CN102492640A - Aeromonas capable of removing hydrogen sulfide (H2S) gas in gas and usage thereof - Google Patents
Aeromonas capable of removing hydrogen sulfide (H2S) gas in gas and usage thereof Download PDFInfo
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- CN102492640A CN102492640A CN201110415793XA CN201110415793A CN102492640A CN 102492640 A CN102492640 A CN 102492640A CN 201110415793X A CN201110415793X A CN 201110415793XA CN 201110415793 A CN201110415793 A CN 201110415793A CN 102492640 A CN102492640 A CN 102492640A
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- gas
- aeromonas
- bio
- hydrogen sulfide
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- Y—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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
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- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
- Treating Waste Gases (AREA)
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
Abstract
The invention discloses aeromonas capable of removing hydrogen sulfide (H2S) gas in a gas and usage thereof, wherein aeromonas sp. CGMCC No.5279 is capable of removing H2S gas in gas. Experimental results show that: by placing the (Aeromonas sp.) CGMCC No.5279 disclosed by the invention on a ceramic grain filter and then filling the same on a bio-trickling filter, the bio-trickling filter can remove H2S gas rapidly, and after the treatment, the exit mass concentration of the H2S is less than 0.03 mg/m<3> and reaches the factory primary standard in the GB14554-93 Emission Standards for Odor Pollutants.
Description
Technical field
The present invention relates to a strain and remove H in the gas
2The Aeromonas of S gas and purposes.
Background technology
H
2S has pungency and asphyxiant colourless gas, and lower concentration just has the intensive foul odour.Sucking H
2When S concentration is low, can see significantly hormesis, when inhaled concentration was higher, olifactory nerve tip paralysis can be to H
2The S stink disappears to continue and then goes into a coma, even dead.
The treatment process of tradition hydrogen sulfide not only costs an arm and a leg but also is prone to cause secondary pollution, facts have proved biological method purification atmospheric pollution Cheap highly effective.Wherein bio-trickling method purification odor pollution gas is a newer Environmental Biotechnology, also is the most promising at present waste gas biologic treating technique.
When process or behind pretreated waste gas entering bio-trickling Tower System; Through when the biomembranous packing layer; After repugnant substance in the gas is water-soluble, is recycled liquid again and, reaches the purpose of Purge gas attached to the absorption of the mikrobe on the filling surface, absorption, degraded.
Existing hydrogen sulfide biologic treating technique is often with on the active sludge direct inoculation filler, and the formation microbial film, the effective microbe ratio is low in the film, also need behind the extension film carry out the domestication of long period to it, and operational condition is controlled than difficult in the domestication process.Therefore need badly a kind of can be at bio-trickling filter rapidly and efficiently to H
2The bacterial strain that S gas is handled.
Summary of the invention
The objective of the invention is to overcome deficiency of the prior art, provide a kind of and can remove H in the gas efficiently
2The Aeromonas of S gas.
Second purpose of the present invention provides a kind ofly can remove H in the gas efficiently
2The purposes of the Aeromonas of S gas.
Technical scheme of the present invention is summarized as follows:
H in a kind of removal gas
2The Aeromonas of S gas (Aeromonas sp.) CGMCC No.5279, it has H in the gas of removal
2The ability of S gas.
H in a kind of removal gas
2The Aeromonas of S gas (Aeromonas sp.) CGMCC No.5279 removes H in the gas
2The purposes of S gas.
Experimental result shows: after filling in bio-trickling filter after being arranged on Aeromonas of the present invention (Aeromonas sp.) CGMCC No.5279 on the ceramic grain filter, it can make bio-trickling filter can remove H fast
2S gas is handled back H
2S outgoing quality concentration is less than 0.03mg/m
3, reach the factory's circle primary standard among the GB14554-93 " odorant pollutant emission standard ".
Description of drawings
Fig. 1 handles for bio-trickling filter and contains H
2The experimental installation synoptic diagram of S gas.
Fig. 2 handles for bio-trickling filter and contains H
2The equipment synoptic diagram of S gas.
Embodiment
Through specific embodiment the present invention is further described below.
Remove H in the gas
2The isolation cultivation method of the Aeromonas Aeromonas sp. of S gas comprises the steps:
(1) mud is taken from Jizhuangzi Waste Water Treatment Plant, Tianjin, and supplement the nutrients every day liquid and aeration reach more than the 90mL/g SVI, accomplishes microorganism culturing.Stop to add nutritive medium, add sodium thiosulfate solution (sulfonium ion concentration is 2g/L) every day, keep ventilation, after 15 days wherein desulfurization bacterium become dominant bacteria, the desulfurization bacterium domestication is accomplished.
Nutritive medium is formed: glucose 0.1g, peptone 0.5g, K
2HPO
40.6g, KH
2PO
40.6g, MgCl
26H
2O0.1g, NH
4Cl 0.2g, small amount of Fe SO
47H
2O and MgSO
4-5H
2O, adding distil water is to 1000mL.
(2) muddy water mixed solution that step (1) is obtained takes out 10mL, adds in the Erlenmeyer flask that 90mL sterile purified water and 20 sterilization granulated glass spherees have been housed, and the 20min that fully vibrates smashes the mud flco, makes bacterial cell fully be discharged in the supernatant; Leave standstill 30min, draw the adding of 1mL supernatant with aseptic straw and be equipped with in the test tube of 9mL sterile distilled water, be mixed with 10
-2The solution of concentration, by that analogy, preparation 10
-3~10
-7The solution of concentration;
(3) choosing gradient is 10
-5~10
-7Bacteria suspension, get 1mL respectively and be inoculated in the substratum, each extent of dilution is done 3 parallel appearance, numbering; Under the condition of aerobic, preserve moisture for 10 ℃ and cultivated for 3 weeks;
(4) choosing colony is big in the culture medium flat plate from step (3); Single bacterium colony that form is different, line separates once more in the solid medium flat board, repeats plate streaking and separates; Make the homomorphosis of bacterium colony in microscope on the flat board; Single, similar single bacterium colony, the called after Aeromonas Aeromonas sp. of being of size
Solid medium: Na
2S
2O
35H
2O 8g, K
2HPO
42.0g, KH
2PO
42.0g, NH
4Cl 0.4g, MgCl
26H
2O 0.2g, FeSO
47H
2O 0.01g, agar 20g, adding distil water are to 1000mL, and transferring pH is 7.0.
Aeromonas Aeromonas sp. of the present invention has following Microbiological Characteristics:
1. morphological characteristic
Examine under a microscope, for shaft-like, long 2.0 μ m, wide 0.62 μ m; On substratum, form the oyster white bacterium colony.
2. cultivate and learn characteristic
Under 10 ℃, when in solid medium, cultivating, (Aeromonas sp.) of the present invention bacterial strain has following characteristic.
Smooth surface is moistening, rat, and the edge indentation, thalline is rounded, and color is a beige.
3. physiological property
Gram negative bacterium, catalase is negative, methyl red test is positive, hydrolyzed starch, liquefy gelatin, edwardsiella hoshinae, growth pH value are 6~8,5~30 ℃ of growth temperatures.
Learn characteristic according to mentioned microorganism; Called after Aeromonas (Aeromonas sp.); Be preserved in China Committee for Culture Collection of Microorganisms common micro-organisms center on September 22nd, 2011, deposit number is CGMCC No.5279, and the preservation address is: No. 3, Yard 1, BeiChen xi Road, Chaoyang District, Beijing City; Institute of Microorganism, Academia Sinica, and survived.
Aeromonas (Aeromonas sp.) is to gas H
2The removal effect of S gas.
With the Aeromonas that filters out (Aeromonas sp.), be inoculated into and carry out enlarged culturing in the nutrient solution, form bacteria suspension; Ceramic grain filter is soaked wherein, add nutrient solution every day and continue aeration, filter material surface microbial film thickness reaches 1~2m, hangs film and accomplishes; The filtrate that hangs up properly film is successively added in the bio-trickling filter (see figure 1), at spray liquid flow 8L/h, contain H
2The air flow quantity 0.4m of S
3/ h, H wherein
2S mass concentration 0.2~0.25mg/m
3, room temperature processing condition under starter gear.Treat H
2The clearance of S has reached more than 85%, and outgoing quality concentration is controlled at 0.03mg/m
3Below, show that the bio-trickling tower apparatus has started to finish, get into steady operational status.
After stable, move 40 days more continuously under the same processing condition, install stable continuously, H
2The clearance of S is stabilized in more than 85%, and it is very good to move treatment effect continuously, reaches the factory's circle primary standard among the GB14554-93 " odorant pollutant emission standard ".
With comparing on Aeromonas of the present invention (Aeromonas sp.) the inoculation filler with on the active sludge direct inoculation filler; The filtrate that has Aeromonas of the present invention (Aeromonas sp.) is positioned in the bio-trickling filter; Removal hydrogen sulfide that can be stable after 5 days, and the bio-trickling filter of common inoculation of activated-sludge could stable removal hydrogen sulfide after general 2 weeks.
The composition of nutrient solution is: Na
2S
2O
35H
2O 8g, K
2HPO
42.0g, KH
2PO
42.0g, NH
4CI 0.4g, MgCl
26H
2O 0.2g, FeSO
47H
2O 0.01g, adding distil water are to 1000mL, and transferring pH is 7.0.
Claims (2)
1. remove H in the gas for one kind
2The Aeromonas of S gas (Aeromonas sp.) CGMCC No.5279, it has H in the gas of removal
2The ability of S gas.
2. H in a kind of removal gas of claim
2The Aeromonas of S gas (Aeromonas sp.) CGMCC No.5279 removes H in the gas
2The purposes of S gas.
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CN201110415793.XA CN102492640B (en) | 2011-12-14 | 2011-12-14 | Aeromonas capable of removing hydrogen sulfide (H2S) gas in gas and usage thereof |
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CN102492640B CN102492640B (en) | 2014-09-03 |
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103468608A (en) * | 2013-08-27 | 2013-12-25 | 重庆瑞宝环保工程有限公司 | Complex flora for sewage treatment and culture method of complex flora |
CN106582258A (en) * | 2016-12-23 | 2017-04-26 | 山东大学 | Method for removing hydrogen sulfide by utilizing heterotrophic microorganisms |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101153270A (en) * | 2006-09-27 | 2008-04-02 | 中国科学院沈阳应用生态研究所 | Bacterium agent for renovation of organic pollution aquifer, producing and using method of the same |
CN101165167A (en) * | 2006-10-18 | 2008-04-23 | 中国科学院沈阳应用生态研究所 | Microbial inoculum for repairing amino benzenes polluted water and its preparation method and using method |
-
2011
- 2011-12-14 CN CN201110415793.XA patent/CN102492640B/en active Active
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101153270A (en) * | 2006-09-27 | 2008-04-02 | 中国科学院沈阳应用生态研究所 | Bacterium agent for renovation of organic pollution aquifer, producing and using method of the same |
CN101165167A (en) * | 2006-10-18 | 2008-04-23 | 中国科学院沈阳应用生态研究所 | Microbial inoculum for repairing amino benzenes polluted water and its preparation method and using method |
Non-Patent Citations (1)
Title |
---|
杨义飞等: "利用异养菌脱除H2S恶臭的实验研究", 《哈尔滨建筑大学学报》, vol. 35, no. 1, 28 February 2002 (2002-02-28), pages 73 - 76 * |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103468608A (en) * | 2013-08-27 | 2013-12-25 | 重庆瑞宝环保工程有限公司 | Complex flora for sewage treatment and culture method of complex flora |
CN106582258A (en) * | 2016-12-23 | 2017-04-26 | 山东大学 | Method for removing hydrogen sulfide by utilizing heterotrophic microorganisms |
CN106582258B (en) * | 2016-12-23 | 2019-05-14 | 山东大学 | A method of hydrogen sulfide is removed using heterotrophic microorganism |
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CN102492640B (en) | 2014-09-03 |
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