CN110591981A - Paracoccus P-2 for degrading deltamethrin and application thereof - Google Patents
Paracoccus P-2 for degrading deltamethrin and application thereof Download PDFInfo
- Publication number
- CN110591981A CN110591981A CN201911016671.6A CN201911016671A CN110591981A CN 110591981 A CN110591981 A CN 110591981A CN 201911016671 A CN201911016671 A CN 201911016671A CN 110591981 A CN110591981 A CN 110591981A
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- CN
- China
- Prior art keywords
- deltamethrin
- paracoccus
- degradation
- degrading
- culture
- 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.)
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- OWZREIFADZCYQD-NSHGMRRFSA-N deltamethrin Chemical compound CC1(C)[C@@H](C=C(Br)Br)[C@H]1C(=O)O[C@H](C#N)C1=CC=CC(OC=2C=CC=CC=2)=C1 OWZREIFADZCYQD-NSHGMRRFSA-N 0.000 title claims abstract description 101
- 239000005892 Deltamethrin Substances 0.000 title claims abstract description 94
- 229960002483 decamethrin Drugs 0.000 title claims abstract description 94
- 241001057811 Paracoccus <mealybug> Species 0.000 title claims abstract description 57
- 230000000593 degrading effect Effects 0.000 title claims abstract description 24
- 241000371997 Eriocheir sinensis Species 0.000 claims abstract description 30
- 239000003795 chemical substances by application Substances 0.000 claims abstract description 10
- 238000004321 preservation Methods 0.000 claims abstract description 10
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 24
- 108020004465 16S ribosomal RNA Proteins 0.000 claims description 4
- 230000015556 catabolic process Effects 0.000 abstract description 44
- 238000006731 degradation reaction Methods 0.000 abstract description 44
- 210000003205 muscle Anatomy 0.000 abstract description 18
- 210000000514 hepatopancreas Anatomy 0.000 abstract description 16
- 230000000694 effects Effects 0.000 abstract description 15
- 230000001580 bacterial effect Effects 0.000 description 29
- 239000007788 liquid Substances 0.000 description 29
- 239000000243 solution Substances 0.000 description 28
- 239000001963 growth medium Substances 0.000 description 26
- VLKZOEOYAKHREP-UHFFFAOYSA-N n-Hexane Chemical compound CCCCCC VLKZOEOYAKHREP-UHFFFAOYSA-N 0.000 description 20
- 238000002474 experimental method Methods 0.000 description 17
- 239000000575 pesticide Substances 0.000 description 15
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 14
- 150000001447 alkali salts Chemical class 0.000 description 13
- 239000000523 sample Substances 0.000 description 13
- CSCPPACGZOOCGX-UHFFFAOYSA-N Acetone Chemical compound CC(C)=O CSCPPACGZOOCGX-UHFFFAOYSA-N 0.000 description 12
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 11
- 238000011081 inoculation Methods 0.000 description 11
- 241000894006 Bacteria Species 0.000 description 10
- SIKJAQJRHWYJAI-UHFFFAOYSA-N Indole Chemical compound C1=CC=C2NC=CC2=C1 SIKJAQJRHWYJAI-UHFFFAOYSA-N 0.000 description 10
- 238000012258 culturing Methods 0.000 description 10
- 108010010803 Gelatin Proteins 0.000 description 9
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- 235000019698 starch Nutrition 0.000 description 9
- 239000001888 Peptone Substances 0.000 description 8
- 108010080698 Peptones Proteins 0.000 description 8
- 238000000034 method Methods 0.000 description 8
- 235000019319 peptone Nutrition 0.000 description 8
- 239000000126 substance Substances 0.000 description 8
- 239000003153 chemical reaction reagent Substances 0.000 description 7
- 239000012153 distilled water Substances 0.000 description 7
- 239000011780 sodium chloride Substances 0.000 description 7
- 238000012360 testing method Methods 0.000 description 7
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- 241001465754 Metazoa Species 0.000 description 5
- 238000001035 drying Methods 0.000 description 5
- 238000004043 dyeing Methods 0.000 description 5
- PZOUSPYUWWUPPK-UHFFFAOYSA-N indole Natural products CC1=CC=CC2=C1C=CN2 PZOUSPYUWWUPPK-UHFFFAOYSA-N 0.000 description 5
- RKJUIXBNRJVNHR-UHFFFAOYSA-N indolenine Natural products C1=CC=C2CC=NC2=C1 RKJUIXBNRJVNHR-UHFFFAOYSA-N 0.000 description 5
- 239000000447 pesticide residue Substances 0.000 description 5
- 239000002728 pyrethroid Substances 0.000 description 5
- 238000005406 washing Methods 0.000 description 5
- ZCYVEMRRCGMTRW-UHFFFAOYSA-N 7553-56-2 Chemical compound [I] ZCYVEMRRCGMTRW-UHFFFAOYSA-N 0.000 description 4
- 229920001817 Agar Polymers 0.000 description 4
- WQZGKKKJIJFFOK-GASJEMHNSA-N Glucose Natural products OC[C@H]1OC(O)[C@H](O)[C@@H](O)[C@@H]1O WQZGKKKJIJFFOK-GASJEMHNSA-N 0.000 description 4
- 239000008272 agar Substances 0.000 description 4
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- 229910000396 dipotassium phosphate Inorganic materials 0.000 description 4
- 239000003814 drug Substances 0.000 description 4
- 229940079593 drug Drugs 0.000 description 4
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- 238000003860 storage Methods 0.000 description 4
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- WEVYAHXRMPXWCK-UHFFFAOYSA-N Acetonitrile Chemical compound CC#N WEVYAHXRMPXWCK-UHFFFAOYSA-N 0.000 description 3
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 3
- 102000016938 Catalase Human genes 0.000 description 3
- 108010053835 Catalase Proteins 0.000 description 3
- PEDCQBHIVMGVHV-UHFFFAOYSA-N Glycerine Chemical compound OCC(O)CO PEDCQBHIVMGVHV-UHFFFAOYSA-N 0.000 description 3
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 3
- 235000015278 beef Nutrition 0.000 description 3
- 229910052799 carbon Inorganic materials 0.000 description 3
- 238000007598 dipping method Methods 0.000 description 3
- 239000011521 glass Substances 0.000 description 3
- 230000007062 hydrolysis Effects 0.000 description 3
- 238000006460 hydrolysis reaction Methods 0.000 description 3
- 239000002054 inoculum Substances 0.000 description 3
- CEQFOVLGLXCDCX-WUKNDPDISA-N methyl red Chemical compound C1=CC(N(C)C)=CC=C1\N=N\C1=CC=CC=C1C(O)=O CEQFOVLGLXCDCX-WUKNDPDISA-N 0.000 description 3
- 238000002156 mixing Methods 0.000 description 3
- 239000000843 powder Substances 0.000 description 3
- KJCVRFUGPWSIIH-UHFFFAOYSA-N 1-naphthol Chemical compound C1=CC=C2C(O)=CC=CC2=C1 KJCVRFUGPWSIIH-UHFFFAOYSA-N 0.000 description 2
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 241000238557 Decapoda Species 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 2
- 239000007836 KH2PO4 Substances 0.000 description 2
- 241000589598 Paracoccus sp. Species 0.000 description 2
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 description 2
- 229910052921 ammonium sulfate Inorganic materials 0.000 description 2
- 238000004458 analytical method Methods 0.000 description 2
- 238000009395 breeding Methods 0.000 description 2
- 230000001488 breeding effect Effects 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 239000011248 coating agent Substances 0.000 description 2
- 238000000576 coating method Methods 0.000 description 2
- 238000005034 decoration Methods 0.000 description 2
- 239000003480 eluent Substances 0.000 description 2
- 229910052564 epsomite Inorganic materials 0.000 description 2
- XJRPTMORGOIMMI-UHFFFAOYSA-N ethyl 2-amino-4-(trifluoromethyl)-1,3-thiazole-5-carboxylate Chemical compound CCOC(=O)C=1SC(N)=NC=1C(F)(F)F XJRPTMORGOIMMI-UHFFFAOYSA-N 0.000 description 2
- 238000000605 extraction Methods 0.000 description 2
- 238000000855 fermentation Methods 0.000 description 2
- 230000004151 fermentation Effects 0.000 description 2
- 210000002816 gill Anatomy 0.000 description 2
- 238000002386 leaching Methods 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 229910000402 monopotassium phosphate Inorganic materials 0.000 description 2
- 239000012074 organic phase Substances 0.000 description 2
- 238000005070 sampling Methods 0.000 description 2
- 238000012216 screening Methods 0.000 description 2
- 239000010802 sludge Substances 0.000 description 2
- VWDWKYIASSYTQR-UHFFFAOYSA-N sodium nitrate Chemical compound [Na+].[O-][N+]([O-])=O VWDWKYIASSYTQR-UHFFFAOYSA-N 0.000 description 2
- 239000002689 soil Substances 0.000 description 2
- 210000001519 tissue Anatomy 0.000 description 2
- 238000002137 ultrasound extraction Methods 0.000 description 2
- BGNGWHSBYQYVRX-UHFFFAOYSA-N 4-(dimethylamino)benzaldehyde Chemical compound CN(C)C1=CC=C(C=O)C=C1 BGNGWHSBYQYVRX-UHFFFAOYSA-N 0.000 description 1
- LVSQXDHWDCMMRJ-UHFFFAOYSA-N 4-hydroxybutan-2-one Chemical compound CC(=O)CCO LVSQXDHWDCMMRJ-UHFFFAOYSA-N 0.000 description 1
- 241000251468 Actinopterygii Species 0.000 description 1
- NLXLAEXVIDQMFP-UHFFFAOYSA-N Ammonia chloride Chemical compound [NH4+].[Cl-] NLXLAEXVIDQMFP-UHFFFAOYSA-N 0.000 description 1
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 1
- 241000195493 Cryptophyta Species 0.000 description 1
- 102000013382 Gelatinases Human genes 0.000 description 1
- 108010026132 Gelatinases Proteins 0.000 description 1
- 241000282414 Homo sapiens Species 0.000 description 1
- 208000030852 Parasitic disease Diseases 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- 240000004808 Saccharomyces cerevisiae Species 0.000 description 1
- PMZURENOXWZQFD-UHFFFAOYSA-L Sodium Sulfate Chemical compound [Na+].[Na+].[O-]S([O-])(=O)=O PMZURENOXWZQFD-UHFFFAOYSA-L 0.000 description 1
- 229930006000 Sucrose Natural products 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 230000003213 activating effect Effects 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 150000001413 amino acids Chemical class 0.000 description 1
- 230000003321 amplification Effects 0.000 description 1
- 238000007664 blowing Methods 0.000 description 1
- 229940041514 candida albicans extract Drugs 0.000 description 1
- 239000012159 carrier gas Substances 0.000 description 1
- 239000000460 chlorine Substances 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 239000000084 colloidal system Substances 0.000 description 1
- 239000003086 colorant Substances 0.000 description 1
- 238000010411 cooking Methods 0.000 description 1
- 239000006071 cream Substances 0.000 description 1
- 239000013078 crystal Substances 0.000 description 1
- 230000002354 daily effect Effects 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 239000003085 diluting agent Substances 0.000 description 1
- 238000010790 dilution Methods 0.000 description 1
- 239000012895 dilution Substances 0.000 description 1
- ZPWVASYFFYYZEW-UHFFFAOYSA-L dipotassium hydrogen phosphate Chemical compound [K+].[K+].OP([O-])([O-])=O ZPWVASYFFYYZEW-UHFFFAOYSA-L 0.000 description 1
- 239000006185 dispersion Substances 0.000 description 1
- 238000010828 elution Methods 0.000 description 1
- 230000003203 everyday effect Effects 0.000 description 1
- 238000011049 filling Methods 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 238000002290 gas chromatography-mass spectrometry Methods 0.000 description 1
- 239000000499 gel Substances 0.000 description 1
- 238000002347 injection Methods 0.000 description 1
- 239000007924 injection Substances 0.000 description 1
- 230000000749 insecticidal effect Effects 0.000 description 1
- 238000002955 isolation Methods 0.000 description 1
- 238000002372 labelling Methods 0.000 description 1
- 238000012417 linear regression Methods 0.000 description 1
- 238000009630 liquid culture Methods 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 231100000053 low toxicity Toxicity 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 230000002503 metabolic effect Effects 0.000 description 1
- 230000000813 microbial effect Effects 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 230000000877 morphologic effect Effects 0.000 description 1
- 239000012452 mother liquor Substances 0.000 description 1
- 239000011664 nicotinic acid Substances 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 238000002414 normal-phase solid-phase extraction Methods 0.000 description 1
- 238000003199 nucleic acid amplification method Methods 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 235000016709 nutrition Nutrition 0.000 description 1
- 230000010355 oscillation Effects 0.000 description 1
- 210000000496 pancreas Anatomy 0.000 description 1
- 230000000149 penetrating effect Effects 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
- 239000011574 phosphorus Substances 0.000 description 1
- 229920001184 polypeptide Polymers 0.000 description 1
- GNSKLFRGEWLPPA-UHFFFAOYSA-M potassium dihydrogen phosphate Chemical compound [K+].OP(O)([O-])=O GNSKLFRGEWLPPA-UHFFFAOYSA-M 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 108090000765 processed proteins & peptides Proteins 0.000 description 1
- 102000004196 processed proteins & peptides Human genes 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 108090000623 proteins and genes Proteins 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- OARRHUQTFTUEOS-UHFFFAOYSA-N safranin Chemical compound [Cl-].C=12C=C(N)C(C)=CC2=NC2=CC(C)=C(N)C=C2[N+]=1C1=CC=CC=C1 OARRHUQTFTUEOS-UHFFFAOYSA-N 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 239000012488 sample solution Substances 0.000 description 1
- 238000007789 sealing Methods 0.000 description 1
- 239000002904 solvent Substances 0.000 description 1
- 241000894007 species Species 0.000 description 1
- 239000012192 staining solution Substances 0.000 description 1
- 239000005720 sucrose Substances 0.000 description 1
- 239000006228 supernatant Substances 0.000 description 1
- 239000002344 surface layer Substances 0.000 description 1
- FKHIFSZMMVMEQY-UHFFFAOYSA-N talc Chemical compound [Mg+2].[O-][Si]([O-])=O FKHIFSZMMVMEQY-UHFFFAOYSA-N 0.000 description 1
- 238000005303 weighing Methods 0.000 description 1
- 239000012138 yeast extract Substances 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12N—MICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
- C12N1/00—Microorganisms, e.g. protozoa; Compositions thereof; Processes of propagating, maintaining or preserving microorganisms or compositions thereof; Processes of preparing or isolating a composition containing a microorganism; Culture media therefor
- C12N1/20—Bacteria; Culture media therefor
- C12N1/205—Bacterial isolates
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/38—Organic compounds containing nitrogen
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12R—INDEXING SCHEME ASSOCIATED WITH SUBCLASSES C12C - C12Q, RELATING TO MICROORGANISMS
- C12R2001/00—Microorganisms ; Processes using microorganisms
- C12R2001/01—Bacteria or Actinomycetales ; using bacteria or Actinomycetales
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- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Microbiology (AREA)
- Organic Chemistry (AREA)
- Health & Medical Sciences (AREA)
- Bioinformatics & Cheminformatics (AREA)
- Zoology (AREA)
- Wood Science & Technology (AREA)
- Genetics & Genomics (AREA)
- Biotechnology (AREA)
- Environmental & Geological Engineering (AREA)
- Tropical Medicine & Parasitology (AREA)
- Virology (AREA)
- Medicinal Chemistry (AREA)
- Biomedical Technology (AREA)
- Water Supply & Treatment (AREA)
- Hydrology & Water Resources (AREA)
- Biodiversity & Conservation Biology (AREA)
- Biochemistry (AREA)
- General Engineering & Computer Science (AREA)
- General Health & Medical Sciences (AREA)
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
Abstract
The invention provides a paracoccus P-2 for degrading deltamethrin and application thereof, relating to the technical field of biological engineering. The preservation number of the paracoccus P-2 is CCTCC M2019721. The paracoccus P-2 has a good degradation effect on deltamethrin, the residual quantity of the deltamethrin in the hepatopancreas and muscle tissues of the eriocheir sinensis can be remarkably reduced, the degradation rate of the deltamethrin in the hepatopancreas by the paracoccus P-2 is 60-80%, the degradation efficiency in the muscle is more than 60%, and the paracoccus P-2 can be prepared into a deltamethrin degradation agent and applied to reducing the content of the deltamethrin in the eriocheir sinensis.
Description
Technical Field
The invention belongs to the technical field of bioengineering, and particularly relates to a paracoccus P-2 for degrading deltamethrin and application thereof.
Background
Chinese mitten crabs (Eriocheir sinensis) also called river crabs are popular among people because of delicious taste, rich nutritional value, simple cooking and the like. At present, the breeding quantity and the market demand of river crabs in China are increased at a high speed, and the problems of quality safety and the like are also concerned.
For a long time, the pyrethroid is always considered as a bionic pesticide with high insecticidal efficiency and low toxicity, and becomes organic phosphorus and chlorine after being put into the market; the pesticide-like is effectively replaced. Especially, in the process of culturing economic aquatic animals, the pyrethroid pesticide is introduced to treat fish parasitic diseases, and the effect is very obvious. Therefore, with the continuous expansion of the application range of the pesticide, the disadvantages of the pesticide are gradually revealed, for example, the pyrethroid pesticide is fat-soluble, can invade into aquatic animals such as gills and muscles, and influences the metabolic activity of the aquatic animals through the gills and the like, so that the pyrethroid pesticide residue seriously exceeds the standard, a large amount of death of the aquatic animals is caused, and the pesticide also causes great troubles to the life of human beings and the bearing capacity of the environment.
Disclosure of Invention
In view of the above, the invention aims to provide a paracoccus P-2 for degrading deltamethrin and an application thereof, which can reduce or eliminate the problem of high residual deltamethrin in aquatic economic animals.
In order to achieve the above object, the present invention provides the following technical solutions:
the invention provides Paracoccus sp-2 for degrading deltamethrin, wherein the preservation number of the Paracoccus P-2 is CCTCC M2019721.
Preferably, the 16S rDNA sequence of paracoccus P-2 is as shown in SEQ ID NO: 1 is shown.
The invention also provides a deltamethrin degrading agent which comprises the paracoccus P-2.
The invention also provides application of the paracoccus P-2 or the deltamethrin degrading agent in reducing the content of deltamethrin in the eriocheir sinensis.
Preferably, in the application, the Paracoccus P-2 is added into the culture pond of the Eriocheir sinensis, and the addition amount of the Paracoccus P-2 is108CFU/L。
Preferably, the pH value of the water in the culture pond is 7-8.
Preferably, the concentration of deltamethrin in the culture pond is less than 150 mg/L.
The invention provides Paracoccus sp-2 for degrading deltamethrin, wherein the preservation number of the Paracoccus P-2 is CCTCC M2019721. The degradation characteristics of the paracoccus P-2 are analyzed, the degradation characteristics of the strain are researched by a method for controlling a single-factor variable, and the influence of different inoculation amounts, pH values and initial pesticide concentrations on the degradation capability of the strain is determined. The results show that the bacterial strain has good degradation effect when the pH is 7, the substrate concentration is low and the inoculation amount is large.
Meanwhile, the degradation effect of the strain P-2 on the deltamethrin is verified under the laboratory culture condition. Adding deltamethrin pesticide into the culture water body of the eriocheir sinensis to ensure that the initial concentration reaches 3.0 mu g/L, and then adding separated paracoccus P-2 to ensure that the concentration of the bacterial liquid in the water body is 6.0 multiplied by 108CFU/L. The result shows that in the experimental group added with the degrading strain, the residual quantity of deltamethrin in the hepatopancreas and muscle tissues of the eriocheir sinensis is obviously reduced, the degrading rate of the paracoccus P-2 to the deltamethrin in the hepatopancreas is between 60 and 80 percent, and the degrading efficiency in the muscle is over 60 percent. The bacterial strain is proved to be capable of effectively reducing the residue of deltamethrin in the eriocheir sinensis body, can be used for preparing deltamethrin degradation agent and is applied to reducing the content of deltamethrin in the eriocheir sinensis body.
Drawings
FIG. 1 shows the morphology of strain P-2 on solid MCM medium;
FIG. 2 is a gram stain of strain P-2;
FIG. 3 is a phylogenetic tree of strain P-2;
FIG. 4 is a linear equation of a standard curve of deltamethrin concentration and response value;
FIG. 5 is a graph of the effect of initial concentrations of deltamethrin on degradation;
FIG. 6 is the effect of pH on degradation;
FIG. 7 is a graph of the effect of inoculum size on degradation;
FIG. 8 shows the residual amount of deltamethrin in the hepatopancreas of Eriocheir sinensis;
FIG. 9 shows the residual amount of deltamethrin in the muscle of Eriocheir sinensis.
Biological preservation information
Paracoccus (Paracoccus sp.) for degrading deltamethrin, the serial number of the strain is P-2, the preservation time is 2019.9.12, the preservation place is China Center for Type Culture Collection (CCTCC), the specific address is Bayioney Lojia mountain in Wuchang district, Wuhan City, Hubei province, and the preservation number is CCTCC M2019721.
Detailed Description
The invention provides Paracoccus sp-2 for degrading deltamethrin, wherein the preservation number of the Paracoccus P-2 is CCTCC M2019721.
The paracoccus P-2 is separated from bottom mud soil of a eriocheir sinensis culture pond polluted by pesticide, and the paracoccus P-2 can grow by taking deltamethrin as a unique carbon source. The bacterial colony of the paracoccus P-2 is round and convex, milky, glossy and viscous, and the paracoccus P-2 is gram-negative bacteria and spherical; the paracoccus P-2 is unable to hydrolyze starch and not liquefy gelatin. The 16S rDNA sequence of paracoccus P-2 is shown as SEQ ID NO: 1, and the following components: AACGAACGCTGGCGGCAGGCCTAACACATGCAAGTCGAGCGCACCCTTCGGGGTGAGCGGCGGACGGGTGAGTAACGCGTGGGAATATGCCCTTTGGTACGGAATAGTCCTGGGAAACTGGGGGTAATACCGTATGCGCCCTTCGGGGGAAAGATTTATCGCCAAAGGATTAGCCCGCGTTGGATTAGGTAGTTGGTGGGGTAATGGCCTACCAAGCCGACGATCCATAGCTGGTTTGAGAGGATGATCAGCCACACTGGGACTGAGACACGGCCCAGACTCCTACGGGAGGCAGCAGTGGGGAATCTTAGACAATGGGGGCAACCCTGATCTAGCCATGCCGCGTGAGTGATGAAGGCCCTAGGGTTGTAAAGCTCTTTCAGCTGGGAAGATAATGACGGTACCAGCAGAAGAAGCCCCGGCTAACTCCGTGCCAGCAGCCGCGGTAATACGGAGGGGGCTAGCGTTGTTCGGAATTACTGGGCGTAAAGCGCACGTAGGCGGACCGGAAAGTTGGGGGTGAAATCCCGGGGCTCAACCCCGGAACTGCCTTCAAAACTATCGGTCTGGAGTTCGAGAGAGGTGAGTGGAATTCCGAGTGTAGAGGTGAAATTCGTAGATATTCGGAGGAACACCAGTGGCGAAGGCGGCTCACAGGCTCGATACTGACGCTGAGGTGCGAAAGCGTGGGGAGCAAACAGGATTAGATACCCTGGTAGTCCACGCCGTAAACGATGAATGCCAGTCGTCGGGCAGCATGCTGTTCGGTGACACACCTAACGGATTAAGCATTCCGCCTGGGGAGTACGGTCGCAAGATTAAAACTCAAAGGAATTGACGGGGGCCCGCACAAGCGGTGGAGCATGTGGTTTAATTCGAAGCAACGCGCAGAACCTTACCAACCCTTGACATCCCAGGACCGGCCCGGAGACGGGTCTTTCACTTCGGTGACCTGGAGACAGGTGCTGCATGGCTGTCGTCAGCTCGTGTCGTGAGATGTTCGGTTAAGTCCGGCAACGAGCGCAACCCACACTCTTAGTTGCCAGCATTTGGTTGGGCACTCTAAGAGAACTGCCGATGATAAGTCGGAGGAAGGTGTGGATGACGTCAAGTCCTCATGGCCCTTACGGGTTGGGCTACACACGTGCTACAATGGTGGTGACAGTGGGTTAATCCCCAAAAGCCATCTCAGTTCGGATTGGGGTCCGCAACTCGACCCCATGAAGTTGGAATCGCTAGTAATCGCGGAACAGCATGCCGCGGTGAATACGTTCCCGGGCCTTGTACACACCGCCCGTCACACCATGGGAGTTGGGTCTACCCGACGGCCGTGCGCTAACCAGCAATGGGGGCAGCGGACCACGGTAGGCTCAGCGACTGGGGTG are provided.
The invention also provides a deltamethrin degrading agent which comprises the paracoccus P-2. The concentration of the paracoccus P-2 in the deltamethrin degradation agent is not particularly limited, and the preferable working concentration reaches 6 x 108And (5) CFU/L. The source and the type of the auxiliary materials contained in the deltamethrin degradation agent are not specially limited.
The invention also provides application of the paracoccus P-2 or the deltamethrin degrading agent in reducing the content of deltamethrin in the eriocheir sinensis.
In the application, the Paracoccus P-2 is preferably added into the culture pond of the Eriocheir sinensis, and the addition amount of the Paracoccus P-2 is 108CFU/L. When the deltamethrin is degraded, the pH value of water in the culture pond is preferably 7-8, and more preferably 7. In the invention, when the concentration of deltamethrin in the culture pond is less than 150mg/L, the degradation effect is higher.
The invention provides a method for degrading deltamethrin by using the paracoccus P-2 and the application thereof, which are described in detail in the following examples, but the invention is not limited to the scope of the invention.
Example 1
1. Sample collection
Collecting a bottom mud sample from bottom mud of a eriocheir sinensis culture pond polluted by pesticide for a long time. Removing non-soil substances such as gravel, algae and the like after obtaining the substrate sludge sample, filling the substrate sludge sample into a sample bottle, labeling and marking the collection time, and storing the sample in a refrigerator at 4 ℃ for strain screening.
2. Drugs and reagents
The drugs and reagents used in this example are shown in table 1:
TABLE 1 reagent name and Source
Name of reagent | Purity of | Manufacturer of the product |
NH4Cl | A·R | Xilong chemical corporation |
KH2PO4 | A·R | Xilong chemical corporation |
K2HPO4 | A·R | Xilong chemical corporation |
(NH4)2SO4 | A·R | Xilong chemical corporation |
NH4NO3 | A·R | Xilong chemical corporation |
NaNO3 | A·R | Xilong chemical corporation |
MgSO4·7H2O | A·R | Chemical reagents of national drug group Co Ltd |
Yeast cream | A·R | Chemical reagents of national drug group Co Ltd |
Peptone | A·R | Beijing Oobo Star Biotechnology Limited liability company |
Beef extract | A·R | Shanghai Bo microbial science and technology Co., Ltd |
Agar powder | A·R | Beijing Solaibao Tech & ltTech & gt Ltd |
Deltamethrin standard substance | 99.5% | National pesticide quality supervision and inspection center |
3. Apparatus and device
The instruments and equipment used in this example are shown in table 2:
TABLE 2 names and sources of instruments and devices
4. Preparation of culture medium
Enrichment culture medium: peptone 10.0g, NaCl 1.0g, KH2PO41.0 g and 1000mL of water, and adjusting the pH value to 7.0-8.0.
Basal salt medium (MCM): NH (NH)4NO3 1.0g,MgSO4·7H2O 0.5g,(NH4)2SO4 0.5g,KH2PO40.5g,NaCl 0.5g,K2HPO41.5g, 0.05g of yeast extract and 1000mL of water, and adjusting the pH value to 7.0-8.0.
MCM solid medium: adding agar about 2% to the culture medium to obtain corresponding solid culture medium.
Starch hydrolysis experiment culture medium: 0.5g of beef extract, 0.5g of NaCl, 1.0g of peptone, 0.2g of starch, 2.0g of agar powder and 100mL of distilled water. The tubes were separated in 5mL tubes to a height of about 1/4. Iodine solution is used as indicator.
Gelatin culture medium: 1.0g of peptone, 12.0g of gelatin, 0.5g of beef extract, 0.5g of NaCl, 7.0-7.6 of pH value, 100mL of distilled water and 2.0g of agar powder. The tubes were separated in 5mL tubes to a height of about 1/4.
Sugar fermentation medium: peptone 1.0g, NaCl 0.5g, 1.6% bromocresol purple ethanol solution 0.2mL, pH 7.0, distilled water 100 mL. 1mL of each 20% sugar solution of different types was prepared and aliquoted in 5mL portions to a height of about 1/4 in a test tube.
Indole culture medium: peptone 0.5g, glucose 0.5g, K2HPO40.2g and 100mL of distilled water, and the pH was adjusted to 7.0. The tubes were separated in 5mL tubes to a height of about 1/4. Indole reagent: 1.0g of p-dimethylaminobenzaldehyde; 95mL of ethanol (95%); concentrated hydrochloric acid 20 mL.
M.R culture medium: 0.5g of glucose, 0.5g of peptone and 0.5g of NaCl, adjusting the pH value to 7.0-7.2, and 100mL of distilled water. The tubes were separated in 5mL tubes to a height of about 1/4. Indicator (b): methyl red 0.10g, 95% ethanol 300mL, distilled water 200 mL.
V.P experiments identify the culture media: peptone 0.5g, glucose 0.5g, K2HPO40.2g, 100mL of distilled water, and pH 7.0-7.2. The tubes were separated in 5mL tubes to a height of about 1/4.
The above culture media were sterilized at 121 deg.C for 30min before use.
5. Experimental methods
5.1 isolation and screening of strains
(1) Weighing 1.0g of bottom mud of the eriocheir sinensis pond, adding the bottom mud into 100mL of enrichment medium with 100mg/L of deltamethrin, and uniformly mixing the bottom mud and the enrichment medium by oscillation;
(2) culturing at 30 ℃ for 7d under the culture condition of 180 r/min;
(3) taking out the culture solution, inoculating the culture solution into a fresh enrichment culture medium by 10 percent of inoculation amount, and increasing the concentration of deltamethrin to 200 mg/L;
(4) repeating the step (3), and increasing the concentration of deltamethrin until the final concentration is 500mg/L to obtain an enrichment culture solution;
(5) taking out the enrichment culture solution, inoculating the enrichment culture solution into a basic salt (MCM) culture medium by 10 percent of inoculation amount, adding deltamethrin to ensure that the final concentration is 50mg/L, and culturing for 7d under the constant temperature culture condition of 180r/min at 30 ℃;
(6) repeating the step (5) to obtain a culture solution after domestication;
(7) 1mL of domesticated culture solution is taken for gradient dilution and diluted into 5 concentrations: 10-4~10-8;
(8) Preparing an MCM solid culture medium (deltamethrin is a unique carbon source) with the deltamethrin concentration of 500mg/L, coating the diluent on the solid culture medium, carrying out constant-temperature culture in an oven at 30 ℃ for 3d, and observing the growth condition of colonies;
(9) selecting a flat plate with proper growing density of bacterial colonies for observation, and selecting bacterial colonies with different colors, different smoothness degrees and good growing conditions for purification;
(10) dipping a small amount of strains by using an inoculating loop, repeatedly streaking and purifying on an MCM solid culture medium by adopting a Z-shaped streaking method until a pure single colony is obtained;
(11) and selecting a single colony, adding the single colony into an LB culture medium for amplification culture, and obtaining pure bacterial liquid for storage.
Short-term preservation: the strain is streaked and cultured on MCM solid nutrient medium with the concentration of the deltamethrin being 500mg/L, sealed by a sealing film, stored in a refrigerator at 4 ℃, and the storage time is recorded.
And (3) long-term storage: the bacterial liquid was mixed with equal amount of 40% (W/V) sterilized glycerol, stored in an ultra-low temperature refrigerator at-80 ℃ and the storage time was recorded.
The shape of Paracoccus P-2 on MCM solid medium is shown in figure 1, and the Paracoccus P-2 is round and convex, milky white, glossy and sticky. When the bacterial strain grows on a solid basic salt culture medium which takes deltamethrin as a unique carbon source, a larger colony can grow.
5.2 physiological and Biochemical identification of the Strain
(1) Gram stain
Preparing a smear: under the aseptic condition, a clean glass slide is taken, a drop of bacteria liquid is dripped into the center (the smear is not too thick, the phenomenon that the bacterial dispersion does not affect the dyeing effect) and the glass slide is dried and fixed (the bacterium coating surface faces upwards during fixation, and the glass slide can not be overheated for 2-3 times through flame).
Primary dyeing: adding a drop of crystal violet, dyeing for 1min, washing with water gently, and removing water drops.
Coal dyeing: and (4) dropwise adding iodine solution, dyeing for 1min, washing with water, and removing water drops.
And (3) decoloring: decolorizing with 95% alcohol, shaking the slide slightly, washing with water until the flowing alcohol is not purple, and washing with water slightly after about 30 s.
Counterdyeing: adding safranin staining solution, and washing after 1 min.
Microscopic examination: after natural drying, the mixture was observed under a microscope.
The gram stain results are shown in FIG. 2, where the Paracoccus P-2 strain is gram-negative, coccoid.
(2) Starch hydrolysis test
Shaking the bacterial liquid to a growth logarithmic phase, dipping a small amount of bacterial liquid by using an inoculating loop, inoculating the bacterial liquid on a starch plate, and culturing for 24-48 h at 30 ℃. Iodine solution was then added dropwise to the vicinity of the inoculated colonies, and the whole colony was covered with iodine solution, and the result was immediately examined. If the reaction is positive (i.e., the starch is decomposed), the plate becomes blue as a whole, but the starch is decomposed around the colonies, and a white transparent ring appears.
(3) Experiment of liquefaction of gelatin
Shaking the bacterial liquid to the logarithmic phase of growth, taking 20 mu L of bacterial liquid by using a sterile syringe, penetrating through gelatin colloid, inoculating the bacterial liquid to the center of the culture medium, and slowly injecting to avoid breaking the gel. The culture was carried out at room temperature. From day 2 onwards, it was observed daily whether gelatin could be liquefied by bacteria, since some details could produce gelatinase, which hydrolyzes gelatin into polypeptides, and upon decomposition into amino acids, liquefaction occurred. Those that can cause this phenomenon are positive.
(4) Sugar fermentation experiments:
the bacterial solution was shaken to the logarithmic phase of growth, 20. mu.L of the bacterial solution was taken with a sterile syringe, inoculated into the central part of the medium, cultured at room temperature, and observed every day. If the bromocresol purple turns yellow, the test result is judged to be positive.
(5) Indole experiments
Shaking the bacterial liquid to a growth logarithmic phase, adding 20 mu L of the bacterial liquid into an indole culture medium, culturing at room temperature for 72h, adding an indicator, and judging the bacterial liquid to be positive if a red annular ring appears on the surface layer of the liquid surface. Care was taken not to shake the tube and add the indicator slowly dropwise along the tube wall.
(6) Methyl Red experiment (M. R experiment)
Shaking the bacterial liquid to a growth logarithmic phase, adding 20 mu L of the bacterial liquid into an M.R culture medium, culturing at a constant temperature of 30 ℃, taking out 1ml of the culture liquid after 24 hours, 48 hours, 72 hours and 96 hours respectively, adding a small amount of methyl red indicator (about 2 drops), and judging the culture liquid to be positive if the culture liquid is bright red.
(7) Acetylmethylmethanol experiment (V. P experiment)
And shaking the bacterial liquid to a growth logarithmic phase, adding 20 mu L of the bacterial liquid into a V.P culture medium, and culturing at the constant temperature of 37 ℃ for 1-2 days. Taking out the culture solution, shaking for 2min, adding 5-10 drops of 40% NaOH solution and 5% 1-naphthol solution with the same amount, shaking the test tube again, keeping the temperature at 37 ℃ for 30min, taking out the culture solution, observing, and judging as positive reaction if the culture solution is red.
(8) Catalase test
Dipping a small amount of bacteria on a new MCM plate culture medium by adopting a scribing method, picking fresh single bacterial colonies after the bacteria grow out, adding the single bacterial colonies into a sterile centrifuge tube, and dropwise adding 3% H2O2When 2mL of the solution was observed to have bubbles within 30 seconds, the solution was judged to be positive.
The results of the experiment are shown in table 3:
TABLE 3 physiological and biochemical characteristics of Strain P-2
Physiological and biochemical characteristics | Identification results | Standard bacterium | Physiological and biochemical characteristics | Identification results | Standard bacterium |
Starch hydrolysis | - | - | V.P experiment | - | - |
Gelatin test | - | - | Catalase test | + | + |
Indole experiments | - | - | Glucose | - | - |
M.R experiment | - | - | Sucrose | - | - |
The physiological and biochemical characteristics show that the strain P-2 can not hydrolyze starch and liquefy gelatin, the V.P experiment and the M.R experiment are negative, and the catalase experiment is positive.
(9) Determination of strain species
The 16S rDNA sequence measured by the strain is compared and analyzed in a GenBank database by using BLAST, and the similarity of the sequence and the gene sequence of the strain such as Paracoccus sp is found to reach 99 percent. The phylogenetic tree, physiological, biochemical and morphological characteristics shown in FIG. 3 were combined to confirm that the strain P-2 is Paracoccus.
Example 2
1. Detection of deltamethrin content in culture solution
(1) Mixing 1mL culture solution, 2mL acetone and 2mL n-hexane, performing ultrasonic extraction for 20min, centrifuging at 6000r/min for 5min, and collecting the upper organic phase;
(2) repeating the step (1), and combining the obtained two extraction liquids;
(3)70℃N2drying, and keeping the volume of normal hexane to 1 mL;
(4) pre-leaching the Florisil column by using normal hexane and acetone (9+1, V + V), and discarding the leaching solution;
(5) when the liquid level of the solvent reaches the upper surface in the column, immediately pouring the sample obtained in the step (3), and collecting leacheate;
(6) using N as the sample in (5)2Drying, and keeping the volume of normal hexane to 1 mL;
(7) 100 mu L of the solution is diluted by n-hexane for 100 times to be detected.
The gas chromatographic conditions are represented as follows: the chromatographic column adopts a DB-1 nonpolar capillary chromatographic column 30m 0.25 μm;
temperature programming: maintaining at 80 deg.C for 1min, increasing to 230 deg.C at 15 deg.C/min, and maintaining for 1 min; raising the temperature to 270 ℃ at a speed of 40 ℃/min, and keeping the temperature for 10 min; sample inlet temperature: no shunt sampling at 240 ℃;
flow rate: 1.2mL/min, constant current; sample introduction amount: 1 mu L of the solution; a detector: ECD, 320 ℃; flow rate of carrier gas: nitrogen (N)2) And the tail blowing flow rate is 60 mL/min.
Deltamethrin degradation rate (%) [ 1- (measured residue/control measured residue) ] × 00%
2. Deltamethrin standard recovery rate determination
(1) Adding deltamethrin into a sterilized basic salt liquid culture medium to make the final concentrations of the deltamethrin respectively 40, 80, 120, 160 and 320 mu g/L;
(2) taking 2mL of each concentration, adding 4, 4 and 3mL of n-hexane in sequence, fully oscillating for 2min, performing ultrasonic extraction for 20min, centrifuging at 6000r/min for 10min, and taking an upper organic phase;
(3) after extraction for three times, combining the extracts, filtering, adding a proper amount of anhydrous sodium sulfate to absorb water, using normal hexane to fix the volume to 10mL, and measuring by adopting a gas chromatography-mass spectrometry method. And calculating a regression equation according to the peak area, and calculating the concentration of the sample according to the equation.
The response value of deltamethrin is used as ordinate (Y) and the injection concentration is used as abscissa (X) to make a graph, and the standard curve of deltamethrin is obtained as shown in figure 4, and the linear regression equation is as follows: y 2474.324107 x, correlation coefficient 0.99088274. Therefore, the concentration and the response value of the deltamethrin have a good relationship, and the deltamethrin can be used for detecting the pyrethroid pesticides.
3. Effect of initial concentration on the degradation Rate of the Strain
Inoculating strain seed liquid into basic salt culture medium with final concentration of deltamethrin of 20, 50, 100, 150 and 200mg/L in an inoculation amount of 10%, culturing at 30 ℃ and 180r/min, setting three times for each group, and detecting deltamethrin residue after 5 d.
The results are shown in fig. 5, where represents significant differences (./p < 0.05); as the initial concentration of the pesticide increases, the degradation rate of paracoccus P-2 gradually decreases. When the concentration of the deltamethrin is 20mg/L, the 5d degradation rate is the highest and reaches 88.6%, the degradation effect is inhibited along with the increase of the substrate concentration, and when the concentration of the deltamethrin is 150mg/L, the 5d degradation rate is 83.2%, and is obviously reduced compared with that of the deltamethrin 20 mg/L. The overall degradation effect is obvious, and the degradation rate reaches more than 80 percent.
4. Influence of pH value on degradation rate of strain
In a basic salt culture medium with 100mg/L of deltamethrin, the pH is adjusted to be 2.0, 4.0, 6.0, 7.0 and 8.0. Inoculating strain seed liquid according to the inoculation amount of 10%, culturing at 30 ℃ for 5d at 180r/min, setting three times for each group, and detecting the residual amount of deltamethrin.
The results are shown in fig. 6, where p represents significant differences (× p <0.01, × p < 0.001); the pH value has a great influence on the degradation rate of the strain P-2. The result shows that the degradation effect is poor under the condition of strong acid or strong alkali. When the pH is 7, the degradation rate of 5d is 86.6% at most, and by taking the group as a control, when the pH is 2, 4 and 6, the degradation efficiency of 5d is 24.3%, 36.8% and 60.2% respectively, the degradation rate is obviously reduced, as can be seen from the trend in the figure, the degradation efficiency of the strain begins to show a reduction trend along with the alkaline environment, and when the pH is 8, the degradation efficiency is 74.4%.
5. Effect of inoculum size on degradation rate of strains
Inoculating fresh seed liquid of strains in a basic salt culture medium with 100mg/L of deltamethrin in an inoculation amount of 1%, 3%, 5%, 10% and 15%, culturing at 30 ℃, sampling after 180r/min and 5d, setting three times for each group, and determining the residual quantity of deltamethrin.
Results are shown in fig. 7, representing significant differences (./p < 0.01); the degradation efficiency and the inoculation amount of the strain show a positive correlation trend. The group with the inoculation amount of 15% is used as a control, when the inoculation amount is 1% and 3%, the degradation rate is obviously reduced, and when the inoculation amount reaches 5%, the difference is not obvious. The degradation rates at the inoculum levels of 10% and 15% were 80.1% and 82.5%, respectively.
6. Laboratory use of degrading strain P-2
Deltamethrin is prepared into mother liquor of 100mg/L, 10L of water is added into a culture box, deltamethrin is added to ensure that the final concentration is 3 mug/L, and the group is a control group. Adding deltamethrin with the same concentration into another culture box, and adding paracoccus P-2 to ensure that the concentration of the bacterial liquid in the water body is 6.0 multiplied by 108CFU/L, this group is the experimental group.
After standing for 24h, 30 Chinese mitten crabs are respectively put into the two groups of breeding boxes. After 3, 6, 9, 12 and 15 days of cultivation, the two cultivation boxes respectively take five Chinese mitten crabs out of the five cultivation boxes, respectively take out livers and muscles, and put the livers and the muscles at the temperature of minus 80 ℃ for detecting the pesticide residue in each tissue. Taking the liver and muscle of normal Eriocheir sinensis as control.
Sample treatment:
(1) and adding 10mL of acetonitrile and 2g of NaCl into a centrifuge tube by taking 2g of the tissue homogenate sample, and fully whirling, vibrating and uniformly mixing. Centrifuging for 10min under 10000r/min, and taking the supernatant;
(2) repeating the above operations, and combining; clear liquid;
(3)80 ℃ water bath, N2Drying;
(4) redissolving the residue with 200mL of n-hexane;
LC-Florisil solid phase extraction column
(5) Sequentially activating the small column by using 5mL of acetone and n-hexane (V + V is 1+9), and then adding 5mL of n-hexane;
(6) adding a sample solution, and collecting eluent;
(7) adding 5mL of acetone and n-hexane (V + V ═ 1+9) again for repeated elution, and collecting the eluent;
(8) at 50 deg.C,N2And drying, and then adding n-hexane to a constant volume of 1mL for detection.
The residual amount of deltamethrin in the hepatopancreas of Eriocheir sinensis is shown in FIG. 8, wherein AS is a standard group; DM is deltamethrin group; DM + P-2 is deltamethrin + P-2; blank is normal hepatopancreas; represents significant differences (. about.. p.)<0.01,***p<0.001). The method is proved to be true and effective in detecting the residual quantity by taking no pesticide and degrading bacteria AS reference, the standard addition level (AS) is 4.0 mug/kg, and the detected deltamethrin content is 3.91 +/-0.26 mug/kg. And taking a group added with 3.0 mu g/L of deltamethrin as a control, the deltamethrin content in the hepatopancreas of the eriocheir sinensis shows a trend of increasing first and then decreasing, the deltamethrin content in the hepatopancreas reaches the maximum value of 3.28 +/-0.48 mu g/kg at the 6 th day, and then gradually decreases until the 12 th day, and the deltamethrin residue in the hepatopancreas is below the detection limit. The addition amount of deltamethrin is 3.0 mu g/L, and the added bacterial liquid is 6 multiplied by 108In the CFU/L experimental group, the content of deltamethrin also shows a trend of increasing and then decreasing, at the 6 th day, the content of deltamethrin in the hepatopancreas reaches the maximum value of 1.22 +/-0.28 mu g/kg, and then gradually decreases, and after 12 days, deltamethrin residue cannot be detected in the hepatopancreas. Differential analysis shows that pesticide residue in the experimental group added with the paracoccus P-2 is obviously reduced compared with that in the control group. The degradation rate of the paracoccus P-2 to the deltamethrin is between 60 and 80 percent, and the degradation rate reaches the highest value at the 9 th day, namely 80 percent.
The residual amount of deltamethrin in the muscle of Eriocheir sinensis is shown in FIG. 9, wherein AS is a standard group; DM is deltamethrin group; DM + P-2 is deltamethrin + P-2; blank normal muscle. Note: represents significant differences (× p <0.05, × p <0.01, × p < 0.001). The normal eriocheir sinensis is used AS a reference, no deltamethrin residue is detected in the hepatopancreas of the normal eriocheir sinensis, the standard addition level (AS) is 4.0 mu g/kg, and the deltamethrin residue after the standard addition is detected to be 4.07 +/-0.39 mu g/kg, so that the method is proved to be true and effective in residue detection. The group with the addition of 3.0 mu g/L of deltamethrin is taken as a control group, and the detected trend that the content of deltamethrin in the muscle tissue of the eriocheir sinensis also shows a trend of increasing first and then decreasing is consistent with the detected trend of pesticide residue in the liver and pancreas. At 6d, the deltamethrin content in the muscle tissue reaches 3.93 plus or minus 0.47 mug/kg at the maximum, after which the deltamethrin content in the muscle tissue starts to decrease gradually until reaching the lowest value at 15d, which is 2.38 plus or minus 0.21 mug/kg. In the experimental group added with the pesticide and the paracoccus P-2, the content of deltamethrin in the muscle of the eriocheir sinensis also shows a trend of increasing firstly and then decreasing, and the difference analysis shows that the pesticide residue in the experimental group is obviously reduced compared with that in the control group after the degrading bacteria are added. At 12d, the degradation efficiency is highest and reaches 72%, the overall degradation efficiency in muscle tissues is lower than that of hepatopancreas, and the degradation rate is higher and reaches more than 60% at 3d, 12d and 15 d.
The paracoccus P-2 has a good degradation effect on deltamethrin, the residual quantity of the deltamethrin in hepatopancreas and muscle tissues of eriocheir sinensis can be remarkably reduced, the degradation rate of the deltamethrin in the hepatopancreas by the paracoccus P-2 is between 60% and 80%, and the degradation efficiency in muscles is over 60%.
The foregoing is only a preferred embodiment of the present invention, and it should be noted that, for those skilled in the art, various modifications and decorations can be made without departing from the principle of the present invention, and these modifications and decorations should also be regarded as the protection scope of the present invention.
Sequence listing
<110> university of Nanjing university
<120> Paracoccus P-2 for degrading deltamethrin and application thereof
<160> 1
<170> SIPOSequenceListing 1.0
<210> 1
<211> 1385
<212> DNA
<213> Paracoccus sp.
<400> 1
aacgaacgct ggcggcaggc ctaacacatg caagtcgagc gcacccttcg gggtgagcgg 60
cggacgggtg agtaacgcgt gggaatatgc cctttggtac ggaatagtcc tgggaaactg 120
ggggtaatac cgtatgcgcc cttcggggga aagatttatc gccaaaggat tagcccgcgt 180
tggattaggt agttggtggg gtaatggcct accaagccga cgatccatag ctggtttgag 240
aggatgatca gccacactgg gactgagaca cggcccagac tcctacggga ggcagcagtg 300
gggaatctta gacaatgggg gcaaccctga tctagccatg ccgcgtgagt gatgaaggcc 360
ctagggttgt aaagctcttt cagctgggaa gataatgacg gtaccagcag aagaagcccc 420
ggctaactcc gtgccagcag ccgcggtaat acggaggggg ctagcgttgt tcggaattac 480
tgggcgtaaa gcgcacgtag gcggaccgga aagttggggg tgaaatcccg gggctcaacc 540
ccggaactgc cttcaaaact atcggtctgg agttcgagag aggtgagtgg aattccgagt 600
gtagaggtga aattcgtaga tattcggagg aacaccagtg gcgaaggcgg ctcacaggct 660
cgatactgac gctgaggtgc gaaagcgtgg ggagcaaaca ggattagata ccctggtagt 720
ccacgccgta aacgatgaat gccagtcgtc gggcagcatg ctgttcggtg acacacctaa 780
cggattaagc attccgcctg gggagtacgg tcgcaagatt aaaactcaaa ggaattgacg 840
ggggcccgca caagcggtgg agcatgtggt ttaattcgaa gcaacgcgca gaaccttacc 900
aacccttgac atcccaggac cggcccggag acgggtcttt cacttcggtg acctggagac 960
aggtgctgca tggctgtcgt cagctcgtgt cgtgagatgt tcggttaagt ccggcaacga 1020
gcgcaaccca cactcttagt tgccagcatt tggttgggca ctctaagaga actgccgatg 1080
ataagtcgga ggaaggtgtg gatgacgtca agtcctcatg gcccttacgg gttgggctac 1140
acacgtgcta caatggtggt gacagtgggt taatccccaa aagccatctc agttcggatt 1200
ggggtccgca actcgacccc atgaagttgg aatcgctagt aatcgcggaa cagcatgccg 1260
cggtgaatac gttcccgggc cttgtacaca ccgcccgtca caccatggga gttgggtcta 1320
cccgacggcc gtgcgctaac cagcaatggg ggcagcggac cacggtaggc tcagcgactg 1380
gggtg 1385
Claims (7)
1. A Paracoccus sp P-2 for degrading deltamethrin is characterized in that the preservation number of the Paracoccus P-2 is CCTCC M2019721.
2. The paracoccus P-2 of claim 1, wherein the 16S rDNA sequence of paracoccus P-2 is as set forth in SEQ ID NO: 1 is shown.
3. A deltamethrin degrading agent comprising paracoccus P-2 of claim 1 or 2.
4. Use of the Paracoccus P-2 according to claim 1 or 2 or the deltamethrin degrading agent according to claim 3 for reducing the content of deltamethrin in Eriocheir sinensis.
5. The application of claim 4, wherein the Paracoccus P-2 is added into the culture pond of the Eriocheir sinensis during the application, and the addition amount of the Paracoccus P-2 is 108CFU/L。
6. The use according to claim 5, wherein the pH value of the water in the culture pond is 7-8.
7. The application of claim 6, wherein the concentration of deltamethrin in the culture pond is 20-150 mg/L.
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