CN102337236B - Alkaline Bacilluspseudofirmus MC02 and application thereof - Google Patents
Alkaline Bacilluspseudofirmus MC02 and application thereof Download PDFInfo
- Publication number
- CN102337236B CN102337236B CN 201110256796 CN201110256796A CN102337236B CN 102337236 B CN102337236 B CN 102337236B CN 201110256796 CN201110256796 CN 201110256796 CN 201110256796 A CN201110256796 A CN 201110256796A CN 102337236 B CN102337236 B CN 102337236B
- Authority
- CN
- China
- Prior art keywords
- bacilluspseudofirmus
- alkaline
- bacterial strain
- reduction
- aqds
- 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
Links
Images
Abstract
The invention discloses alkaline Bacilluspseudofirmus MC02 CGMCC (China General Microbiological Culture Collection Center): 4772 and application of the alkaline Bacilluspseudofirmus MC02 in reduction of iron oxides and humus. The Bacilluspseudofirmus MC02 is obtained by separating and purifying an alkaline sludge microbial fuel cell anode biofilm which well operates; and under the alkaline condition, the Bacilluspseudofirmus MC02 has strong Fe(III) and AQDS (anthraquinone-2,6-disulfonic acid) reducing capacity, broad electron utilization spectrum and wide application prospect.
Description
Technical field
The invention belongs to the Environmental Biotechnology field, be specifically related to a strain class bacillus firmus (
Bacillus pseudofirmus), and soil ulmin reduction and the application of iron reductive under alkaline anaerobic condition.
Background technology
Humus respiration is a ubiquitous microbial respiratory metabolisable form in the anaerobic environment.Humus respiration claims that again quinone breathes, refer to mikrobe with soil ulmin as unique terminal electron acceptor, accept the electronics that provides from materials such as organic acids, the process of thalli growth is supported in the generation of coupling energy.Humus respiration and iron reduction are in close relations.Humus respiration acts in the biomass geochemistry working cycle of element significant; Show as: 1) mikrobe is in the process of carrying out humus respiration; Can produce CO directly with organic matter in the environment or environment toxic substance oxidations such as toluene, vinylchlorid
22) respiration produces goes back some the oxidation state materials in ortho states humic, the enough reducing environments of mass-energy, like Fe (III), Mn (IV), Cr (VI), U (VI), nitroaromatic and many halos pollutent.The humic acid respiration can influence the biomass geochemistry circulation of C in the environment, N, Fe, Mn and some trace metal elements; And can promote the detoxification of heavy metal and organic pollutant; Have active effect at aspects such as self, the reparation of contaminated soil original position, WWTs, therefore the relevant research of humus respiration in recent years receives much attention.
Since the later stage nineties in last century, multiple with humic acid or humic acid pattern thing anthraquinone-2,6-disulfonic acid (AQDS) also separates in succession for the bacterium of terminal electron acceptor and identifies.Yet alkaline condition is unfavorable for microbial growth relatively, and under this exacting terms, mikrobe possibly tamed out a cover mechanism, with the environment of cope with bad better.At present, do not find to have the class bacillus firmus report of Fe (III) reduction and humic acid reducing activity as yet.
Summary of the invention
The objective of the invention is to find the efficient reduction of the alkalescence bacterium of a strain anaerobic humus and ferriferous oxide.
Another object of the present invention provides the application of above-mentioned type of bacillus firmus in ferriferous oxide and soil ulmin reduction.
The class bacillus firmus of gained of the present invention (
Bacillus pseudofirmus) MC02, being deposited in China Committee for Culture Collection of Microorganisms common micro-organisms center on April 21st, 2011, the preservation address is No. 3, Yard 1, BeiChen xi Road, Chaoyang District, Beijing City, preserving number is:
CGMCC:4772, and in identifying the bacterial classification survival on the same day.
Fe (III) breathes and the bacterial strain of humus respiration capability to the invention provides new the having of a strain; Said bacterial strain is compared with reporting bacterial strain, under alkaline condition, has stronger Fe (III) reduction and humic acid reducing power; Electronics utilization spectrum is wider; Can reduce the higher ferriferous oxide of percent crystallinity, for example lepidocrokile, rhombohedral iron ore are with a wide range of applications.
Description of drawings
Fig. 1 is the design sketch that bacterial strain MC02 utilizes different electron donor reduction AQDS;
Fig. 2 is the design sketch that bacterial strain MC02 utilizes different electron donor reduction Fe (III);
Fig. 3 is that bacterial strain MC02 is a substrate with glucose, reduces the design sketch of different ferriferous oxides;
Fig. 4 is that bacterial strain MC02 is substrate with glucose, under different electron shuttle body mediations, and the design sketch of reduction lepidocrokile.
Embodiment
The enrichment of bacterial strain MC02 with separate
1) from pH is 9.0 sludge microbe fuel cell, tears and get the anode carbon felt and be soaked in the 50mL liquid enrichment medium; (configuration such as the CN200910041235.4 of sludge microbe fuel cell are said), the composition of liquid concentration and separation substratum is: 16g AQDS (electron acceptor(EA)), 0.25g NH
4Cl, 0.678g NaH
2PO
42H
2O, 0.1g KCl, 2.94g NaHCO
3, 1.59g Na
2CO
3, 10.0mL vitamin solution, 10.0mL trace element solution (pH 9.0).Wherein, vitamin solution is to contain 2.0mg vitamin H, 2.0mg folic acid, VB6 10.0mg VITAMINs, 5.0mg VitB1,5.0mg vitamin G, 5.0mg nicotinic acid, 5.0mg VA, 0.1mg cobalamin, 5.0mg para-amino benzoic acid, 5.0mg Thioctic Acid in every liter of deionized water; Trace element solution is to contain 1.5g nitrilotriacetic acid(NTA), 3.0g MgSO in every liter of deionized water
47H
2O, 0.5g MnSO
4H
2O, 1.0g NaCl, 0.1g FeSO
47H
2O, 0.1g CoCl
26H
2O, 0.1g CaCl
2, 0.1g ZnSO
47H
2O, 0.01g CuSO
45H
2O, 0.01g AlK (SO
4)
212H
2O, 0.01g H
3BO
3, 0.01g Na
2MoO
42H
2O;
2) inflated with nitrogen is no less than 30 minutes in the vaccinated enrichment medium, and air-blowing finishes and covers serum cap and add the aluminium lid sealing, places anaerobism workstation (N
2/ CO
2=80/20), 30 ℃ leave standstill cultivation, observe the colour-change situation of nutrient solution;
3) become when orange-yellow from colourless when the nutrient solution color, the inoculum size with 10% is forwarded to another fresh liquid separation culture medium with nutrient solution, and anaerobic operation and anaerobism culture condition are with 2), so enrichment culture is three times;
4) reacted nutrient solution employing of the 4th generation dilution-plate method is suitably diluted, nutrient solution 0.1 mL after the dilution is evenly coated on the LB solid medium, place anaerobism workstation (N
2/ CO
2=80/20) cultivate 48h for 30 ℃, picking list bacterium colony carries out single bacterium colony isolation and purification, and wherein, the composition of said LB solid medium is: peptone 10g/L, and yeast extract 5g/L, NaCl 10 g/L, agar powder 20 g/L, pH are 9.0.
Obtained strains type of being bacillus firmus (
Bacillus pseudofirmus) MC02, on April 21st, 2011 in China Committee for Culture Collection of Microorganisms's common micro-organisms center preservation, preserving number is: CGMCC 4772, and in identifying bacterial classification survival on the same day.
Bacterial strain(
Bacillus pseudofirmus) MC02
Morphological specificity
1) thalli morphology characteristic
Bacterial strain MC02 Gram-positive, shaft-like, gemma and middle life are arranged, the paired or catenation of thalline.
) the colonial morphology characteristic
After aerobic LB agar plate was cultivated 48h, the bacterium colony smooth surface was opaque, and the edge is irregular, the about 2-3mm of colony diameter.
Bacterial strain(
Bacillus pseudofirmus) MC02
Physiological and biochemical property
According to the physiological and biochemical property of " the outstanding Bacteria Identification identification handbook of uncle " the 9th edition described standard program test strain, its biochemical character is seen table 1.
Bacterial strain(
Bacillus pseudofirmus) MC02
The molecular classification status
The 16SrRNA of the bacterial strain that separation is obtained is through pcr amplification, order-checking.The Genebank number of landing of the 16S rRNA gene order of bacterial strain PAH-1 is JN566125, and concrete sequence is seen SEQ ID NO:1.
The sequence that obtains is compared with the relevant 16S rRNA sequence on the Genebank.Compare with Cluster X method with the disclosed corresponding bacterial strain sequence of Genebank.Based on 1000 multiple sampling analyses, use MEGA 4.0 to press adjacent method constructing system tree.The 16S rRNA phylogenetic tree that structure obtains is as shown in Figure 1.
Theoretical according to phylogeny, similarity just can be thought unified bacterial strain only greater than 97% between bacterial strain.Aimed strain reaches 99.8% with a type bacillus firmus similarity, and therefore, bacterial strain MC02 is defined as
Bacillus pseudofirmus
Bacterial strainMC02
Utilize the test of different electron donor reduction AQDS
Liquid culture based formulas: 0.25g NH in every liter of deionized water
4Cl, 0.678g NaH
2PO
42H
2O, 0.1g KCl, 2.94g NaHCO
3, 1.59g Na
2CO
3Each 10.0 mL (vitamin solution and the same isolation medium of trace element solution composition) of vitamin solution and trace element solution; (carbonic acid buffering, pH 9.0) was in 121 ℃ of sterilizations 20 minutes; Different electron donors such as the sodium acetate of sterilization back interpolation sterilization, glucose, sucrose, USP Kosher, lactic acid, final concentration is 10 mmol/L.Be seeded to the beef extract-peptone liquid nutrient medium from the inclined-plane picking lawn of preserving bacterial strain MC02, in 30 ℃, 180 rev/mins of shaking table activation thalline 18 hours make bacterial number reach exponential phase of growth.4 ℃, the centrifugal 10min of 8000r/min removes supernatant, and carbonic acid buffer suspends again.Repeat aforesaid operations 2 times.About 1.2 (λ=600 nm) of concentration of final suspension-s.Add 1ml (CFU=1.0 * 10
7) as handling, the contrast that does not add bacterium is set simultaneously.Every separated about 12h gets the 4mL nutrient solution, adopts ultraviolet-visible spectrophotometer to measure AH at the 510nm place
2DS content is with AH
2DS concentration is index, and the checking bacterial strain utilizes the ability of different electron donor reduction AQDS, and test-results is as shown in Figure 1.Can know that from Fig. 1 when being electron donor with sucrose, glucose, USP Kosher and lactic acid in the system, the reduction efficiency of AQDS is higher, wherein, when being substrate with glucose, reduction efficiency is the highest, has 85% AQDS to be reduced approximately.The electronics utilization spectrum of MC02 is wider, and reduction efficiency is higher.
Bacterial strainMC02
Utilize the test of different electron donor reduction Fe (III)
The prescription of liquid nutrient medium is the same, contains the Fe (III) (soluble state iron) of 25mM in the system.Other operation is the same.Every got at a distance from 5 days the 4ml nutrient solution that mixes in 16ml 0.5mol/l HCl solution 180 rev/mins vibrated 1.5 hours; Refilter; Adopt adjacent phenanthroline method to give the Fe (II) in the filtrating colour developing; Adopt ultraviolet spectrophotometer to measure the content of Fe (II) at 510nm place, and be contrast, verify the iron reducing power of bacterial strain with the nutrient solution that does not add bacterium.As shown in table 2, MC02 can utilize sucrose, USP Kosher, Hydrocerol A and glucose reduction Fe (III).Wherein, when being substrate with sucrose, reduction efficiency is the highest, has the iron of 0.5mM to be reduced approximately.
Bacterial strainMC02
With glucose is donor, reduces the test of different ferriferous oxides
The prescription of liquid nutrient medium is the same, contains the different ferriferous oxide (pyrrhosiderite, lepidocrokile and rhombohedral iron ore) of 25mM in the system.Other operation and testing method are the same.The result is as shown in Figure 3, is electron acceptor(EA) with glucose, and bacterial strain is the highest to the reduction efficiency of lepidocrokile, secondly is pyrrhosiderite.
Bacterial strainMC02
With glucose is donor, under different electron shuttle body mediations, and the test of reduction lepidocrokile
The prescription of liquid nutrient medium is the same, contains the lepidocrokile of 25 mM in the system, and the electron shuttle body adds the AQDS of 0.5 mM and the humic acid (HA) of 0.2 g/l respectively.Result such as Fig. 4 add AQDS and HA and can obviously improve the reduction efficiency of bacterial strain to ferriferous oxide, and reduction of a fraction you can well imagine high 16% and 38%.
< 110>Guangdong Prov. Inst. of Ecological Environment & Soil Science
< 120>one strain alkaline species bacillus firmus and application thereof
<130> MC02
<160> 1
<170> PatentIn?version?3.5
<210> 1
<211> 1408
<212> DNA
< 213>type bacillus firmus (Bacillus pseudofirmus)
<400> 1
acataaaggt?tacctcaccg?acttcgggtg?ttacaaactc?tcgtggtgtg?acgggcggtg 60
tgtacaaggc?ccgggaacgt?attcaccgcg?gcatgctgat?ccgcgattac?tagcaattcc 120
ggcttcatgt?aggcgagttg?cagcctacaa?tccgaactga?gaatggcttt?atgggattcg 180
ctcaacctcg?cggttttgca?gccctttgta?ccatccattg?tagcacgtgt?gtagcccagg 240
tcataagggg?catgatgatt?tgacgtcatc?cccaccttcc?tccggtttgt?caccggcagt 300
caccttagag?tgcccaactg?aatgctggca?actaagatca?agggttgcgc?tcgttgcggg 360
acttaaccca?acatctcacg?acacgagctg?acgacaacca?tgcaccacct?gtcactttgt 420
cccccgaagg?ggaaagccct?atctctaggg?tggtcaaagg?atgtcaagac?ctggtaaagg 480
ttcttcgcgt?tgcttcgaat?taaaccacat?gctccactgc?ttgtgcgggc?ccccgtcaat 540
tcctttgagt?ttcaaccttg?cggtcgtact?ccccaggcgg?agtgcttaat?gtgttaactt 600
cggcactaag?ggcatcgaaa?cccctaacac?ctagcactca?tcgtttacgg?cgtggactac 660
cagggtatct?aatcctgttt?gctccccacg?ctttcgcgcc?tcagcgtcag?ttacagacca 720
gagagtcgcc?ttcgccactg?gtgttcctcc?acatatctac?gcatttcacc?gctacacgtg 780
gaattccact?ctcctcttct?gtactcaagt?ctcccagttt?ccaatgaccc?tccacggttg 840
agccgtgggc?tttcacatca?gacttaagag?accgcctgcg?cgcgctttac?gcccaataat 900
tccggacaac?gcttgccacc?tacgtattac?cgcggctgct?ggcacgtagt?tagccgtggc 960
tttctggtta?ggtaccgtca?aggtgccgcc?ttattcaaac?ggcacttgtt?cttccctaac 1020
aacagagctt?tacgatccga?aaaccttcat?cactcacgcg?gcgttgctcc?gtcagacttt 1080
cgtccattgc?ggaagattcc?ctactgctgc?ctcccgtagg?agtctgggcc?gtgtctcagt 1140
cccagtgtgg?ccgatcaccc?tctcaggtcg?gctacgcatc?gtcgccttgg?taagccgtta 1200
ccttaccaac?tagctaatgc?gccgcgggcc?catctgtaag?tgatagccag?aggccatctt 1260
ttaccgctcc?accatgaggt?ggaacgggtt?atccggtatt?agccccggtt?tcccggagtt 1320
atcccagtct?tacaggcagg?ttgcccacgt?gttactcacc?cgtccgccgc?taacatcagg 1380
gagcaagctc?ccatcagtcc?gctcgact 1408
Claims (2)
- Type bacillus firmus ( Bacillus pseudofirmus) bacterial strain MC02, its preserving number is CGMCC:4772.
- 2. the application of said type of bacillus firmus MC02 of claim 1 in ferriferous oxide and soil ulmin reduction.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN 201110256796 CN102337236B (en) | 2011-09-01 | 2011-09-01 | Alkaline Bacilluspseudofirmus MC02 and application thereof |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN 201110256796 CN102337236B (en) | 2011-09-01 | 2011-09-01 | Alkaline Bacilluspseudofirmus MC02 and application thereof |
Publications (2)
Publication Number | Publication Date |
---|---|
CN102337236A CN102337236A (en) | 2012-02-01 |
CN102337236B true CN102337236B (en) | 2012-09-26 |
Family
ID=45513190
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN 201110256796 Active CN102337236B (en) | 2011-09-01 | 2011-09-01 | Alkaline Bacilluspseudofirmus MC02 and application thereof |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN102337236B (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110607263B (en) * | 2019-09-26 | 2021-01-22 | 石河子大学 | Bacillus alcalophilus strain wp-1 and application thereof |
Families Citing this family (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102618463B (en) * | 2012-03-22 | 2013-06-05 | 中国热带农业科学院环境与植物保护研究所 | Kocuria rosea with humus reduction activity |
CN105586292B (en) * | 2015-12-25 | 2018-11-02 | 平潭综合实验区市政园林有限公司 | One bacillus and its application |
CN110499275B (en) * | 2018-05-18 | 2021-11-05 | 天津大学 | Method for domesticating humic acid reducing bacteria under disturbance load condition based on AQS |
CN108865923B (en) * | 2018-05-24 | 2021-10-01 | 苏州逸凡特环境修复有限公司 | Microbial strain for treating heavy metal contaminated soil and screening method and application thereof |
CN110257487A (en) * | 2019-06-27 | 2019-09-20 | 福建省致青生态环保有限公司 | A kind of method and its application calculating microbial inoculum applied amount based on cellulose enzyme gene |
CN110184332B (en) * | 2019-06-27 | 2023-01-03 | 福建省致青生态环保有限公司 | Composting microbial inoculum compounding method for treating high-fiber materials and application thereof |
CN110257486B (en) * | 2019-06-27 | 2022-09-09 | 福建省致青生态环保有限公司 | Method for characterizing compost maturity based on cellulase gene |
CN115433692A (en) * | 2022-06-10 | 2022-12-06 | 兰州理工大学 | Humic acid degrading bacteria and application thereof |
Family Cites Families (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1340464A (en) * | 2000-08-25 | 2002-03-20 | 中国水产科学研究院黄海水产研究所 | Bacillus rigens method for biologically repairing culture environment of aquatic products |
CN1563342A (en) * | 2004-02-10 | 2005-01-12 | 凌亮 | Microbe preparation in use for treating high difficult wastewater and preparation method |
CN101892180B (en) * | 2010-04-30 | 2012-07-04 | 广东省生态环境与土壤研究所 | Corynebacterium humireducens and application thereof |
CN101993843B (en) * | 2010-08-17 | 2012-10-03 | 中国水产科学研究院黄海水产研究所 | Bacillus firmus strain and application thereof |
-
2011
- 2011-09-01 CN CN 201110256796 patent/CN102337236B/en active Active
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110607263B (en) * | 2019-09-26 | 2021-01-22 | 石河子大学 | Bacillus alcalophilus strain wp-1 and application thereof |
Also Published As
Publication number | Publication date |
---|---|
CN102337236A (en) | 2012-02-01 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN102337236B (en) | Alkaline Bacilluspseudofirmus MC02 and application thereof | |
CN102115719B (en) | Aerobic denitrifying bacterium, and screening method and application thereof | |
CN109810923B (en) | Aerobic denitrifying bacterium SLY2-21 for sewage denitrification and application thereof | |
CN102296037A (en) | Pseudomonas aeruginosa and separation method and application thereof | |
CN101892180B (en) | Corynebacterium humireducens and application thereof | |
Wang et al. | Nitrogen removal from synthetic wastewater using single and mixed culture systems of denitrifying fungi, bacteria, and actinobacteria | |
CN109182192A (en) | One plant of aerobic denitrifying bacteria HY3-2 and its application in sewage water denitrification | |
CN111808775B (en) | High-temperature-resistant thermophilic bacillus amylovorus and application thereof | |
CN101096645A (en) | Gas production enterobacteria and uses thereof | |
CN101353634B (en) | Klebsiella pneumoniae and use thereof | |
CN102634466B (en) | Thauera humireducens and application thereof and microbiological preparation | |
CN102864098B (en) | Denitrification phosphorus removal bacterium H-hrb02 as well as screening method and application thereof | |
CN101070528A (en) | Iron-reduced tuftedmonas and its use | |
CN113980830A (en) | Pseudomonas stutzeri, culture thereof and application thereof | |
CN102634467B (en) | Iron reducing bacteria and application thereof | |
CN105400719B (en) | One plant of greedy copper Pseudomonas bacterial strain that can convert heavy metal and its application | |
CN101353635B (en) | A stain of Pantoea agglomerans and use thereof | |
CN102533596B (en) | Alcaligenes denitrificans with denitrification performance and application thereof | |
CN100429304C (en) | Bacillus alcaligenes strain for degrading ortho-nitrophenol and preparing method | |
CN114703104A (en) | Bacterial strain with iron reduction capacity and electrochemical activity and application thereof | |
CN105670965B (en) | Strain with iron reduction capacity and application thereof | |
CN102391959B (en) | Alkaline planococcussp strain and application thereof | |
CN113980852A (en) | Microbial composition for synergistically degrading benzonitrile herbicide and microbial agent produced by same | |
CN101586093A (en) | Enterobacter aerogenes and application thereof | |
CN108753648B (en) | High-temperature-resistant bacterium for promoting ammonia assimilation in sludge composting process |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
C14 | Grant of patent or utility model | ||
GR01 | Patent grant |