CN105621626A - High-concentration chemical sewage composite inocula and use thereof - Google Patents

High-concentration chemical sewage composite inocula and use thereof Download PDF

Info

Publication number
CN105621626A
CN105621626A CN201410619848.2A CN201410619848A CN105621626A CN 105621626 A CN105621626 A CN 105621626A CN 201410619848 A CN201410619848 A CN 201410619848A CN 105621626 A CN105621626 A CN 105621626A
Authority
CN
China
Prior art keywords
parts
sewage
cgmccno
bacillus
agent capable
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.)
Granted
Application number
CN201410619848.2A
Other languages
Chinese (zh)
Other versions
CN105621626B (en
Inventor
王栋
姚春秀
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
JIANGSU YOUNJET ENVIRONMENTAL PROTECTION TECHNOLOGY Co Ltd
Original Assignee
JIANGSU YOUNJET ENVIRONMENTAL PROTECTION TECHNOLOGY Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by JIANGSU YOUNJET ENVIRONMENTAL PROTECTION TECHNOLOGY Co Ltd filed Critical JIANGSU YOUNJET ENVIRONMENTAL PROTECTION TECHNOLOGY Co Ltd
Priority to CN201410619848.2A priority Critical patent/CN105621626B/en
Publication of CN105621626A publication Critical patent/CN105621626A/en
Application granted granted Critical
Publication of CN105621626B publication Critical patent/CN105621626B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)

Abstract

The invention discloses high-concentration chemical sewage composite inocula. The high-concentration chemical sewage composite inocula comprise, by weight, 180-220 parts of bacillus cereus, 150-160 parts of bacillus circulans, 75-85 parts of Exiguobacterium acetylicum, 90-120 parts of bacillus coagulans, 150-170 parts of pseudomonas aeruginosa, 20-25 parts of micrococcus luteus, 120-140 parts of thiobacillus thiooxidans, 180-230 parts of rhodococci, 20-30 parts of lactobacillus brevis, 50-65 parts of paracoccus denitrificans, 95-112 parts of alcaligenes faecalis, 110-125 parts of pseudomonas putida, 100-130 parts of enterobacter aerogenes, 280-320 parts of beer yeast and 140-160 parts of lactobacillus fermenti. All strains of the composite inocula reasonably cooperate with each other, produce synergistic effects, do not produce antagonism, have a high survival rate, is suitable for one step addition and fast forms dominant bacterial community. The high-concentration chemical sewage composite inocula have unique treatment effects on high-concentration chemical sewage, have a COD clearance rate of 94.17%, reduce an operation cost and promote qualified discharge.

Description

A kind of high-concentration chemical industry sewage composite bacteria agent capable and application thereof
Technical field
The invention belongs to sewage treatment area, be specifically related to the formula of a kind of high-concentration chemical industry sewage composite bacteria agent capable.
Background technology
The environmental protection industry of China is started late, but quickly grow, all quickly propelling in all kinds of waste water treatment process technology of sewage treatment area and device fabrication at present, all trades and professions have been built up large number of throughout the country, treatment of sewage factory (station) in large scale, achieves good environmental benefit and social benefit. simultaneously, the environmental protection industry of China also faces many Tough questions, due to eager for instant success and quick profits, substantial amounts of manpower and materials flower in process modification in the introducing process of green technology, in the optimization of equipment retrofit and growth of microorganism environment, but the microorganism that biochemical treatment is played a decisive role, unexpectedly few people make inquiries, to such an extent as to AO method, AAO method, AOAO method, SBR method, CASS method, the numerous sewage treatment process of the item such as CAST method is come on stage one after another, patent and the manufacturer of various fillers are too numerous to mention, but still have at present account for significant percentage of sewage treatment plant (station) cannot be properly functioning, particularly in some high-concentration chemical industry sewage process field, manufacturing enterprise spend huge sums build sewage treatment facility, most ruuning situation is not good enough, not only operating cost is high, but also can not qualified discharge, still discharge beyond standards expense is paid to local environmental administration, what have is even forced to stop production.
The trade effluent complicated component of high concentration, including alkyl halide hydro carbons, olefines, alicyclic hydrocarbon type, heteroaromatic hydro carbons, halogeno-benzene alkanes, tetrabromobisphenol class, nitrobenzene, furan, pyridine, the organic pollution of sulfate and various synthetic is along with the waste water of plant emissions or solid waste entered environment, complexity and biological strange property due to these these body structures of material, these pollutant can not be removed by the microorganism of traditional method of wastewater treatment activated sludge culture effectively, these materials accumulate for a long time in the environment, the ecological environment depended on for existence to us causes very big pollution, very big harm is brought to the physical and mental health of the mankind. quite a few industrial pollution enterprise of China would rather be punished also to be unwilling to invest and administer waste water, even if there have sewage-treatment plant to run to be also abnormal.
Therefore, in a kind of unit volume of exploitation, Biomass is many and biofacies enriches, biological activity is high, rapid decomposable organic substance, and the complex microbial inoculum improving COD, BOD, TOC, ammonia nitrogen and certain specific hard-degraded substance clearance is extremely urgent to current sewage disposal technology.
Summary of the invention
The technical problem to be solved in the present invention is to overcome existing defect, it is provided that a kind of high-concentration chemical industry sewage composite bacteria agent capable, and this composite bacteria agent capable is mixed by the raw material bacterium of following weight portion:
Bacillus cercus 180��220, Bacillus circulans 150��160 parts, acetyl Exiguobacterium sp 75��85 parts, Bacillus coagulans 90��120 parts, Pseudomonas aeruginosa 150��170 parts, micrococcus luteus 20��25 parts, thiobacillus thiooxidant 120��140 parts, Rhodococcus fascians 180��230 parts, Lactobacillus brevis 20��30 parts, Paracoccus denitrificans 50��65 parts, alcaligenes faecalis 95��112 parts, pseudomonas putida 110��125 parts, clostridium perfringen 100��130 parts, addicted to salt Halomonas 200��250 parts, beer yeast 280��320 parts, Lactobacillus fermenti 140��160 parts.
Further, this composite bacteria agent capable is mixed by the raw material bacterium of following weight portion: Bacillus cercus 200 parts, Bacillus circulans 155 parts, acetyl Exiguobacterium sp 80 parts, Bacillus coagulans 100 parts, Pseudomonas aeruginosa 160 parts, micrococcus luteus 23 parts, thiobacillus thiooxidant 130 parts, addicted to salt alkali bacillus 200 parts, halo micrococcus luteus 100 parts, photobacterium phosphoreum 30 parts, Lactobacillus brevis 25 parts, Paracoccus denitrificans 60 parts, alcaligenes faecalis 103 parts, pseudomonas putida 120 parts, clostridium perfringen 120 parts, addicted to salt Halomonas 230 parts, beer yeast 300 parts, Lactobacillus fermenti 150 parts.
Strain of the present invention all can from China Committee for Culture Collection of Microorganisms's common micro-organisms center (CGMCC), China typical culture collection center and American Type Culture collection warehousing (ATCC), Chinese agriculture Microbiological Culture Collection administrative center (ACCC) be commercially available.
The existence form of the composite bacteria agent capable of the present invention is preferably the mixture of lyophilized powder, microbial inoculum or microbial inoculum and solid adjuvant material.
When the existence form of described microbial inoculum is lyophilized powder, preparation method includes Bacillus cercus, Bacillus circulans, acetyl Exiguobacterium sp, Bacillus coagulans, Pseudomonas aeruginosa, micrococcus luteus, Wei Si Salmonella, thiobacillus thiooxidant, Rhodococcus fascians, Lactobacillus brevis, Paracoccus denitrificans, alcaligenes faecalis, pseudomonas putida, clostridium perfringen, beer yeast, Lactobacillus fermenti prepare fermentation liquid respectively, after mixing according to mass ratio, make lyophilized powder by this area conventional method.
A kind of method that high-concentration chemical industry sewage composite bacteria agent capable utilizing the present invention processes sewage, it is characterised in that include following step:
1), polyurethane block filler that diameter the is 0.5��3cm carrier as composite bacteria agent capable is being laid at the bottom of the pond of sewage reactor;
2), adding the 5LCOD diluted treatment sewage at 800��1000mg/L in sewage reactor, add glucose 150��160g, dipotassium hydrogen phosphate 6��8g, Magnesium sulfate heptahydrate 6��8g, wheat bran 40��60g, stirring and dissolving makes culture fluid; The pH of culture fluid is adjusted to 7��7.5;
3), in culture fluid, composite bacteria agent capable 50��80g is added; It is uniformly mixed;
4), water temperature control, at 30��35 DEG C, to stir every day 3��5 times, ventilative half an hour every time;
5), the clearance of the COD of sewage, ammonia nitrogen etc. in every day assaying reaction device; Guarantee that COD of sewage is reducing day by day, represent that strain starts growth, after COD of sewage drops to below 300mg/L, step up concentration and the salinity of influent COD, but total salt concentration need to be controlled and be not more than 40000mg/L, when after 5��10 days circulate, start to continue through the treatment sewage of not diluted.
The invention has the beneficial effects as follows: the sewage disposal composite flora of the present invention can adopt a dosing method, easy and simple to handle, is beneficial to production, it is possible to quickly form dominant microflora; Reasonable compatibility between each strain in formula, symbiosis is coordinated, mutually not antagonism, and the survival rate of microbial inoculum is high. The method that the microbial inoculum using this formula processes sewage is simple, macromole, difficult degradation, poisonous and harmful substance such as phenols, arene and ammonia nitrogen, phosphorus, high-sulfate etc. are had the treatment effect of uniqueness, COD clearance may be up to 94.17%, there is significantly high Treatment Stability and utilization rate, be suitable to high-concentration chemical industry sewage process, the process water yield and water quality treatment can be improved, reduce operating cost, promote qualified discharge.
Detailed description of the invention
Hereinafter the preferred embodiments of the present invention are illustrated, it will be appreciated that preferred embodiment described herein is merely to illustrate and explains the present invention, is not intended to limit the present invention.
Embodiment 1
One utilizes high-concentration chemical industry sewage composite bacteria agent capable, and this composite bacteria agent capable is mixed by the raw material bacterium of following weight portion:
Bacillus cercus 200 parts, Bacillus circulans 155 parts, acetyl Exiguobacterium sp 80 parts, Bacillus coagulans 100 parts, Pseudomonas aeruginosa 160 parts, micrococcus luteus 23 parts, thiobacillus thiooxidant 130 parts, Lactobacillus brevis 25 parts, alcaligenes faecalis 103 parts, pseudomonas putida 120 parts, clostridium perfringen 120 parts, addicted to salt Halomonas 230 parts, beer yeast 300 parts, Lactobacillus fermenti 150 parts.
Wherein said Bacillus cercus is Bacillus cercus (Bacilluscereus): CGMCCNO.3836;
Bacillus circulans is Bacillus circulans is (Bacilluscirculans): CGMCC1.554;
Acetyl Exiguobacterium sp is acetyl Exiguobacterium sp (Exiguobacteriumacetylicum): CGMCCNo.4137;
Bacillus coagulans is Bacillus coagulans is (Bacilluscoagulans) CGMCCNo.7646;
Pseudomonas aeruginosa is Pseudomonas aeruginosa (Pseudomonasaeruginosa): ATCC15442;
Micrococcus luteus is micrococcus luteus (Micrococcusluteus): CGMCCNo.6072;
Thiobacillus thiooxidant is thiobacillus thiooxidant (Thiobacillusthiooxidans) CGMCCNO.2158;
Rhodococcus fascians is Rhodococcus fascians (Rhodococcussp.) CGMCCNo.5287;
Lactobacillus brevis is Lactobacillus brevis (Lactobacillusbrevis) CGMCCNo.6683;
Paracoccus denitrificans is Paracoccus denitrificans (Paracoccusdenitrificans) ACCC10489;
Alcaligenes faecalis is alcaligenes faecalis (Alcaligenesfaecalis) CCTCCNO:M2013176;
Pseudomonas putida is pseudomonas putida (Pseudomonasputida) CCTCCNO:M2013457;
Clostridium perfringen is clostridium perfringen (Enterobacteraerogenes) CGMCC1969;
It is addicted to salt Halomonas (Halomonashalophile) CGMCC12316 addicted to salt Halomonas;
Beer yeast is beer yeast (Saccharomycescerevisiac) ACCC20203;
Lactobacillus fermenti is Lactobacillus fermenti is (Lactobacillusfermentum) CGMCCNo.4648.
Embodiment 2
One utilizes high-concentration chemical industry sewage composite bacteria agent capable, and this composite bacteria agent capable is mixed by the raw material bacterium of following weight portion:
Bacillus cercus 180 parts, Bacillus circulans 150 parts, acetyl Exiguobacterium sp 75 parts, Bacillus coagulans 90 parts, Pseudomonas aeruginosa 150 parts, micrococcus luteus 20 parts, thiobacillus thiooxidant 120 parts, Rhodococcus fascians 180 parts, Lactobacillus brevis 20 parts, Paracoccus denitrificans 50 parts, alcaligenes faecalis 95 parts, pseudomonas putida 110 parts, clostridium perfringen 100 parts, beer yeast 280 parts, Lactobacillus fermenti 140 parts;
Wherein said Bacillus cercus is Bacillus cercus (Bacilluscereus): CGMCCNo.6074;
Bacillus circulans is Bacillus circulans is (Bacilluscirculans): CGMCC1.383;
Acetyl Exiguobacterium sp is acetyl Exiguobacterium sp (Exiguobacteriumacetylicum): CGMCCNo.4137;
Bacillus coagulans is Bacillus coagulans (Bacilluscoagulans) CCTCCM206012
Pseudomonas aeruginosa is Pseudomonas aeruginosa (Pseudomonasaeruginosa): CGMCCNo.1.239;
Micrococcus luteus is micrococcus luteus (Micrococcusluteus): CGMCCNo.7584;
Thiobacillus thiooxidant is thiobacillus thiooxidant (Thiobacillusthiooxidans): CGMCCNO.0759;
Rhodococcus fascians is Rhodococcus fascians (Rhodococcussp.): CGMCCNo.4762;
Lactobacillus brevis is Lactobacillus brevis (Lactobacillusbrevis): CGMCCNO.1306;
Paracoccus denitrificans is Paracoccus denitrificans (Paracoccusdenitrificans): CGMCCNo.3658;
Alcaligenes faecalis is alcaligenes faecalis (Alcaligenesfaecalis): CCTCCNo.M205095;
Pseudomonas putida is pseudomonas putida (Pseudomonasputida): CCTCCNO:2010342;
Clostridium perfringen is clostridium perfringen (Enterobacteraerogenes) CGMCCNo.4155;
It is addicted to salt Halomonas (Halomonashalophile) CGMCC12316 addicted to salt Halomonas;
Beer yeast is beer yeast (Saccharomycescerevisiac): ACCC20203
Lactobacillus fermenti is Lactobacillus fermenti (Lactobacillusfermentum): CGMCCNo.0843.
Embodiment 3
One utilizes high-concentration chemical industry sewage composite bacteria agent capable, and this composite bacteria agent capable is mixed by the raw material bacterium of following weight portion:
Bacillus cercus 220 parts, Bacillus circulans 160 parts, acetyl Exiguobacterium sp 85 parts, Bacillus coagulans 120 parts, Pseudomonas aeruginosa 170 parts, micrococcus luteus 25 parts, thiobacillus thiooxidant 140 parts, Rhodococcus fascians 230 parts, Lactobacillus brevis 30 parts, Paracoccus denitrificans 65 parts, alcaligenes faecalis 112 parts, pseudomonas putida 125 parts, clostridium perfringen 130 parts, beer yeast 320 parts, Lactobacillus fermenti 160 parts.
Wherein said Bacillus cercus is Bacillus cercus (Bacilluscereus): CGMCCNo.6074;
Bacillus circulans is Bacillus circulans is (Bacilluscirculans): ATCC13403;
Acetyl Exiguobacterium sp acetyl Exiguobacterium sp is (Exiguobacteriumacetylicum): CGMCCNo.4137;
Bacillus coagulans is Bacillus coagulans (Bacilluscoagulans) CGMCCNo.7646;
Pseudomonas aeruginosa is Pseudomonas aeruginosa (Pseudomonasaeruginosa): ACCC02722;
Micrococcus luteus is micrococcus luteus (Micrococcusluteus): CGMCCNo.7584;
Thiobacillus thiooxidant is thiobacillus thiooxidant (Thiobacillusthiooxidans) CGMCCNO.2158;
Rhodococcus fascians is Rhodococcus fascians (Rhodococcussp.) CGMCCNo.4762;
Lactobacillus brevis is Lactobacillus brevis (Lactobacillusbrevis) CGMCCNO.1306;
Paracoccus denitrificans is Paracoccus denitrificans (Paracoccusdenitrificans) ACCC10489;
Alcaligenes faecalis is alcaligenes faecalis (Alcaligenesfaecalis) CCTCCNo.M205095
Pseudomonas putida is pseudomonas putida (Pseudomonasputida): CCTCCNO:M209146;
Clostridium perfringen is clostridium perfringen: (Enterobacteraerogenes) CGMCCNo.3163;
It is addicted to salt Halomonas (Halomonashalophile) CGMCC12316 addicted to salt Halomonas;
Beer yeast is beer yeast (Saccharomycescerevisiac) ACCC20203;
Lactobacillus fermenti is Lactobacillus fermenti (Lactobacillusfermentum) CGMCCNo.4648.
Embodiment 4
The formula flora of a kind of composite bacteria agent capable utilized in embodiments of the invention 1 processes the method for sewage:
1) it is, the 0.5 polyurethane block filler carrier as composite bacteria agent capable laying diameter at the bottom of the pond of sewage reactor;
2), adding the 5LCOD diluted treatment sewage at 800g/L, total salt concentration about 4000mg/L in sewage reactor, add glucose 150g, dipotassium hydrogen phosphate 6g, Magnesium sulfate heptahydrate 6g, wheat bran 60g, stirring and dissolving makes culture fluid; The pH of culture fluid is adjusted to about 7;
3), in culture fluid, composite bacteria agent capable 50g is added; It is uniformly mixed;
4), water temperature control, at 35 DEG C, to stir every day 3��5 times, ventilative half an hour every time;
5), the clearance of the COD of sewage, ammonia nitrogen etc. in every day assaying reaction device; Guarantee that COD of sewage is reducing day by day, represent that strain starts growth, after COD of sewage drops to below 300mg/L, passing into COD and be diluted in 1500g/L, total salt concentration is diluted in the treatment sewage of about 7500mg/L, after COD of sewage drops to below 300mg/L, pass into COD and be diluted in 3500g/L, total salt concentration is diluted in the treatment sewage of about 18000mg/L, starts, at full capacity by continuous print sewage, to be no longer diluted after COD of sewage drops to below 300mg/L. After the method for the present embodiment processes 2 weeks, the clearance of the COD of water outlet is up to 91.8%, and the clearance of ammonia nitrogen is up to 97.5%, and total salt concentration also has the clearance of 9.6% simultaneously, and result is as shown in table 1.
The high-concentration chemical industry sewage composite bacteria agent capable treatment effect statistics of table 1 present invention
Project name Water quality before treatment Water quality after process Clearance
COD(mg/L) 5500 451 91.8%
Ammonia nitrogen (mg/L) 650 16 97.5%
Salinity (mg/L) 25000 22600 9.6%
Embodiment 5
The formula flora of a kind of composite bacteria agent capable utilized in embodiments of the invention 3 processes the method for sewage:
1), polyurethane block filler that diameter the is 3cm carrier as composite bacteria agent capable is being laid at the bottom of the pond of sewage reactor;
2), adding 5LCOD in sewage reactor at 1000mg/L, total salt concentration is the diluted treatment sewage of about 3500mg/L, adds glucose 160g, dipotassium hydrogen phosphate 8g, Magnesium sulfate heptahydrate 8g, wheat bran 60g, and stirring and dissolving makes culture fluid; The pH of culture fluid is adjusted to about 7.5;
3), in culture fluid, composite bacteria agent capable 80g is added; It is uniformly mixed;
4), water temperature control, at 32��35 DEG C, to stir every day 3��5 times, ventilative half an hour every time;
5), the clearance of the COD of sewage, ammonia nitrogen etc. in every day assaying reaction device; Guarantee that COD of sewage is reducing day by day, represent that strain starts growth, after COD of sewage drops to below 300mg/L, passing into COD and be diluted in 2000g/L, total salt concentration is diluted in the treatment sewage of about 7000mg/L, after COD of sewage drops to below 300mg/L, pass into COD and be diluted in 5000g/L's, total salt concentration is diluted in the treatment sewage of 19000mg/L, starts, at full capacity by continuous print sewage, to be no longer diluted after COD of sewage drops to below 300mg/L. After the method for the present embodiment processes 2 weeks, the clearance of the COD of water outlet is up to 92.8%, and the clearance of ammonia nitrogen is up to 95.7%, and total salt also has the clearance of 8.7% simultaneously, and concrete outcome is as shown in table 2.
The high-concentration chemical industry sewage composite bacteria agent capable treatment effect statistics of table 2 present invention
Project name Water quality before treatment Water quality after process Clearance
COD(mg/L) 6200 446 92.8%
Ammonia nitrogen (mg/L) 539 23 95.7%
Salinity (mg/L) 23000 21000 8.7%
Last it is noted that the foregoing is only the preferred embodiments of the present invention, it is not limited to the present invention, although the present invention being described in detail with reference to previous embodiment, for a person skilled in the art, technical scheme described in foregoing embodiments still can be modified by it, or wherein portion of techniques feature carries out equivalent replacement. All within the spirit and principles in the present invention, any amendment of making, equivalent replacement, improvement etc., should be included within protection scope of the present invention.

Claims (4)

1. a high-concentration chemical industry sewage composite bacteria agent capable, this composite bacteria agent capable is mixed by the raw material bacterium of following weight portion:
Bacillus cercus 180��220 parts, Bacillus circulans 150��160 parts, acetyl Exiguobacterium sp 75��85 parts, Bacillus coagulans 90��120 parts, Pseudomonas aeruginosa 150��170 parts, micrococcus luteus 20��25 parts, thiobacillus thiooxidant 120��140 parts, Rhodococcus fascians 180��230 parts, Lactobacillus brevis 20��30 parts, Paracoccus denitrificans 50��65 parts, alcaligenes faecalis 95��112 parts, pseudomonas putida 110��125 parts, clostridium perfringen 100��130 parts, addicted to salt Halomonas 200��250 parts, beer yeast 280��320 parts, Lactobacillus fermenti 140��160 parts.
2. a kind of high-concentration chemical industry sewage composite bacteria agent capable as claimed in claim 1, it is characterized in that, described composite bacteria agent capable is mixed by the raw material bacterium of following weight portion: Bacillus cercus 200 parts, Bacillus circulans 155 parts, acetyl Exiguobacterium sp 80 parts, Bacillus coagulans 100 parts, Pseudomonas aeruginosa 160 parts, micrococcus luteus 23 parts, thiobacillus thiooxidant 130 parts, Rhodococcus fascians 200 parts, Lactobacillus brevis 25 parts, Paracoccus denitrificans 60 parts, alcaligenes faecalis 103 parts, pseudomonas putida 120 parts, clostridium perfringen 120 parts, addicted to salt Halomonas 230 parts, beer yeast 300 parts, Lactobacillus fermenti 150 parts.
3. a kind of high-concentration chemical industry sewage composite bacteria agent capable as claimed in claim 2, it is characterised in that wherein said Bacillus cercus is Bacillus cercus (Bacilluscereus): CGMCCNO.3836;
Bacillus circulans is Bacillus circulans is (Bacilluscirculans): CGMCC1.554;
Acetyl Exiguobacterium sp is acetyl Exiguobacterium sp (Exiguobacteriumacetylicum): CGMCCNo.4137;
Bacillus coagulans is Bacillus coagulans is (Bacilluscoagulans) CGMCCNo.7646;
Pseudomonas aeruginosa is Pseudomonas aeruginosa (Pseudomonasaeruginosa): ATCC15442;
Micrococcus luteus is micrococcus luteus (Micrococcusluteus): CGMCCNo.6072;
Thiobacillus thiooxidant is thiobacillus thiooxidant (Thiobacillusthiooxidans) CGMCCNO.2158;
Rhodococcus fascians is Rhodococcus fascians (Rhodococcussp.) CGMCCNo.5287;
Lactobacillus brevis is Lactobacillus brevis (Lactobacillusbrevis) CGMCCNo.6683;
Paracoccus denitrificans is Paracoccus denitrificans (Paracoccusdenitrificans) ACCC10489;
Alcaligenes faecalis is alcaligenes faecalis (Alcaligenesfaecalis) CCTCCNO:M2013176;
Pseudomonas putida is pseudomonas putida (Pseudomonasputida) CCTCCNO:M2013457;
Clostridium perfringen is clostridium perfringen (Enterobacteraerogenes) CGMCC1969;
It is addicted to salt Halomonas (Halomonashalophile) CGMCC12316 addicted to salt Halomonas;
Beer yeast is beer yeast (Saccharomycescerevisiac) ACCC20203;
Lactobacillus fermenti is Lactobacillus fermenti is (Lactobacillusfermentum) CGMCCNo.4648.
4. the method that the high-concentration chemical industry sewage composite bacteria agent capable described in any one of claim 1-3 utilizing the present invention processes sewage, it is characterised in that include following step:
1), polyurethane block filler that diameter the is 0.5��3cm carrier as composite bacteria agent capable is being laid at the bottom of the pond of sewage reactor;
2), adding the 5LCOD diluted treatment sewage at 800��1000mg/L in sewage reactor, add glucose 150��160g, dipotassium hydrogen phosphate 6��8g, Magnesium sulfate heptahydrate 6��8g, wheat bran 40��60g, stirring and dissolving makes culture fluid; The pH of culture fluid is adjusted to 7��7.5;
3), in culture fluid, composite bacteria agent capable 50��80g is added; It is uniformly mixed;
4), water temperature control, at 30��35 DEG C, to stir every day 3��5 times, ventilative half an hour every time;
5), the clearance of the COD of sewage, ammonia nitrogen etc. in every day assaying reaction device; Guarantee that COD of sewage is reducing day by day, represent that strain starts growth, after COD of sewage drops to below 300mg/L, step up concentration and the salinity of influent COD, but the total salt concentration that need to control sewage is not more than 40000mg/L, when after 5��10 days circulate, start to continue through the treatment sewage of not diluted.
CN201410619848.2A 2014-11-05 2014-11-05 A kind of high-concentration chemical industry sewage composite bacteria agent and its application Expired - Fee Related CN105621626B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201410619848.2A CN105621626B (en) 2014-11-05 2014-11-05 A kind of high-concentration chemical industry sewage composite bacteria agent and its application

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201410619848.2A CN105621626B (en) 2014-11-05 2014-11-05 A kind of high-concentration chemical industry sewage composite bacteria agent and its application

Publications (2)

Publication Number Publication Date
CN105621626A true CN105621626A (en) 2016-06-01
CN105621626B CN105621626B (en) 2018-09-28

Family

ID=56037033

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201410619848.2A Expired - Fee Related CN105621626B (en) 2014-11-05 2014-11-05 A kind of high-concentration chemical industry sewage composite bacteria agent and its application

Country Status (1)

Country Link
CN (1) CN105621626B (en)

Cited By (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106906156A (en) * 2017-01-10 2017-06-30 北京师范大学 Microbial inoculum for processing coal-to-olefin waste water
CN107227282A (en) * 2017-08-08 2017-10-03 苏州克莱尔环保科技有限公司 A kind of extraordinary flora of sewage disposal and its cultural method
CN108660178A (en) * 2018-07-19 2018-10-16 佛山皖阳生物科技有限公司 A kind of preparation method of high flocculating rate microbial flocculant
CN109370957A (en) * 2018-12-10 2019-02-22 江南大学 A kind of sewage treatment composite bacteria agent and preparation method thereof
CN109504642A (en) * 2019-01-21 2019-03-22 中国科学院成都生物研究所 One plant of denitrifying bacterium and its application
CN109576184A (en) * 2018-12-25 2019-04-05 重庆融极环保工程有限公司 A kind of complex microbial inoculum for waste water of basic printing and dyeing processing
CN109650642A (en) * 2017-10-11 2019-04-19 卢松 A kind of environment-protective process that xanthan gum industrial wastewater is effectively treated
CN110066747A (en) * 2019-04-04 2019-07-30 上海淳渊环境科技有限公司 A kind of composite bacteria agent and water body total nitrogen processing method
CN110563293A (en) * 2019-09-09 2019-12-13 湖南鑫恒环境科技有限公司 sludge treatment method
CN112625967A (en) * 2020-12-31 2021-04-09 江南大学 Bacterial strain capable of removing cadmium ions and application thereof
CN112831429A (en) * 2020-12-10 2021-05-25 中原环保股份有限公司 Composite microbial inoculum for deodorization of sewage treatment plant and preparation process thereof
CN113955862A (en) * 2020-07-21 2022-01-21 天津市富康德环保科技有限公司 Microbial water purifying agent
CN114921359A (en) * 2022-03-21 2022-08-19 绵津环保科技(上海)有限公司 Environmental microbial inoculum for treating refractory organic matters in high-salinity sewage and application thereof

Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1562820A (en) * 2004-02-10 2005-01-12 凌亮 Method for treating wastewater of carbonization by using microbe
CN1563342A (en) * 2004-02-10 2005-01-12 凌亮 Microbe preparation in use for treating high difficult wastewater and preparation method
CN1603248A (en) * 2003-02-14 2005-04-06 中国科学院南京土壤研究所 Biological denitrification method for ammonium-nitrogen containing waste water and microbes thereof
CN102071140A (en) * 2010-03-26 2011-05-25 无锡中佳科技股份有限公司 Composite microbial biogen capable of degrading organic waste efficiently and preparation method and applications thereof
CN102071141A (en) * 2010-03-26 2011-05-25 无锡中佳科技股份有限公司 Denitrified microbial agent as well as preparation method and application thereof
CN102181386A (en) * 2010-09-10 2011-09-14 中国农业科学院研究生院 Exiguobacterium acetylicum L31 and application thereof
CN102864107A (en) * 2012-09-26 2013-01-09 朱文霞 Microbial preparation for rehabilitating phenyl amine polluted water body
CN103232990A (en) * 2013-04-25 2013-08-07 西华大学 Immobilized microorganism preparation and method for treating high-salinity waste water of pickled vegetable by adopting immobilized microorganism preparation
CN103466903A (en) * 2013-10-10 2013-12-25 浙江汉蓝环境科技有限公司 Method for treating coal chemical industry wastewater by using microorganisms

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1603248A (en) * 2003-02-14 2005-04-06 中国科学院南京土壤研究所 Biological denitrification method for ammonium-nitrogen containing waste water and microbes thereof
CN1562820A (en) * 2004-02-10 2005-01-12 凌亮 Method for treating wastewater of carbonization by using microbe
CN1563342A (en) * 2004-02-10 2005-01-12 凌亮 Microbe preparation in use for treating high difficult wastewater and preparation method
CN102071140A (en) * 2010-03-26 2011-05-25 无锡中佳科技股份有限公司 Composite microbial biogen capable of degrading organic waste efficiently and preparation method and applications thereof
CN102071141A (en) * 2010-03-26 2011-05-25 无锡中佳科技股份有限公司 Denitrified microbial agent as well as preparation method and application thereof
CN102181386A (en) * 2010-09-10 2011-09-14 中国农业科学院研究生院 Exiguobacterium acetylicum L31 and application thereof
CN102864107A (en) * 2012-09-26 2013-01-09 朱文霞 Microbial preparation for rehabilitating phenyl amine polluted water body
CN103232990A (en) * 2013-04-25 2013-08-07 西华大学 Immobilized microorganism preparation and method for treating high-salinity waste water of pickled vegetable by adopting immobilized microorganism preparation
CN103466903A (en) * 2013-10-10 2013-12-25 浙江汉蓝环境科技有限公司 Method for treating coal chemical industry wastewater by using microorganisms

Cited By (16)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106906156A (en) * 2017-01-10 2017-06-30 北京师范大学 Microbial inoculum for processing coal-to-olefin waste water
CN107227282A (en) * 2017-08-08 2017-10-03 苏州克莱尔环保科技有限公司 A kind of extraordinary flora of sewage disposal and its cultural method
CN109650642A (en) * 2017-10-11 2019-04-19 卢松 A kind of environment-protective process that xanthan gum industrial wastewater is effectively treated
CN108660178A (en) * 2018-07-19 2018-10-16 佛山皖阳生物科技有限公司 A kind of preparation method of high flocculating rate microbial flocculant
CN109370957A (en) * 2018-12-10 2019-02-22 江南大学 A kind of sewage treatment composite bacteria agent and preparation method thereof
CN109576184A (en) * 2018-12-25 2019-04-05 重庆融极环保工程有限公司 A kind of complex microbial inoculum for waste water of basic printing and dyeing processing
CN109504642B (en) * 2019-01-21 2022-01-04 中国科学院成都生物研究所 Denitrifying bacterium and application thereof
CN109504642A (en) * 2019-01-21 2019-03-22 中国科学院成都生物研究所 One plant of denitrifying bacterium and its application
CN110066747A (en) * 2019-04-04 2019-07-30 上海淳渊环境科技有限公司 A kind of composite bacteria agent and water body total nitrogen processing method
CN110563293A (en) * 2019-09-09 2019-12-13 湖南鑫恒环境科技有限公司 sludge treatment method
CN110563293B (en) * 2019-09-09 2021-09-28 湖南鑫恒环境科技有限公司 Sludge treatment method
CN113955862A (en) * 2020-07-21 2022-01-21 天津市富康德环保科技有限公司 Microbial water purifying agent
CN112831429A (en) * 2020-12-10 2021-05-25 中原环保股份有限公司 Composite microbial inoculum for deodorization of sewage treatment plant and preparation process thereof
CN112625967A (en) * 2020-12-31 2021-04-09 江南大学 Bacterial strain capable of removing cadmium ions and application thereof
CN112625967B (en) * 2020-12-31 2022-05-10 江南大学 Bacterial strain capable of removing cadmium ions and application thereof
CN114921359A (en) * 2022-03-21 2022-08-19 绵津环保科技(上海)有限公司 Environmental microbial inoculum for treating refractory organic matters in high-salinity sewage and application thereof

Also Published As

Publication number Publication date
CN105621626B (en) 2018-09-28

Similar Documents

Publication Publication Date Title
CN105621626A (en) High-concentration chemical sewage composite inocula and use thereof
US9272933B2 (en) Bio-augmentation composition and use thereof for improving efficiency of effluent treatment in hydrocarbon processing plant
CN106635861B (en) A kind of de- COD denitrification microorganism microbial inoculum of salt tolerant and preparation method thereof
CN103373759B (en) Method for denitrifying wastewater generated in process of producing FCC (fluid catalytic cracking) catalyst
CN103373758B (en) Denitrifying method for ammonia-containing waste water discharged in acrylic production process
CN103373762A (en) Biological denitrification method for salt-containing sewage
KR101207373B1 (en) The probiotics containing mixed strains of bm-s-1 and biological liquid treatment method of organic enriched sludge collected from sewage or waste water using the probiotics
CN104891678B (en) For administering the biologic product of the high-concentration waste water that amino acid fermentation produces
WO2021077453A1 (en) Pseudomonas stutzeri, composite microbial inoculum prepared using the pseudomonas stutzeri, and use of the composite microbial inoculum
CN108117221A (en) A kind of processing method of reverse osmosis concentrated water
CN105198161B (en) A kind of processing preparation suitable for high-concentration hardly-degradable waste water
CN109868233A (en) A kind of efficient acid water special bacteria agent and its application method
CN102745821B (en) Compound microorganism bacterium agent used for sludge reduction, preparation method and application thereof
CN105585133B (en) The biological denitrification method of the high saline sewage of catalyst production process discharge
CN103305443B (en) Preparation and method for restoring ammonia nitrogen-containing industrial sewage
CN103373767B (en) Method for biologically denitrifying high-salinity sewage generated in production process of catalysts
CN105152478B (en) Treatment method of industrial wastewater produced during preparation of sodium glutamate through concentration isoelectric process
CN102373191B (en) Dominant consortium flora for degrading urban waste water and preparation method thereof
CN102515366B (en) Microbiological degradation method for nitrobenzene industrial wastewater
CN109055252A (en) Heterotrophic nitrification-aerobic denitrification composite microbial preparation and preparation method thereof
CN108118008A (en) Microbial bacterial agent of Efficient salt-tolerant and its preparation method and application
CN102643748A (en) Sludge-reduced microorganism combined dominant population in sewage processing
CN103381418B (en) Method for processing tobacco waste or organic fluorine wastewater
CN106635860B (en) A kind of Salt-tolerant microbial agent and its preparation method and application
CN104891677B (en) A kind of preparation technology of the composite bacteria agent capable repairing Amino Acid Fermentation Wastewater

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20180928