry method desulfuration system the most according to claim 1, it is characterised in that: at saturator (3), desulfurizing tower A (11), desulfurizing tower B(13) and the bottom of decontaminating separator (14) be each provided with blow down branch (17), each blow down branch (17) is even Connect blowdown main (18).
4. according to a kind of biogas dry method desulfuration system described in claim 1,2 or 3, it is characterised in that: biogas input pipe (1), Diffuse house steward (4), diffuse arm (7), air inlet pipe (6), escape pipe (5), exhaustor (12), clean gas outlet pipe (15), purification Gas inlet tube (16), blow down branch (17), blowdown main (18), the 4th bypass pipe (19), the 3rd bypass pipe (20), the second bypass The valve suitable with pipe model all it is each provided with on pipe (21), the first bypass pipe (2).
A kind of biogas dry method desulfuration system the most according to claim 1, it is characterised in that: at desulfurizing tower A(11), desulfurizing tower B(13) top is provided with operating platform (9), operating platform (9) be provided above desulfurizing agent lifting device (10), operation is flat The lower section of platform (9) is provided with ladder (8).
CN201620595613.9U 2016-06-19 2016-06-19 A kind of biogas dry method desulfuration system Active CN205850588U (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201620595613.9U CN205850588U (en) 2016-06-19 2016-06-19 A kind of biogas dry method desulfuration system

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201620595613.9U CN205850588U (en) 2016-06-19 2016-06-19 A kind of biogas dry method desulfuration system

Publications (1)

Publication Number Publication Date
CN205850588U true CN205850588U (en) 2017-01-04

Family

ID=57636676

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201620595613.9U Active CN205850588U (en) 2016-06-19 2016-06-19 A kind of biogas dry method desulfuration system

Country Status (1)

Country Link
CN (1) CN205850588U (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110433642A (en) * 2019-08-28 2019-11-12 苏州仕净环保科技股份有限公司 A kind of double-tower type desulfuring and denitrifying apparatus

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110433642A (en) * 2019-08-28 2019-11-12 苏州仕净环保科技股份有限公司 A kind of double-tower type desulfuring and denitrifying apparatus

Similar Documents

Publication Publication Date Title
Xiao et al. Review of desulfurization process for biogas purification
CN106955589B (en) Boiler flue gas simultaneous desulfurization and denitrification device
CN102500323B (en) Modified active carbon desulfurizer and preparation method thereof and treatment method of hydrogen sulfide waste gas
CN102061261A (en) Method for culturing microalgae by utilizing flue gas of coal fired power plant
CN104524935A (en) Single-tower type double-circulation sprinkling composite absorption device and method
CN201873655U (en) Biomass methane refining system
CN103031172A (en) Layered biological-chemical combined biogas desulfurizing device
CN205850588U (en) A kind of biogas dry method desulfuration system
CN103357260A (en) Flue gas desulfurization-denitration integrated process for strengthening urea by applying ferrous complexing agent
CN103432879A (en) Method for desulfurization and denitrification of complexing ferroporphyrin smoke based on supergravity
CN103145244A (en) Synergistic biological treatment method for washing waste water and amine salt waste liquor produced by capturing CO2 in smoke of coal-fired power plant
CN106497620B (en) Biogas purification and biogas slurry treatment system and method with biogas slurry as CO2 absorbent
CN202983509U (en) Removing device of hydrogen sulfide in methane
CN103007747A (en) Multi-stage catalyzed sorption reactor
CN104941420A (en) Flue gas desulfurization comprehensive treatment system and method
CN203960157U (en) A kind of marsh gas treating system
CN112011378A (en) Method for performing biogas desulfurization by using wastewater in biochemical process
CN203030188U (en) Multi-stage catalytic adsorption reactor
CN211706407U (en) Desulfurization system
CN212327831U (en) Environmental-friendly resourceful treatment system for fireflood tail gas
CN204710066U (en) Biogas recirculation desulfurization preparation facilities
Deng et al. Biogas cleaning and upgrading
CN203990299U (en) Gas protection desulfurizer
CN210631907U (en) Complex iron method desulfurizer performance evaluation device
CN206428204U (en) A kind of device of coke-stove gas LNG combined production of methanol

Legal Events

Date Code Title Description
C14 Grant of patent or utility model
GR01 Patent grant