CN112897824A - Bamboo charcoal-photosynthetic bacteria-constructed wetland integration sewage treatment system - Google Patents
Bamboo charcoal-photosynthetic bacteria-constructed wetland integration sewage treatment system Download PDFInfo
- Publication number
- CN112897824A CN112897824A CN202110451444.7A CN202110451444A CN112897824A CN 112897824 A CN112897824 A CN 112897824A CN 202110451444 A CN202110451444 A CN 202110451444A CN 112897824 A CN112897824 A CN 112897824A
- Authority
- CN
- China
- Prior art keywords
- bamboo charcoal
- photosynthetic bacteria
- treatment system
- sewage treatment
- chamber
- 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.)
- Pending
Links
- 235000017166 Bambusa arundinacea Nutrition 0.000 title claims abstract description 86
- 235000017491 Bambusa tulda Nutrition 0.000 title claims abstract description 86
- 241001330002 Bambuseae Species 0.000 title claims abstract description 86
- 235000015334 Phyllostachys viridis Nutrition 0.000 title claims abstract description 86
- 239000011425 bamboo Substances 0.000 title claims abstract description 86
- 238000011282 treatment Methods 0.000 title claims abstract description 57
- 239000010865 sewage Substances 0.000 title claims abstract description 48
- 230000010354 integration Effects 0.000 title description 2
- 239000003610 charcoal Substances 0.000 claims abstract description 72
- 238000001179 sorption measurement Methods 0.000 claims abstract description 41
- 241000894006 Bacteria Species 0.000 claims abstract description 39
- 230000000243 photosynthetic effect Effects 0.000 claims abstract description 36
- 240000003483 Leersia hexandra Species 0.000 claims abstract description 23
- 229910021536 Zeolite Inorganic materials 0.000 claims abstract description 20
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 claims abstract description 20
- 239000010457 zeolite Substances 0.000 claims abstract description 20
- 230000000813 microbial effect Effects 0.000 claims abstract description 14
- 239000005416 organic matter Substances 0.000 claims abstract description 14
- 238000004891 communication Methods 0.000 claims abstract description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 25
- 238000000034 method Methods 0.000 claims description 19
- 230000008569 process Effects 0.000 claims description 13
- 239000000446 fuel Substances 0.000 claims description 9
- 150000001875 compounds Chemical class 0.000 claims description 4
- 239000002245 particle Substances 0.000 claims description 3
- 239000000758 substrate Substances 0.000 claims description 3
- 238000005406 washing Methods 0.000 claims description 3
- 239000008367 deionised water Substances 0.000 claims description 2
- 229910021641 deionized water Inorganic materials 0.000 claims description 2
- 238000001035 drying Methods 0.000 claims description 2
- 238000001914 filtration Methods 0.000 claims description 2
- 238000011068 loading method Methods 0.000 claims description 2
- 238000002360 preparation method Methods 0.000 claims description 2
- 239000010405 anode material Substances 0.000 claims 1
- 239000010406 cathode material Substances 0.000 claims 1
- 239000002351 wastewater Substances 0.000 abstract description 28
- 238000000746 purification Methods 0.000 abstract description 8
- 239000002131 composite material Substances 0.000 abstract description 5
- 241000196324 Embryophyta Species 0.000 abstract 1
- 231100000614 poison Toxicity 0.000 abstract 1
- 230000007096 poisonous effect Effects 0.000 abstract 1
- 229910001385 heavy metal Inorganic materials 0.000 description 12
- 230000000694 effects Effects 0.000 description 10
- 244000005700 microbiome Species 0.000 description 9
- 239000000126 substance Substances 0.000 description 9
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 8
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 5
- 239000010949 copper Substances 0.000 description 5
- 229910052698 phosphorus Inorganic materials 0.000 description 5
- 239000011574 phosphorus Substances 0.000 description 5
- 231100000331 toxic Toxicity 0.000 description 5
- 230000002588 toxic effect Effects 0.000 description 5
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 description 4
- 239000007836 KH2PO4 Substances 0.000 description 4
- TWRXJAOTZQYOKJ-UHFFFAOYSA-L Magnesium chloride Chemical compound [Mg+2].[Cl-].[Cl-] TWRXJAOTZQYOKJ-UHFFFAOYSA-L 0.000 description 4
- 241000190950 Rhodopseudomonas palustris Species 0.000 description 4
- VMHLLURERBWHNL-UHFFFAOYSA-M Sodium acetate Chemical compound [Na+].CC([O-])=O VMHLLURERBWHNL-UHFFFAOYSA-M 0.000 description 4
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 4
- 239000001110 calcium chloride Substances 0.000 description 4
- 229910001628 calcium chloride Inorganic materials 0.000 description 4
- 229910000396 dipotassium phosphate Inorganic materials 0.000 description 4
- 238000005516 engineering process Methods 0.000 description 4
- 229910000402 monopotassium phosphate Inorganic materials 0.000 description 4
- 229910052757 nitrogen Inorganic materials 0.000 description 4
- 238000012545 processing Methods 0.000 description 4
- 238000004065 wastewater treatment Methods 0.000 description 4
- 239000012138 yeast extract Substances 0.000 description 4
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 3
- 229910052793 cadmium Inorganic materials 0.000 description 3
- BDOSMKKIYDKNTQ-UHFFFAOYSA-N cadmium atom Chemical compound [Cd] BDOSMKKIYDKNTQ-UHFFFAOYSA-N 0.000 description 3
- 239000011651 chromium Substances 0.000 description 3
- 229910052802 copper Inorganic materials 0.000 description 3
- 239000003344 environmental pollutant Substances 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 231100000719 pollutant Toxicity 0.000 description 3
- GNSKLFRGEWLPPA-UHFFFAOYSA-M potassium dihydrogen phosphate Chemical compound [K+].OP(O)([O-])=O GNSKLFRGEWLPPA-UHFFFAOYSA-M 0.000 description 3
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 2
- 229910021578 Iron(III) chloride Inorganic materials 0.000 description 2
- 241000700605 Viruses Species 0.000 description 2
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 2
- 229940041514 candida albicans extract Drugs 0.000 description 2
- 150000001720 carbohydrates Chemical class 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 238000013329 compounding Methods 0.000 description 2
- ZPWVASYFFYYZEW-UHFFFAOYSA-L dipotassium hydrogen phosphate Chemical compound [K+].[K+].OP([O-])([O-])=O ZPWVASYFFYYZEW-UHFFFAOYSA-L 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 229910052564 epsomite Inorganic materials 0.000 description 2
- 238000000855 fermentation Methods 0.000 description 2
- 230000004151 fermentation Effects 0.000 description 2
- XLYOFNOQVPJJNP-ZSJDYOACSA-N heavy water Substances [2H]O[2H] XLYOFNOQVPJJNP-ZSJDYOACSA-N 0.000 description 2
- 229910052739 hydrogen Inorganic materials 0.000 description 2
- 239000001257 hydrogen Substances 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 229910001629 magnesium chloride Inorganic materials 0.000 description 2
- SQQMAOCOWKFBNP-UHFFFAOYSA-L manganese(II) sulfate Chemical compound [Mn+2].[O-]S([O-])(=O)=O SQQMAOCOWKFBNP-UHFFFAOYSA-L 0.000 description 2
- 229910000357 manganese(II) sulfate Inorganic materials 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 229910052751 metal Inorganic materials 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 235000015097 nutrients Nutrition 0.000 description 2
- 235000016709 nutrition Nutrition 0.000 description 2
- 230000035764 nutrition Effects 0.000 description 2
- 238000010672 photosynthesis Methods 0.000 description 2
- 230000029553 photosynthesis Effects 0.000 description 2
- 239000000047 product Substances 0.000 description 2
- 230000001737 promoting effect Effects 0.000 description 2
- 238000004064 recycling Methods 0.000 description 2
- 239000001632 sodium acetate Substances 0.000 description 2
- 235000017281 sodium acetate Nutrition 0.000 description 2
- 239000011780 sodium chloride Substances 0.000 description 2
- 230000001954 sterilising effect Effects 0.000 description 2
- 238000004659 sterilization and disinfection Methods 0.000 description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- VYZAMTAEIAYCRO-UHFFFAOYSA-N Chromium Chemical compound [Cr] VYZAMTAEIAYCRO-UHFFFAOYSA-N 0.000 description 1
- 241000736262 Microbiota Species 0.000 description 1
- 241000209504 Poaceae Species 0.000 description 1
- 229920002472 Starch Polymers 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- XSQUKJJJFZCRTK-UHFFFAOYSA-N Urea Chemical compound NC(N)=O XSQUKJJJFZCRTK-UHFFFAOYSA-N 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 239000013543 active substance Substances 0.000 description 1
- 238000005273 aeration Methods 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- BHPNXACHQYJJJS-UHFFFAOYSA-N bacteriochlorin Chemical compound N1C(C=C2N=C(C=C3NC(=C4)C=C3)CC2)=CC=C1C=C1CCC4=N1 BHPNXACHQYJJJS-UHFFFAOYSA-N 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 239000004202 carbamide Substances 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 235000021466 carotenoid Nutrition 0.000 description 1
- 150000001747 carotenoids Chemical class 0.000 description 1
- 239000012876 carrier material Substances 0.000 description 1
- 239000001913 cellulose Substances 0.000 description 1
- 229920002678 cellulose Polymers 0.000 description 1
- 238000003889 chemical engineering Methods 0.000 description 1
- 229910052804 chromium Inorganic materials 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 230000007123 defense Effects 0.000 description 1
- 239000003599 detergent Substances 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 201000010099 disease Diseases 0.000 description 1
- 208000037265 diseases, disorders, signs and symptoms Diseases 0.000 description 1
- 239000003651 drinking water Substances 0.000 description 1
- 235000020188 drinking water Nutrition 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 230000002708 enhancing effect Effects 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 238000011010 flushing procedure Methods 0.000 description 1
- -1 gravel Substances 0.000 description 1
- 238000005286 illumination Methods 0.000 description 1
- 230000005764 inhibitory process Effects 0.000 description 1
- 238000011221 initial treatment Methods 0.000 description 1
- 230000003993 interaction Effects 0.000 description 1
- 244000144972 livestock Species 0.000 description 1
- 230000005012 migration Effects 0.000 description 1
- 238000013508 migration Methods 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 239000002957 persistent organic pollutant Substances 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 239000008107 starch Substances 0.000 description 1
- 235000019698 starch Nutrition 0.000 description 1
- 238000005728 strengthening Methods 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
- 230000035899 viability Effects 0.000 description 1
Images
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/283—Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
-
- 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
- C02F2101/10—Inorganic compounds
- C02F2101/20—Heavy metals or heavy metal compounds
-
- 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
- C02F2101/10—Inorganic compounds
- C02F2101/20—Heavy metals or heavy metal compounds
- C02F2101/22—Chromium or chromium compounds, e.g. chromates
-
- 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
- C02F3/32—Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
- C02F3/327—Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae characterised by animals and plants
-
- 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
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Water Treatment By Sorption (AREA)
- Biological Treatment Of Waste Water (AREA)
Abstract
The invention discloses a bamboo charcoal-photosynthetic bacteria-constructed wetland integrated sewage treatment system. The treatment system comprises a zeolite zone and an adsorption treatment system which are detachably connected; the adsorption treatment system comprises a first chamber and a second chamber which are communicated with each other; the zeolite zone is in communication with the first chamber; the first chamber and the second chamber are sequentially provided with a Leersia hexandra Swartz, an organic matter adsorption layer, a common adsorption layer and a basal layer from top to bottom. The utility model provides an use leersia hexandra swartz as the aquatic plant in the constructed wetland system, cooperate with the modified bamboo charcoal that has the photosynthetic bacteria through leersia hexandra swartz, and form the microbial cell through the modified bamboo charcoal and the bamboo charcoal that adsorb photosynthetic bacteria, can effectually detach the poisonous and harmful component in the waste water, shorten sewage treatment time, effectual realization carries out purification treatment's purpose to waste water, composite system can separate according to actual conditions simultaneously, every part can be applied to different situations alone, carry out sewage treatment.
Description
Technical Field
The invention belongs to the technical field of sewage treatment, and particularly relates to a bamboo charcoal-photosynthetic bacteria-constructed wetland integrated sewage treatment system.
Background
Domestic sewage is a general term for various kinds of sewage generated by water used in daily life of people. Mainly comprises washing water, flushing water, excrement water and the like, and has sewage discharge of collective units and enterprise and public institutions besides the sewage discharge of families. The main characteristics of the sewage are presented: 1. contains various bacteria, viruses and the like, and is easy to transmit diseases; 2. the contents of nitrogen, phosphorus, sulfur and the like are high; 3. contains saccharide, starch, cellulose, urea, etc. which are easy to generate foul smell under anaerobic condition; 4. contains heavy metals such as copper and cadmium; 5. containing Pharmaceuticals and Personal Care Products (PPCPS); 6. the amount of residual disinfection by-products (DBPS) commonly used in drinking water is too high. Due to the appearance of biodiversity, novel detergents and bathroom products, the treatment of bacteria, viruses and difficultly degraded sewage in sewage is increased, and meanwhile, due to the appearance of external factors such as multiple weather changes, the single treatment technology is difficult to achieve effective effect, and the emission requirement can be met only by combining several treatment technologies to form a system to play a role together.
Photosynthetic bacteria (PSB) are a type of light-powered, CO-powered2Or organic matter as a carbon source, and water-ring microorganisms that undergo vegetative propagation by photosynthesis are widely found in nature and are more common in water areas with high organic matter concentrations. The photosynthetic bacteria are gram-negative bacteria, contain various nutrient substances and physiologically active substances, and have the functions of photosynthesis, fermentation, nitrogen fixation, heavy metal removal, hydrogen production and the like. The use of photosynthetic bacteria in sewage treatment began in the 1960 s. The self-cleaning process of high-concentration organic wastewater in nature is the result of ecological succession of microbiota with different nutrition levels, discovered by Japan scientist Xiaolin Zhengtai and the like, and the photosynthetic bacteria pass through the processPlays an important role in the process, and firstly, researches on the treatment of organic wastewater by a photosynthetic bacteria method are carried out. Compared with the currently widely used biological wastewater treatment systems such as an activated sludge process, a biofilm process and an anaerobic process, the PSB can directly and efficiently treat various high-concentration organic wastewater under natural illumination and trace aerobic conditions, and the wastewater does not need to be diluted before treatment. Meanwhile, hydrogen is generated in the treatment process, so that a way is provided for the development of new energy. The photosynthetic bacteria cell contains rich nutrient substances such as bacteriochlorin, carotenoid and the like, can be comprehensively utilized and can not cause secondary pollution when being used as the bait of livestock and the like.
Bamboo charcoal as a porous medium material has high porosity, large specific surface area, good adsorbability, stable physical and chemical properties, low cost and easy acquisition, has the performance characteristics of a microorganism immobilized carrier material, and can be used as a microorganism immobilized carrier. There have been reports on the adsorption of microorganisms on waste water by using bamboo charcoal as a carrier. Rosujun et al (water treatment technology 2009, 35(3):86-89) report that the treatment effect of the biological aerated filter is improved by using bamboo charcoal to adsorb EM; sunxiang et al (environmental science and technology, 2009, 32 (3): 151-; zhoushan et al (journal of chemical engineering in colleges and universities 2008, 22(5): 889-. In the methods, the aerobic microorganisms or the mixed flora of the aerobic microorganisms and the anaerobic microorganisms are fixed by using bamboo charcoal, so that aeration is needed in the sewage treatment process, and the treatment cost is increased. Meanwhile, in the culture process of the mixed flora, the growth of part of strains is inhibited and the like due to nutrition and space competition among the strains, so that the sewage treatment effect is influenced. The activated bamboo charcoal is used for adsorbing photosynthetic bacteria to treat sewage, and no relevant report is provided at home.
In addition, the sewage contains COD, phosphorus, ammonia nitrogen and other pollutants, and also contains various heavy metal pollutants, and the Leersia hexandra Swartz is a good choice for removing the heavy metal pollutants. Leersia hexandra Swartz is a perennial gramineae plant, has strong vitality and strong environmental adaptability, and is widely applied to wetland systems for treating heavy metal chromium in recent years. The Leersia hexandra Swartz has strong enrichment effect on metal Cr (III) and Cr (IV) and has good tolerance on metal Cu.
Therefore, the method for treating sewage by compounding the leersia hexandra and the photosynthetic bacteria adsorbed by the modified bamboo charcoal to form the artificial wetland has no relevant report in China, and the method for compounding the leersia hexandra and the photosynthetic bacteria and researching the interaction relationship of the leersia hexandra and the photosynthetic bacteria has no relevant report in China.
Disclosure of Invention
Aiming at the defects in the prior art, the invention provides a bamboo charcoal-photosynthetic bacteria-constructed wetland integrated sewage treatment system which can effectively remove nitrogen, phosphorus, COD and BOD in wastewater5Cadmium, copper and the like, and enhances the decomposition, migration and conversion capability of the organic pollutants which are toxic, harmful and difficult to degrade in the wastewater.
In order to achieve the purpose, the technical scheme adopted by the invention for solving the technical problems is as follows:
a bamboo charcoal-photosynthetic bacteria-constructed wetland integrated sewage treatment system comprises a zeolite area and an adsorption treatment system which are connected in a detachable way; the adsorption treatment system comprises a first chamber and a second chamber which are communicated with each other; the zeolite zone is in communication with the first chamber; the first chamber and the second chamber are sequentially provided with a Leersia hexandra Swartz, an organic matter adsorption layer, a common adsorption layer and a basal layer from top to bottom.
Further, the particle size of the zeolite is 26-30 mm.
Further, the zeolite particle size was 26.5 mm.
Further, the organic matter adsorption layer is a photosynthetic bacteria layer loaded by the modified bamboo charcoal.
Further, the preparation method of the modified bamboo charcoal comprises the following steps: washing the activated bamboo charcoal with deionized water, drying, placing in a muffle furnace, and modifying at 700 deg.C.
Further, the process of loading photosynthetic bacteria on the modified bamboo charcoal comprises the following steps: concentrating photosynthetic bacteria culture solution by 3-5 times, adjusting pH to 4.0-5.0, adding modified bamboo charcoal pulverized to 5-10 mesh, adsorbing at 30-40 deg.C and 80-100r/min for 4-5 hr, and filtering.
Furthermore, the load capacity of the photosynthetic bacteria is that 15-25g of modified bamboo charcoal is added into every 100mL of photosynthetic bacteria culture solution.
Further, the photosynthetic bacteria are commercially available Rhodopseudomonas palustris (Rhodopseudomonas palustris) with a deposit number of: CCREM SDMCC 150013, ACCC10650, CGMCC1.2349 or GIM 1.167.
Further, the production method of the rhodopseudomonas palustris seed liquid comprises the following steps: adding NH to every 1000mL of water4Cl1.0-1.5g、CH3COONa 2.5-3.5g、MgCl2 0.1-0.18g,CaCl2 0.1-0.25g、KH2PO40.55-0.6g,K2HPO40.38-0.52g of NH and 0.1-0.25g of yeast extract4Cl、CH3COONa、MgCl2、CaCl2、KH2PO4、K2HPO4And dissolving yeast extract in water, adjusting pH to 7.5-8.5, sterilizing at 110-8CFU/mL Rhodopseudomonas palustris seed liquid.
Further, the production method of the fermentation liquor comprises the following steps: adding 3-4g of sodium acetate and NH into 1000mL of water4Cl 2-3g、NaCl 0.1-0.25g、CaCl2 0.05-0.08g、KH2PO4 0.5-0.6g、K2HPO4 0.3-0.45g、MgSO4·7H2O 0.2-0.3g、MnSO4·2H2O 0.02-0.035g、FeCl30.002-0.004g of sodium acetate and 0.1-0.2g of yeast extract4Cl、NaCl、CaCl2、KH2PO4、K2HPO4、MgSO4·7H2O、MnSO4·2H2O、FeCl3And yeast extract dissolved in water at a natural pH in110-115 ℃ sterilization for 25-30 minutes, and cooling to 30-40 ℃.
Further, the common adsorption layer is a bamboo charcoal layer.
Further, the substrate layer is composed of gravels with the grain diameter of 10-20 mm.
Furthermore, a first water inlet is formed in the bottom of the zeolite area, a second water inlet communicated with the zeolite area is formed in the upper end of the adsorption treatment system, and a water outlet is formed in the bottom of the adsorption treatment system on the side far away from the zeolite area.
A microbial fuel cell comprises an anode and a cathode, wherein the anode is modified bamboo charcoal or bamboo charcoal; the cathode is modified bamboo charcoal or bamboo charcoal; and the anode and the cathode are made of different materials, namely when the anode is the modified bamboo charcoal, the cathode is the bamboo charcoal.
Further, the modified bamboo charcoal and the bamboo charcoal are filled into the roller; the roller is provided with a plurality of through holes with the diameter smaller than that of the modified bamboo charcoal and the bamboo charcoal.
Further, the modified bamboo charcoal and the bamboo charcoal are both provided with wires; the lead extends out of the compound sewage treatment system, and a resistor is arranged between the lead and the compound sewage treatment system.
Further, the resistor may be an LED lamp.
The invention has the beneficial effects that:
1. modified bamboo charcoal loaded photosynthetic bacteria in the application mainly aim at the non-degradable toxic and harmful organic matters, are degraded through organic matter strengthening, eliminate the inhibition of the toxic and harmful organic matters on wetland microorganisms, and are matched with Leersia hexandra Swartz to further remove components such as heavy metals in wastewater, thereby effectively realizing the purpose of purifying the wastewater.
2. In the composite system, the photosynthetic bacteria not only can play a role of purifying sewage by themselves, but also can induce and improve the resistance of the Leersia hexandra Swartz through a defense signal cross effect, thereby enhancing the viability of the Leersia hexandra Swartz in a harmful environment and the removal rate of heavy metal components.
3. The activated bamboo charcoal has higher porosity and larger specific surface area after being modified, can effectively promote the adsorption effect of the activated bamboo charcoal on harmful components in the wastewater, and simultaneously can also promote the contact area of the bamboo charcoal and photosynthetic bacteria, thereby greatly promoting the load capacity on the photosynthetic bacteria, and further promoting the purification effect of a system on the wastewater.
4. This application is constituteed by zeolite district and adsorption system that is linked together, but zeolite district and adsorption system in this application both independent settings can be split into solitary functional unit, can be according to actual conditions's needs, carry out split or combination with both, then exert corresponding purification performance again, can be applicable to the waste water treatment of various different conditions, have promoted the throughput of processing system to waste water under different conditions greatly.
5. When the adsorption system treats wastewater, the modified bamboo charcoal and the bamboo charcoal which adsorb photosynthetic bacteria in the system form the microbial cell, namely the modified bamboo charcoal is used as the anode or the cathode of the microbial cell, and then the bamboo charcoal is used as the corresponding cathode or the anode. The microbial battery who forms not only can be with the chemical energy conversion of the processing in-process electric energy, accomplish and retrieve clean energy from waste water, can also effectually accelerate the purification treatment efficiency of lift system to sewage, shorten the processing time of system to sewage greatly.
Drawings
FIG. 1 is a schematic diagram of the present system;
FIG. 2 is a schematic structural view of an organic substance adsorbing layer;
fig. 3 is a schematic structural view of a general adsorption layer.
Wherein, 1, a basal layer; 2. a common adsorption layer; 3. an organic substance adsorbing layer; 4. leersia hexandra Swartz; 5. a second water inlet; 6. a water outlet; 7. a zeolite zone; 8. a first water inlet; 9. a third water inlet; 10. a first chamber; 11. a second chamber; 12. a wire; 13. a drum; 14. and a through hole.
Detailed Description
The following description of the embodiments of the present invention is provided to facilitate the understanding of the present invention by those skilled in the art, but it should be understood that the present invention is not limited to the scope of the embodiments, and it will be apparent to those skilled in the art that various changes may be made without departing from the spirit and scope of the invention as defined and defined in the appended claims, and all matters produced by the invention using the inventive concept are protected.
Examples
As shown in fig. 1, the bamboo charcoal-photosynthetic bacteria-constructed wetland integrated sewage treatment system comprises a zeolite zone 7 and an adsorption treatment system, wherein the adsorption treatment system is composed of a first chamber 10 and a second chamber 11 which are independent from each other, and the first chamber 10 and the second chamber 11 are communicated through a second water inlet 5 arranged at the upper end.
As shown in fig. 1, a first water inlet 8 for wastewater to enter the system is opened at the upper end of the zeolite zone 7, and then a third water inlet 9 communicated with a first chamber 10 is opened at the bottom of the zeolite zone 7. Meanwhile, the zeolite area 7 and the adsorption treatment system are independently arranged, so that the zeolite area 7 and the adsorption treatment system can be separated according to actual use conditions, and the two can work independently.
As shown in fig. 1, the adsorption treatment system comprises a leersia hexandra swartz 4, an organic matter adsorption layer 3, a common adsorption layer 2 and a substrate layer 1 which are sequentially arranged from top to bottom, wherein a second water inlet 5 is formed at the upper end of the system, and a water outlet 6 is formed at the bottom of the system; the organic matter adsorption layer 3 and the common adsorption layer 2 are filled in the roller 13, and the roller 13 is provided with a through hole 14 with the aperture smaller than the diameters of the modified bamboo charcoal and the bamboo charcoal. And the modified bamboo charcoal and the bamboo charcoal are both filled with wires 12 extending to the outside of the system, and resistors are arranged between the wires 12 and can be LED lamps.
Wherein, leersia hexandra 4 can carry out primary treatment to the entering waste water when treating the waste water, removes the components such as heavy metal contained therein, and carries out primary purification to the waste water.
And then the wastewater is further treated by an organic matter adsorption layer 3 formed by the modified bamboo charcoal-loaded photosynthetic bacteria, toxic and harmful organic matter components contained in the wastewater are removed, the toxic and harmful organic matter components are degraded into components such as macromolecular saccharides and the like which can be utilized by microorganisms in the environment, and the wastewater treatment efficiency can be remarkably improved by matching the organic matter adsorption layer with the Leersia hexandra Swartz.
Finally, the waste water is finally disinfected and purified by a common adsorption layer 2 formed by bamboo charcoal and a base layer 1 formed by gravels, and the whole purification process of the waste water is completed.
When the inland inundation takes place in the city, can cooperate through zeolite district 7 or the absorption processing system that this system or this system in the split come and the blowdown clean system of city itself, or sponge city, reach and alleviate the inland inundation of city fast, purify the effect of urban sewage, promoted the treatment effect of sewage.
Meanwhile, the modified bamboo charcoal in the system can be used as an anode or a cathode, the bamboo charcoal can be used as the anode or the cathode opposite to the modified bamboo charcoal, a special microbial fuel cell is formed, chemical energy in the treatment process can be converted into electric energy while sewage formed by urban inland inundation is treated, and corresponding clean energy can be obtained through recycling. And due to the existence of the microbial fuel cell, the sewage purification time of the system can be greatly shortened, and compared with a system without the microbial fuel cell, the treatment time for achieving the same treatment effect can be shortened by more than half.
In addition, since the Leersia hexandra Swartz matched with the modified bamboo charcoal loaded with photosynthetic bacteria is added into the adsorption system, the heavy metal components contained in the water body can be removed while the sewage is adsorbed and purified, and the adsorption system can be independently used for treating the heavy metal pollution of rivers or sewage.
The system can play a self-adsorption purification function of photosynthetic bacteria, modified bamboo charcoal, gravel, bamboo charcoal and other components on sewage, and can be matched with Leersia hexandra Swartz to form a closed-loop sustainable system, in the system, the modified bamboo charcoal adsorbing the photosynthetic bacteria is used as an anode or a cathode, and the bamboo charcoal in the common adsorption layer 2 is used as a cathode or an anode corresponding to the modified bamboo charcoal, so that the microbial fuel cell is formed. The microbial battery can convert chemical energy in the treatment process into electric energy, and the process of recycling clean energy from the wastewater is completed.
Examples of the experiments
1. The composite system prepared by the method is used for treating wastewater containing heavy metal components for 36h, and CO is contained in 100kg of wastewaterThe D content is 460.5mg/L, BOD5The content is 605.7mg/L, the ammonia nitrogen content is 22.3mg/L, the phosphorus content is 6.4mg/L, Cu, the content is 12.6mg/L, Cd, and the content is 5.8 mg/L; meanwhile, the combination of bamboo charcoal + leersia hexandra swartz, photosynthetic bacteria and bamboo charcoal + photosynthetic bacteria is used as a control group, and the treatment results of the experimental group and the control group on the wastewater are shown in table 1.
TABLE 1 results of wastewater treatment
As can be seen from the data in Table 1, the sewage treatment system is constructed by adopting a composite mode of modified bamboo charcoal, photosynthetic bacteria and Leersia hexandra Swartz, and a microbial fuel cell is formed during sewage treatment, so that the constructed system can effectively remove harmful components such as COD (chemical oxygen demand), nitrogen, phosphorus, cadmium, copper and the like contained in the sewage within about 36 hours, and the purified wastewater meets the requirements of the comprehensive sewage discharge standard. In addition, the comparison with a control group shows that the composite system prepared by the embodiment of the application has higher removal rate of heavy metal components and COD compared with the bamboo charcoal + Leersia hexandra without adding photosynthetic bacteria.
Claims (10)
1. A bamboo charcoal-photosynthetic bacteria-constructed wetland integrated sewage treatment system is characterized by comprising a zeolite area and an adsorption treatment system which are detachably connected; the adsorption treatment system comprises a first chamber and a second chamber which are communicated with each other; the zeolite zone is in communication with the first chamber; the first chamber and the second chamber are sequentially provided with a Leersia hexandra Swartz, an organic matter adsorption layer, a common adsorption layer and a basal layer from top to bottom.
2. The bamboo charcoal-photosynthetic bacteria-constructed wetland integrated sewage treatment system according to claim 1, wherein the organic matter adsorption layer is a modified bamboo charcoal-loaded photosynthetic bacteria layer.
3. The bamboo charcoal-photosynthetic bacteria-constructed wetland integrated sewage treatment system according to claim 2, wherein the preparation method of the modified bamboo charcoal comprises the following steps: washing the activated bamboo charcoal with deionized water, drying, placing in a muffle furnace, and modifying at 700 deg.C.
4. The bamboo charcoal-photosynthetic bacteria-constructed wetland integrated sewage treatment system according to claim 2, wherein the process of loading photosynthetic bacteria on the modified bamboo charcoal comprises the following steps: concentrating photosynthetic bacteria culture solution by 3-5 times, adjusting pH to 4.0-5.0, adding modified bamboo charcoal pulverized to 5-10 mesh, adsorbing at 30-40 deg.C and 80-100r/min for 4-5 hr, and filtering.
5. The bamboo charcoal-photosynthetic bacteria-constructed wetland integrated sewage treatment system according to claim 4, wherein the photosynthetic bacteria load is 15-25g of modified bamboo charcoal per 100mL of photosynthetic bacteria culture solution.
6. The bamboo charcoal-photosynthetic bacteria-constructed wetland integrated sewage treatment system according to claim 1, wherein the common adsorption layer is a bamboo charcoal layer.
7. The bamboo charcoal-photosynthetic bacteria-constructed wetland integrated sewage treatment system according to claim 1, wherein the substrate layer is composed of gravels with the particle size of 10-20 mm.
8. The microbial fuel cell is characterized by comprising an anode and a cathode, wherein the anode is modified bamboo charcoal or bamboo charcoal; the cathode is modified bamboo charcoal or bamboo charcoal; and the anode and cathode materials are different.
9. The microbial fuel cell according to claim 8, wherein the modified bamboo charcoal and the bamboo charcoal are both filled in the roller; the roller is provided with a plurality of through holes with the diameter smaller than that of the modified bamboo charcoal and the bamboo charcoal.
10. The microbial fuel cell according to claim 8, wherein the modified bamboo charcoal and the bamboo charcoal are both provided with a wire; the lead extends out of the compound sewage treatment system, and a resistor is arranged between the lead and the compound sewage treatment system.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202110451444.7A CN112897824A (en) | 2021-04-26 | 2021-04-26 | Bamboo charcoal-photosynthetic bacteria-constructed wetland integration sewage treatment system |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202110451444.7A CN112897824A (en) | 2021-04-26 | 2021-04-26 | Bamboo charcoal-photosynthetic bacteria-constructed wetland integration sewage treatment system |
Publications (1)
Publication Number | Publication Date |
---|---|
CN112897824A true CN112897824A (en) | 2021-06-04 |
Family
ID=76108888
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202110451444.7A Pending CN112897824A (en) | 2021-04-26 | 2021-04-26 | Bamboo charcoal-photosynthetic bacteria-constructed wetland integration sewage treatment system |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN112897824A (en) |
Citations (14)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101851023A (en) * | 2010-03-26 | 2010-10-06 | 北京神州瑞霖环保科技有限公司 | Underflow type constructed wetland system with coke powder-steel slag compound filler |
CN101921044A (en) * | 2010-08-11 | 2010-12-22 | 环境保护部南京环境科学研究所 | Two-stage anaerobic-tower type filter chamber livestock/poultry wastewater treatment system and treatment process |
CN102263279A (en) * | 2011-07-06 | 2011-11-30 | 武汉理工大学 | Microbial fuel cell device with artificial wetland aquatic plant electrodes |
CN102583770A (en) * | 2012-01-16 | 2012-07-18 | 湖南农业大学 | Bamboo charcoal-photosynthetic bacteria integrated municipal sanitary wastewater treating agent |
CN102583886A (en) * | 2012-02-21 | 2012-07-18 | 海南农丰宝肥料有限公司 | Artificial wetland for treating sewage |
CN102690021A (en) * | 2012-05-24 | 2012-09-26 | 金丹越 | Dispersive domestic sewage advanced pretreatment system |
CN102897968A (en) * | 2012-08-31 | 2013-01-30 | 中国矿业大学(北京) | Counter flow type vertical flow artificial wetland system |
CN103172226A (en) * | 2013-04-15 | 2013-06-26 | 东南大学 | Surface water stagnation type baffling wetland system for synchronously and intensively removing nitrogen, phosphorus and estrogen |
CN105502672A (en) * | 2016-01-13 | 2016-04-20 | 桂林理工大学 | Side micro-aerobic microbial fuel cell constructed wetland water purification method |
CN105600951A (en) * | 2016-03-28 | 2016-05-25 | 郑州大学 | Method for constructing wet land park type ecological water purification system |
CN107540094A (en) * | 2017-10-26 | 2018-01-05 | 广西师范大学 | Artificial marsh sewage treatment system |
CN107963715A (en) * | 2017-11-06 | 2018-04-27 | 天津大学 | A kind of streamside ecology diafiltration for being filled with oxygen-release material cuts dirty pond |
US20200392027A1 (en) * | 2017-12-13 | 2020-12-17 | Chinese Research Academy Of Environmental Sciences | Method and device for controlling pollutants in basin water used for irrigating farmland in extremely water-scarce areas |
CN112479482A (en) * | 2020-11-02 | 2021-03-12 | 广州鑫泓设备设计有限公司 | Ammonia nitrogen wastewater treatment system based on constructed wetland |
-
2021
- 2021-04-26 CN CN202110451444.7A patent/CN112897824A/en active Pending
Patent Citations (14)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101851023A (en) * | 2010-03-26 | 2010-10-06 | 北京神州瑞霖环保科技有限公司 | Underflow type constructed wetland system with coke powder-steel slag compound filler |
CN101921044A (en) * | 2010-08-11 | 2010-12-22 | 环境保护部南京环境科学研究所 | Two-stage anaerobic-tower type filter chamber livestock/poultry wastewater treatment system and treatment process |
CN102263279A (en) * | 2011-07-06 | 2011-11-30 | 武汉理工大学 | Microbial fuel cell device with artificial wetland aquatic plant electrodes |
CN102583770A (en) * | 2012-01-16 | 2012-07-18 | 湖南农业大学 | Bamboo charcoal-photosynthetic bacteria integrated municipal sanitary wastewater treating agent |
CN102583886A (en) * | 2012-02-21 | 2012-07-18 | 海南农丰宝肥料有限公司 | Artificial wetland for treating sewage |
CN102690021A (en) * | 2012-05-24 | 2012-09-26 | 金丹越 | Dispersive domestic sewage advanced pretreatment system |
CN102897968A (en) * | 2012-08-31 | 2013-01-30 | 中国矿业大学(北京) | Counter flow type vertical flow artificial wetland system |
CN103172226A (en) * | 2013-04-15 | 2013-06-26 | 东南大学 | Surface water stagnation type baffling wetland system for synchronously and intensively removing nitrogen, phosphorus and estrogen |
CN105502672A (en) * | 2016-01-13 | 2016-04-20 | 桂林理工大学 | Side micro-aerobic microbial fuel cell constructed wetland water purification method |
CN105600951A (en) * | 2016-03-28 | 2016-05-25 | 郑州大学 | Method for constructing wet land park type ecological water purification system |
CN107540094A (en) * | 2017-10-26 | 2018-01-05 | 广西师范大学 | Artificial marsh sewage treatment system |
CN107963715A (en) * | 2017-11-06 | 2018-04-27 | 天津大学 | A kind of streamside ecology diafiltration for being filled with oxygen-release material cuts dirty pond |
US20200392027A1 (en) * | 2017-12-13 | 2020-12-17 | Chinese Research Academy Of Environmental Sciences | Method and device for controlling pollutants in basin water used for irrigating farmland in extremely water-scarce areas |
CN112479482A (en) * | 2020-11-02 | 2021-03-12 | 广州鑫泓设备设计有限公司 | Ammonia nitrogen wastewater treatment system based on constructed wetland |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN100487105C (en) | High-effective microorganism complex agent and method of using the same for treating city sewage | |
CN103449680B (en) | Method for removing pollutants in sewage | |
CN101560486B (en) | Achromobacter xylosoxidans strain for biological denitrificaion and application thereof | |
CN108178341B (en) | Solid microbial purification particle and preparation method thereof | |
CN110683657A (en) | Culture sewage treatment method based on microbial degradation | |
Rong et al. | Towards advanced mariculture wastewater treatment by bacterial-algal symbiosis system with different bacteria and algae inoculation ratios | |
CN103086508A (en) | Microbial fuel cell wastewater treatment system for improving nitrogen removal effect | |
CN102583770A (en) | Bamboo charcoal-photosynthetic bacteria integrated municipal sanitary wastewater treating agent | |
CN103319047A (en) | Landfill leachate treatment system | |
CN105036471A (en) | Method for removing sewage pollutants containing lead | |
CN107473404B (en) | Water purifying agent with self-formed block-shaped carbon carrier for fixing microorganisms and preparation method thereof | |
Yang et al. | A review of emerged constructed wetlands based on biochar filler: Wastewater purification and carbon sequestration/greenhouse gas reduction | |
CN103130335A (en) | Germ composite polluted water treatment agent | |
WO2020097994A1 (en) | Sphingobacterium having both heterotrophic nitrification and aerobic denitrification functions and application thereof | |
CN114506919A (en) | Efficient purification composite biological filler and preparation method thereof | |
CN113024024A (en) | Application of organic carbon source and nano manganese dioxide in improving capability of enhancing removal of ammonia nitrogen in water by biological activated carbon | |
CN103373761B (en) | Method for treating industrial circulating water | |
CN115259391B (en) | Multi-element fungus and algae composition for sewage treatment, complexing agent and application thereof | |
CN109678302B (en) | Ex-situ treatment system for eutrophic lake | |
CN115108629B (en) | Advanced sewage treatment method and system | |
CN112897824A (en) | Bamboo charcoal-photosynthetic bacteria-constructed wetland integration sewage treatment system | |
CN105130100A (en) | Method of removing pollutant from cadmium-containing sewage | |
CN108314179A (en) | Strengthen the method for activated sludge removal sewerage nitrogen and phosphor and toxic organic compound difficult to degrade | |
CN209740924U (en) | Ectopic treatment system for eutrophic lakes | |
CN109896703B (en) | Light-enzyme composite catalytic function microorganism water purifying agent for culturing anaerobic sewage |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
RJ01 | Rejection of invention patent application after publication | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20210604 |