CN107345208A - A kind of low-temperature epitaxy green alga and its application for removing nitrogen and phosphorus in sewage - Google Patents

A kind of low-temperature epitaxy green alga and its application for removing nitrogen and phosphorus in sewage Download PDF

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CN107345208A
CN107345208A CN201710467140.3A CN201710467140A CN107345208A CN 107345208 A CN107345208 A CN 107345208A CN 201710467140 A CN201710467140 A CN 201710467140A CN 107345208 A CN107345208 A CN 107345208A
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sewage
green alga
phosphorus
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nitrogen
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CN107345208B (en
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李建宏
刘莉文
杨荧
徐重新
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Nanjing Normal University
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    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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    • C02F2101/30Organic compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/20Nature of the water, waste water, sewage or sludge to be treated from animal husbandry

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Abstract

The invention discloses a kind of green alga, it is identified, it is under the jurisdiction of Chlorophyta (Chlorophyta), Chlorococcum guiding principle (Chlorophyceae), Chlorococcale (Chlorococcales), Shan Zao sections (Scenedesmaceae), four chain Trentepohlias (Tetradesmus), the entitled WU4 of algae strain, is deposited in China typical culture collection center, and deposit number is:CCTCC M 2017335, preservation date are:On June 14th, 2017.The Novel green algae can be used for removing the nitrogen and phosphorus in sewage, significant effect.Relative to prior art, Novel green algae of the present invention, applied to the removal of nitrogen and phosphorus in aquaculture wastewater under cryogenic conditions, application process is simple, and removal efficiency of nitrogen and phosphorus is high, significant effect.

Description

A kind of low-temperature epitaxy green alga and its application for removing nitrogen and phosphorus in sewage
Technical field
The present invention relates to a kind of new low-temperature epitaxy algae and the biology with organic pollution in its Environment control (2), the server end analyzes and processes to the answer data, judges whether answer person's handwriting is effective, if invalid.
Background technology
In recent years, under the vigorously supporting of agricultural sector, large-scale cultivation development in China's is swift and violent, effective guarantee consumer The demand supply growing to meat product, brings huge industrial economy benefit;It is but big caused by large-scale cultivation accumulation Sewage and random discharge are measured, great pollution is caused to ecological environment, while also easily triggers epidemic disease to propagate and spread, seriously Threaten human health and social harmony is stable.Wherein pig excrement and sewage category high concentration organic sewage, the content of nitrogen and phosphorous is big, directly arranges Body eutrophication can be induced by putting, and cause seriously to pollute to water body and ecological environment of soil, be national environmental protection department supervision Emphasis be also prevention and control difficult point.Pig excrement and sewage middle and high concentration nitrogen, the content of phosphorus how are effectively reduced, it is relevant to make up to country Defined discharge standard, ecological environment security is not only concerned, while be also that can pig-breeding industry the sustainable health hair of scale The important restriction factor of exhibition, it has also become the hot subject that multi-crossed disciplines exploratory development urgently solves.
Green alga is a kind of photosynthetic autotrophs biology, have photosynthetic efficiency is high, growth cycle is short, breeding is fast, strong adaptability, training The features such as simple is supported, it needs to absorb nitrogen, the nutriment such as phosphorus in environment in growth course, to complicated in compound body Macromolecular organic matter, so as to reduce the content of the organic substances such as Water, phosphorus, reach the effect of purifying water body.
It is such as of the prior art green but the degraded that green alga is applied to nitrogen and phosphorus in sewage at present also has some defects Algae is all the nitrogen phosphorus in degraded sewage under the normal temperature even hot environment of summer, and at low ambient temperatures, these chlorella growths It is obstructed, nitrogen phosphorus ability step-down of degrading.
Technical scheme
Goal of the invention:
For above-mentioned technical problem, the invention provides a kind of Novel green algae, and by laboratory experiment, it is in pig excrement and sewage Nitrogen, phosphorus organic matter have a significantly consumption degradation function, the algae and its using technology have important scientific research value and it is huge should Use potentiality.
Technical scheme:
To reach the invention described above purpose, identified the invention discloses a kind of green alga, it is under the jurisdiction of Chlorophyta (Chlorophyta), Chlorococcum guiding principle (Chlorophyceae), Chlorococcale (Chlorococcales), Shan Zao sections (Scenedesmaceae), the curved sharp four chains algae (Tetradesmus acuminatus) in four chain Trentepohlias (Tetradesmus), The entitled WU4 of algae strain, i.e. Classification And Nomenclature are:Tetradesmus acuminatus WU4, are deposited in China typical culture collection Center, preservation address:Chinese Wuhan Wuhan Universitys, postcode:430072, deposit number is:CCTCC M 2017335, preservation Date is:On June 14th, 2017.
The 18SrDNA nucleotides of the green alga is as shown in SEQ ID NO.1.
The condition of culture of the green alga is as follows:15 ± 2 degrees Celsius of cultivation temperature, culture matrix are BG11 culture mediums.
The green alga algae strain is by being sampled from high nitrogen and phosphorus content sanitary sewage water body, and gained is screened through culture of isolated.
Culture of isolated screening uses dilution spread method of scoring:Coating, line are that a kind of base of pure culture is obtained in microorganism The classical way of plinth.Algae solution is subjected to proper ratio dilution, filtered using the filter membrane of 0.45 μm of filter sizes, with reference to sterile Fluid nutrient medium washs filtration algae solution repeatedly, while uses flat board culture and picking single bacterium colony technology, so as to obtain axenic culture.
Present invention also offers the application that the green alga removes nitrogen in sewage, the temperature of application is 6-15 degrees Celsius, described Sewage is the breeding wastewater containing high concentration N, phosphorus organic pollution, such as pig excrement and sewage etc..
Present invention also offers the application that the green alga removes phosphor in sewage, the temperature of application is 6-15 degrees Celsius, described Sewage is the breeding wastewater containing high concentration N, phosphorus organic pollution, such as pig excrement and sewage etc..
Specific embodiment described herein is only to spirit explanation for example of the invention Under warm environment, these chlorella growths are obstructed, nitrogen phosphorus ability step-down of degrading.Therefore, the present invention screens a kind of low temperature green alga, can be very Good growth at low ambient temperatures, and nitrogen and phosphorus content in pig excrement and sewage can be removed under cryogenic, the significant effect of acquirement.
Technique effect
Relative to prior art, Novel green algae of the present invention has following technical advantage:
Novel green algae of the present invention, applied to the removal of nitrogen and phosphorus in pig excrement and sewage under cryogenic conditions, application process letter Single, removal efficiency of nitrogen and phosphorus is high, significant effect.
Brief description of the drawings
Fig. 1 is the standard curve of total phosphorus in Method Measuring Total Quantity of Phosphorus;
Fig. 2 is clearance of the WU4 algaes strain of the present invention in pig excrement and sewage total phosphorus
Fig. 3 is the standard curve of total nitrogen in determination of total nitrogen content method;
Fig. 4 is clearance of the WU4 algaes strain of the present invention in pig excrement and sewage total nitrogen.
Embodiment
The present invention is further described below with reference to specific embodiment.
Involved reagent and culture medium prescription in embodiment:
(1) BG11 culture medium prescriptions:
Its constituent is:Contain 30g NaNO in 1L deionized waters3、0.8g K2HPO4、1.5g MgSO4·7H2O、 2.86g H3BO3、1.81g MnCl2·4H2O、0.22g ZnSO4·7H2O、0.39g Na2MoO·2H2O、0.08g CuSO4· 2H2O、0.05g Co(NO3)2·6H2O、1.36g CaCl2、2g Na2CO3, 0.3g ferric citrates, 0.3g citric acids, 0.05g EDTANa2
(2)(1+1)H2SO4
(3) molybdate solution:Dissolve 13g ammonium molybdates (NH4)6MO7O24·4H2O is in 100ml deionized waters.Dissolving 0.35g potassium antimony tartrates KSbC4H4O7·1/2H2O is in 100ml deionized waters.It is in the case where being stirred continuously, ammonium molybdate solution is slow Slowly it is added to 300ml (1+1) H2SO4In, add antimony tartrate potassium solution and be well mixed.Brown Glass Brown glass bottles and jars only, 4 DEG C of preservations.
(4) 10% ascorbic acid solutions:Dissolving 10g ascorbic acid is settled to 100ml with deionized water.Brown Glass Brown glass bottles and jars only, 4 DEG C preserve.
(5) 5%K2S2O8:Dissolve 5g K2S2O8, 100ml is settled to deionized water.
(6) phosphate stock solution:Weigh 0.2197gKH2PO4, add 5ml (1+1) H2SO4, it is settled to deionized water 1000ml。
(7) phosphate standard solution:10ml phosphate stock solution is taken to be diluted in 250ml volumetric flasks with deionized water Graticule.Now match somebody with somebody.
(8) alkaline chitinase solution:Weigh 40g K2S2O8, 15gNaOH, 1000ml is settled to deionized water, is stored in Polyethylene bottle.
(9) (1+9) hydrochloric acid
(10) potassium nitrate Standard Reserving Solution:Weigh 0.7218gKNO3, 1000ml is settled to deionized water.Add 2ml Chloroform is protective agent, and 4 DEG C preserve.
(11) potassium nitrate standard solution:Stock solution is diluted 10 times with deionized water and obtained.
Concrete operation step:
(1) WU4 is separating obtained from sewage water body
Dilution spread method of scoring:Coating, line are that a kind of basic classical way of pure culture is obtained in microorganism, specifically Step is as follows:It is acquired from high nitrogen and phosphorus content sanitary sewage water body with plankton net, the algae of collection is placed on equipped with training In the sample bottle for supporting base.Adopting next water sample from field, impurity is many sometimes, so preliminary filtering need to be carried out to the water sample of collection Processing.Because algae cell density than relatively low, therefore easily causes the failure being separately cultured in sample, in order to avoid directly to collection The failure that sample is separately cultured, enrichment pretreatment first can be carried out to the sample of filtration treatment, add appropriate BG11 trainings thereto Base is supported to accelerate the growth of target algae kind, the frustule in sample is reached the separation training for being advantageous to target algae kind after certain density Support.Algae solution sample to be separated by enrichment culture is carried out gradient dilution with sterilized BG11 culture mediums, then flat board It is coated with partition method and carries out algae kind separation.It is that 1% agar carries out high pressure steam sterilization to add content in the medium, after sterilizing terminates When the temperature of nutrient solution it is cool to 50 degree or so when culture medium poured into sterile petri dish rapidly, that is, it is standby that solid medium is made With.The algae solution of dilution is equably coated in the media surface of sterilizing with spreading rod, is then placed in low temperature and irradiance incubator Culture, the best monoclonal algae kind of picking growing way, that is, completes the separation of new algae strain.Then sterile BG11 cultures are inoculated in Enrichment and growth in base.
The above-mentioned enrichment algae solutions of 50ml are taken, 5000r/min, centrifuge 8min.Supernatant is removed, after then addition liquid nitrogen is fully ground, It is placed in a clean centrifuge tube.400 μ l PlantZol are added, vibration mixes, and sample is suspended completely.Add 7.5 μ l RNase A fully mixes into above-mentioned lysate.55 DEG C are incubated 15 minutes.Add isometric phenol-chloroform-isoamyl alcohol (25:24:1), Vibration mixes, 12000rpm centrifugations 5min.Careful upper strata aqueous phase of drawing in clean centrifuge tube, add isometric phenol-chloroform- Isoamyl alcohol (25:24:1) it is, fully reverse to mix.12000rpm centrifuges 5min, removes supernatant.Add 500 μ l 70% ethanol, whirlpool Rotation vibration 5 seconds, 12000rpm centrifugation 5min, removes supernatant.1-2min is centrifuged again, and exhaust residual liquid.DNA precipitations are dried, are added Enter 50 μ lTE, 65 DEG C of incubation 10min dissolving DNAs, during which flick hydrotropy for several times, 4 DEG C of preservations.
The primer sequence of 18SrDNA for expanding eucaryon green alga is:
- the ACCTGGTTGATCCTGCCAGTAG-3 of upstream 5 " " (SEQ ID NO.2)
- the ACCTTGTTACGACTTCTCCTTCCTCC-3 of downstream 5 " " (SEQ ID NO.3)
PCR reaction conditions:95 DEG C of denaturation 3min;95 DEG C of 30sec, 55 DEG C of 45sec, 72 DEG C of 1min, 32 circulations;Last 72 DEG C extension 10min.Amplified production holds up biology Co., Ltd of section by Nanjing and completes sequencing.
The 18SrDNA nucleotide sequences of the algae strain (WU4) are as shown in SEQ ID NO.1, by observing it under the microscope Form and identification is compared in ncbi database, it is under the jurisdiction of Chlorophyta (Chlorophyta), Chlorococcum guiding principle (Chlorophyceae), Chlorococcale (Chlorococcales), Shan Zao section (Scenedesmaceae), four chain Trentepohlias (Tetradesmus) the curved sharp four chains algae (Tetradesmus acuminatus) in, the entitled WU4 of algae strain, i.e. Classification And Nomenclature are: Tetradesmus acuminatus WU4, are deposited in China typical culture collection center, preservation address:Chinese Wuhan Wuhan University, postcode:430072, deposit number is:CCTCC M 2017335, preservation date are:On June 14th, 2017.
(2) above-mentioned separated algae is cultivated in Nanjing Normal University's algae training room under 15 ± 2 degrees celsius with BG11 Liquid culture.
(3) hoggery sewerage is derived from Nanjing agriculture science institute pig farm.Pig-farm wastewater 0.45 μm of membrane filtration, mistake The pig-farm wastewater of filter is used as experiment material.
The water quality condition of experiment hoggery sewerage
(4) this experiment was carried out 2 months in 2017, and temperature control is at 6-15 degrees Celsius.The pig manure for taking above-mentioned filtering good gives up Water 40ml takes 5ml WU4 algae solutions to be added thereto in 100ml conical flasks, do three it is parallel.In order to which WU4 preferably adapts to pig manure The environment of waste water, is repeatedly transferred.
The stand density (A750nm) of the WU4 of table 1 inoculations for the first time
Second of stand density (A750nm) transferred of the WU4 of table 2
The stand density (A750nm) of the WU4 of table 3 third time switchings
(5) survey it with the algae strain of third time switching and remove the content of nitrogen phosphorus in pig-farm wastewater.
(6) assay method of pig-farm wastewater total phosphorus is ammonium molybdate spectrophotometric method in this experiment.
1. taking 7 50ml color-comparison tubes, 0,0.5,1,3,5,10,15ml phosphate standard solution is added to it respectively, 25ml is settled to deionized water.Then 4ml 5% potassium persulfate solution is added to it, in one piece of gauze of mouth of pipe bag after jumping a queue And tightened with rope.
2. above-mentioned colorimetric cylinder is put into large beaker, it is placed in high-pressure sterilizing pot and heats, 1.1Kg/cm is set2, 120 DEG C, 30min.When pressure indication table in pot subject to sterilization drops to zero, take out colorimetric cylinder and let cool.It is then diluted to 50ml graticules.
3. adding 1ml ascorbic acid solutions in the digestion solution 2. obtained to step respectively, mix.Add 2ml molybdates after 30s Solution, after being stored at room temperature 15min after fully mixing, absorbance is determined at 700nm wavelength.Deduct the absorbance of blank test Afterwards, and corresponding phosphorus content drawing curve (as shown in Figure 1).
4. water sampling 2ml, centrifuge 5000r/min, 3min.Supernatant 1ml is taken to be determined in 50ml color-comparison tubes with deionized water Hold to 25ml.Then 4ml 5% potassium persulfate solution is added to it, is pricked in one piece of gauze of mouth of pipe bag after jumping a queue and with rope Tightly.
5. with step 2..
6. because water sample contains color, (1+1) H of two parts of volumes of mixing is added to its digestion solution2SO4With a volume 10% ascorbic acid solution, mixed liquor will configure on the same day.After being stored at room temperature 15min after fully mixing, determined at 700nm wavelength Absorbance.Phosphorus content is checked in from standard curve after deducting the absorbance of blank test.
The WU4 algaes strain of table 4 removes the efficiency (%) of total phosphorus in pig excrement and sewage
The strain of WU4 algaes removes the percentage of phosphorus in pig excrement and sewage, as a result as shown in Figure 2.
(7) assay method of pig-farm wastewater total nitrogen is potassium persulfate oxidation ultraviolet spectrophotometry in this experiment.
1. taking 8 25ml color-comparison tubes, adding 0,0.5,1,2,3,5,7,8ml potassium nitrate standard to it respectively uses Liquid, and it is diluted to 10ml graticules with deionized water.
2. to above-mentioned color-comparison tube add 5ml alkaline chitinase, after jumping a queue one piece of gauze of mouth of pipe bag and with restrict Tightened.Above-mentioned colorimetric cylinder is put into large beaker, is placed in high-pressure sterilizing pot and heats, 1.1Kg/cm is set2, 120 DEG C, 30min.When pressure indication table in pot subject to sterilization drops to most zero, colorimetric cylinder is taken out, is cooled to room temperature.
3. adding (1+9) hydrochloric acid 1ml, then 25ml graticules are diluted to deionized water.10min is stood after mixing, is used 10mm quartz colorimetric utensils survey its absorbance (A=A220-2 × A275) at 220nm and 275nm respectively.With the absorbance of correction Draw standard curve (as shown in Figure 3).
4. water sampling 2ml, centrifuge 5000r/min, 3min.Supernatant 1ml is taken to be determined in 25ml color-comparison tubes with deionized water Hold to 10ml.Operate below according to Specification Curve of Increasing step 2. -3..Then according to calibration absorbance, looked on calibration curve Go out the nitrogen pool of response, then total nitrogen content is calculated with following equation.
Total nitrogen (mg/L)=m/v
In formula:M is the nitrogen content (μ g) checked in from standard curve;
V is taken volume of water sample (ml)
The WU4 algaes strain of table 5 removes the efficiency (%) of total nitrogen in pig excrement and sewage
The strain of WU4 algaes removes the percentage of nitrogen in pig excrement and sewage, as a result as shown in Figure 4.
Technical scheme is described in detail above-described embodiment, it should be understood that described above Specific embodiment only of the invention, is not intended to limit the invention, it is all done in the spirit of the present invention any repair Change or improve, should be included within the scope of the invention.
SEQUENCE LISTING
<110>Nanjing Normal University
<120>A kind of low-temperature epitaxy green alga and its application for removing nitrogen and phosphorus in sewage
<130> 2017.06
<160> 3
<170> PatentIn version 3.3
<210> 1
<211> 1668
<212> DNA
<213>Four chain Trentepohlias (Tetradesmus)
<400> 1
aactgcttat actgtgaaac tgcgaatggc tcattaaatc agttatagtt tatttggtgg 60
taccttacta ctcggataac cgtagtaatt ctagggctaa tacgtgcgta aatcccgact 120
tctggaaggg acgtatatat tagataaaag gccgaccgag ctttgctcga cccgcggtga 180
accatgatat cttcacgaag cgcatggcct tgagccggcg ctgttccatt caaatttctg 240
ccctatcaac tttcgatggt aggatagagg cctaccatgg tggtaacggg tgacggagga 300
ttagggttcg attccggaga gggagcctga gaaacggcta ccacatccaa ggaaggcagc 360
aggcgcgcaa attacccaat cctgatacgg ggaggtagtg acaataaata acaataccgg 420
gcatttcatg tctggtaatt ggaatgagta caatctaaat cccttaacga ggatccattg 480
gagggcaagt ctggtgccag cagccgcggt aattccagct ccaatagcgt atatttaagt 540
tgttgcagtt aaaaagctcg tagttggatt tcgggtgggt tctagcggtc cgcctatggt 600
gagtactgct atggccttcc tttctgtcgg ggacgggctt ctgggcttca ctgtccggga 660
ctcggagtcg acgtggttac tttgagtaaa ttagagtgtt caaagcaggc ttacgccaga 720
atactttagc atggaataac acgataggac tctggcctat cttgttggtc tgtaggaccg 780
gagtaatgat taagagggac agtcgggggc attcgtattt cattgtcaga ggtgaaattc 840
ttggatttat gaaagacgaa ctactgcgaa agcatttgcc aaggatgttt tcattaatca 900
agaacgaaag ttgggggctc gaagacgatt agataccgtc gtagtctcaa ccataaacga 960
tgccgactag ggattggcga atgttttttt aatgacttcg ccagcacctt atgagaaatc 1020
aaagtttttg ggttccgggg ggagtatggt cgcaaggctg aaacttaaag gaattgacgg 1080
aagggcacca ccaggcgtgg agcctgcggc ttaatttgac tcaacacggg aaaacttacc 1140
aggtccagac atagtgagga ttgacagatt gagagctctt tcttgattct atgggtggtg 1200
gtgcatggcc gttcttagtt ggtgggttgc cttgtcaggt tgattccggt aacgaacgag 1260
acctcagcct gctaaatagt ctcagttgct ttttgcagct ggctgacttc ttagagggac 1320
tattggcgtt tagtcaatgg aagtatgagg caataacagg tctgtgatgc ccttagatgt 1380
tctgggccgc acgcgcgcta cactgatgca ttcaacaagc ctatccttga ccgaagggtc 1440
tgggtaatct ttgaaactgc atcgtgatgg ggatagatta ttgcaattat tagtcttcaa 1500
cgaggaatgc ctagtaagcg caagtcatca gcttgcgttg attacgtccc tgccctttgt 1560
acacaccgcc cgtcgctcct accgattggg tgtgctggtg aagtgttcgg attggcagct 1620
tagggtggca acacctcagg tctgccgaga agttcataaa ccctccca 1668
<210> 2
<211> 22
<212> DNA
<213>Artificial sequence
<400> 2
acctggttga tcctgccagt ag 22
<210> 3
<211> 26
<212> DNA
<213>Artificial sequence
<400> 3
accttgttac gacttctcct tcctcc 26

Claims (8)

1. a kind of green alga, it is characterised in that identified, it is under the jurisdiction of Chlorophyta (Chlorophyta), Chlorococcum guiding principle (Chlorophyceae), Chlorococcale (Chlorococcales), Shan Zao section (Scenedesmaceae), four chain Trentepohlias (Tetradesmus), the entitled WU4 of algae strain, is deposited in China typical culture collection center, and deposit number is:CCTCC M 2017335, preservation date is:On June 14th, 2017.
2. green alga according to claim 1, it is characterised in that the 18SrDNA nucleotides of the green alga such as SEQ ID NO.1 It is shown.
3. green alga according to claim 1, it is characterised in that the condition of culture of the green alga is as follows:Cultivation temperature 15 ± 2 Degree Celsius, culture matrix is BG11 culture mediums.
4. green alga according to claim 1, it is characterised in that the green alga algae strain is dirty by being lived from high nitrogen and phosphorus content Sampled in water water body, gained is screened through culture of isolated.
5. any one of the claim 1-4 green algas remove the application of nitrogen in sewage, it is characterised in that the temperature of the application is 6-15 degrees Celsius.
6. application according to claim 5, it is characterised in that the sewage is pig excrement and sewage or other breeding wastewaters.
7. any one of the claim 1-4 green algas remove the application of phosphor in sewage, it is characterised in that the temperature of the application is 6-15 degrees Celsius.
8. application according to claim 7, it is characterised in that the sewage is pig excrement and sewage or other breeding wastewaters.
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