CN107522286A - A kind of tail water processing method based on sulphur/oyster shell - Google Patents

A kind of tail water processing method based on sulphur/oyster shell Download PDF

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Publication number
CN107522286A
CN107522286A CN201710962682.8A CN201710962682A CN107522286A CN 107522286 A CN107522286 A CN 107522286A CN 201710962682 A CN201710962682 A CN 201710962682A CN 107522286 A CN107522286 A CN 107522286A
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CN
China
Prior art keywords
oyster shell
tail water
sulphur
discarded
processing method
Prior art date
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Pending
Application number
CN201710962682.8A
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Chinese (zh)
Inventor
贺航运
崔文亮
钱东
吴芳磊
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Zhejiang Deep German Environmental Technology Co Ltd
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Zhejiang Deep German Environmental Technology Co Ltd
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Priority to CN201710962682.8A priority Critical patent/CN107522286A/en
Publication of CN107522286A publication Critical patent/CN107522286A/en
Pending legal-status Critical Current

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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/28Anaerobic digestion processes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/105Phosphorus compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia

Abstract

A kind of tail water processing method based on sulphur/oyster shell, the substitute that discarded oyster shell is used as to lime stone is used in tail water handling process, and in reactor, the mass ratio of sulfur granules and oyster shell is 1:0.7~1:0.8, and the particle diameter of sulfur granules is 1 mm ~ 8mm;It is 1mm ~ 5mm that the discarded oyster shell is crushed to particle diameter by reducing mechanism.Discarded oyster shell serves not only as the habitat of microorganism, and containing abundant calcium carbonate, the Thiobacillus for sulphur autotrophic type provides carbon source;Separately containing a variety of inorganic microelements such as sodium, barium, copper, iron, magnesium, manganese, nickel, strontiums, nutrition is provided for microbe survival;The physique of oyster shell is cuticula, prismatic layer, nacre composition, and major part is prismatic layer, bladed structure, containing a large amount of 2 ~ 10um micropores, with stronger adsorption capacity, while also adhere to organic carbon source on oyster shell, therefore the function of autotrophy/heterotrophism collaboration denitrogenation can be realized.Technique in the present invention can turn waste into wealth, and carry out deep phosphorous removal denitrogenation to tail water, cost is low.

Description

A kind of tail water processing method based on sulphur/oyster shell
Technical field
The invention belongs to sewage treatment area, and in particular to a kind of tail water processing method based on sulphur/oyster shell.
Background technology
As the fast development of China's economy and the nutrient such as quickening, a large amount of nitrogen phosphorus of urbanization process enter water body In, cause the eutrophication of water body, in order to further control water pollution, input of the China in sewage disposal is also increasingly Greatly.
Meanwhile in order to improve the quality of water environment of receiving water body, tail water in sewage treatment plant urgently advanced treating, especially The advanced treating to wherein nitrogen and phosphorus, current processing method be mainly based upon denitrification deep-bed filter carrying out, it is necessary to Carbon source is added, increases cost;Compared to heterotrophism denitrogenation, denitrogenation is with the obvious advantage due to that need not add carbon source.Sulphur autotrophic denitrification is Refer to the Thiobacillus of some obligate inorganic chemosynthetic autotrophs, thiosulfate is utilized in the environment of anaerobic or anoxic(S2O3 2-)、 Elemental sulfur(S), sulfide(S2-)It is electron acceptor by nitrate nitrogen using nitrate Deng for electron donor(NO3-)It is reduced to nitrogen(N2) Sulphur is oxidized to the autotrophic denitrification process of sulfate simultaneously.The combination for studying more mostly sulphur and lime stone at present is anti- Should.
Oyster is with its delicious flavour, nutritious and be loved by consumers in shellfish by nest RT-PCR, but after consuming A large amount of oyster shells abandon as rubbish, have not only polluted environment but also have caused the waste of resource.Oyster shell mineral matter is based on calcium constituent, calcium Content is 40%, if can be substituted lime stone and be studied for tail water processing, the present invention on this direction.
The content of the invention
The deficiency of the prior art for more than, the invention provides a kind of tail water processing side based on sulphur/oyster shell Method, cost is low, turns waste into wealth, denitrogenation dephosphorization significant effect.
In order to solve the above-mentioned technical problem, the present invention is addressed by following technical proposals.
A kind of tail water processing method based on sulphur/oyster shell, the substitute that discarded oyster shell is used as to lime stone are used In tail water handling process, in reactor, the mass ratio of sulfur granules and oyster shell is 1:0.7~1:0.8, and the particle diameter of sulfur granules For 1 mm ~ 8mm.
Preferably, it is 1mm ~ 5mm that the discarded oyster shell is crushed to particle diameter by reducing mechanism.
Discarded oyster shell serves not only as the habitat of microorganism, and containing abundant calcium carbonate, for the sulphur bar of sulphur autotrophic type Pseudomonas provides carbon source;Separately containing a variety of inorganic microelements such as sodium, barium, copper, iron, magnesium, manganese, nickel, strontiums, provided for microbe survival Nutrition;The physique of oyster shell is cuticula, prismatic layer, nacre composition, and major part is prismatic layer, bladed structure, Containing a large amount of 2 ~ 10um micropores, there is stronger adsorption capacity, while also adhere to organic carbon source on oyster shell, therefore can realize certainly The function of foster/heterotrophism collaboration denitrogenation.
Compared with prior art, the technique in the present invention can turn waste into wealth, using sulphur and discarded oyster shell as filler, Deep phosphorous removal denitrogenation is carried out to tail water, cost is low.
Brief description of the drawings
Fig. 1 is total nitrogen removal effect figure.
Fig. 2 is total phosphorus removal effect figure.
Embodiment
The present invention is described in further detail with embodiment below in conjunction with the accompanying drawings.
In the present invention, a kind of tail water processing method based on sulphur/oyster shell, feature is filtered in existing denitrification depth bed In the tail water handling process in pond, the substitute that discarded oyster shell is used as to lime stone is used in tail water handling process, reactor In, the mass ratio of sulfur granules and oyster shell is 1:0.7~1:0.8, and the particle diameter of sulfur granules is 1 mm ~ 8mm.It is described discarded male It is 1mm ~ 5mm that oyster shell is crushed to particle diameter by reducing mechanism.
In method in the present invention, other processing steps being not directed to and parameter are all handling process ginseng conventional in industry Number.
In the present invention, using discarded oyster shell as inorganic carbon source, based on calcium constituent, calcium content is oyster shell mineral matter 40% or so, separately there are a variety of inorganic elements such as sodium, barium, copper, iron, magnesium, manganese, nickel, strontium.The physique of oyster shell be cuticula, Prismatic layer, nacre composition, major part is prismatic layer, bladed structure, containing a large amount of 2 ~ 10um micropores, has stronger absorption Ability, utilized using oyster shell as the carbon source of sulphur autotrophic denitrification, ring caused by due to abandoning oyster shell can not only be mitigated Border is polluted, but also can be turned waste into wealth for sewage disposal.
Meanwhile a small amount of organic matter is adsorbed with discarded oyster shell, therefore autotrophy/heterotrophism collaboration denitrogenation can be realized Function, further enhance denitrification effect.
See that Fig. 1, Fig. 1 show the removal effect of the total nitrogen after system run all right, total nitrogen average removal rate reaches 93%, And processing system of the lime stone as inorganic carbon source is used, 80% or so, contrast effect significantly carries its total nitrogen average removal rate Rise;See that Fig. 2, Fig. 2 show the removal effect of stable rear total phosphorus, total phosphorus average removal rate reaches 33%, and uses lime stone As the processing system of inorganic carbon source, 26% or so, contrast effect is obviously improved its total phosphorus average removal rate.
As can be seen here, in the present invention, the lime stone used in tradition is substituted using discarded oyster shell as tail water processing Method, not only turn waste into wealth, saved cost, and significantly improve nitrogen removal rate and total tp removal rate, effect shows Write, economic value is high.
Protection scope of the present invention includes but is not limited to embodiment of above, and protection scope of the present invention is with claims It is defined, any replacement being readily apparent that to those skilled in the art that this technology is made, deformation, improvement each fall within the present invention's Protection domain.

Claims (2)

1. a kind of tail water processing method based on sulphur/oyster shell, it is characterised in that discarded oyster shell is used as lime stone Substitute is used in tail water handling process, and in reactor, the mass ratio of sulfur granules and oyster shell is 1:0.7~1:0.8, and sulphur The particle diameter of grain is 1 mm ~ 8mm.
2. a kind of tail water processing method based on sulphur/oyster shell according to claim 1, it is characterised in that described useless It is 1mm ~ 5mm that the oyster shell abandoned is crushed to particle diameter by reducing mechanism.
CN201710962682.8A 2017-10-17 2017-10-17 A kind of tail water processing method based on sulphur/oyster shell Pending CN107522286A (en)

Priority Applications (1)

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CN201710962682.8A CN107522286A (en) 2017-10-17 2017-10-17 A kind of tail water processing method based on sulphur/oyster shell

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Application Number Priority Date Filing Date Title
CN201710962682.8A CN107522286A (en) 2017-10-17 2017-10-17 A kind of tail water processing method based on sulphur/oyster shell

Publications (1)

Publication Number Publication Date
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Cited By (6)

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Publication number Priority date Publication date Assignee Title
CN112340846A (en) * 2020-11-19 2021-02-09 海天水务集团股份公司 Deep denitrification method for municipal sewage
CN112340845A (en) * 2020-11-19 2021-02-09 海天水务集团股份公司 Advanced nitrogen and phosphorus removal process for town sewage
CN114195259A (en) * 2021-12-06 2022-03-18 清华大学 Low-carbon nitrate wastewater efficient purification device system based on mixed matrix and purification treatment method
CN114605726A (en) * 2022-03-15 2022-06-10 四川达沃斯生态环保科技股份有限公司 Modified biological suspended filler and preparation method thereof
CN114804523A (en) * 2022-04-25 2022-07-29 华南理工大学 Device and method for culturing thiobacillus dephosphorization and phosphorus resource recovery based on composite filler
CN115636507A (en) * 2022-11-23 2023-01-24 山东建筑大学 Constructed wetland slow-release filler based on sulfur autotrophic denitrification

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CN101555070A (en) * 2008-04-11 2009-10-14 (株)日新综合环境 Porous sulfur complex media
CN101696057A (en) * 2009-10-23 2010-04-21 厦门大学 Sewage dephosphorization device of shuck filling biofilter
CN105923757A (en) * 2016-05-11 2016-09-07 深圳市瑞清环保科技有限公司 Method for phosphorus removal and denitrification through iron elementary substance cooperating with sulfur autotrophic denitrification

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US20070262019A1 (en) * 2005-12-23 2007-11-15 Sukalyan Sengupta Process for autotrophic denitrification using elemental sulfur and mollusk shells
US20070267346A1 (en) * 2005-12-23 2007-11-22 Sukalyan Sengupta Process for autotrophic perchlorate reduction using elemental sulfur and mollusk shells
CN101555070A (en) * 2008-04-11 2009-10-14 (株)日新综合环境 Porous sulfur complex media
CN101696057A (en) * 2009-10-23 2010-04-21 厦门大学 Sewage dephosphorization device of shuck filling biofilter
CN105923757A (en) * 2016-05-11 2016-09-07 深圳市瑞清环保科技有限公司 Method for phosphorus removal and denitrification through iron elementary substance cooperating with sulfur autotrophic denitrification

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Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112340846A (en) * 2020-11-19 2021-02-09 海天水务集团股份公司 Deep denitrification method for municipal sewage
CN112340845A (en) * 2020-11-19 2021-02-09 海天水务集团股份公司 Advanced nitrogen and phosphorus removal process for town sewage
CN112340846B (en) * 2020-11-19 2023-06-13 海天水务集团股份公司 Deep denitrification method for urban sewage
CN112340845B (en) * 2020-11-19 2023-06-13 海天水务集团股份公司 Advanced denitrification and dephosphorization process for town sewage
CN114195259A (en) * 2021-12-06 2022-03-18 清华大学 Low-carbon nitrate wastewater efficient purification device system based on mixed matrix and purification treatment method
CN114605726A (en) * 2022-03-15 2022-06-10 四川达沃斯生态环保科技股份有限公司 Modified biological suspended filler and preparation method thereof
CN114804523A (en) * 2022-04-25 2022-07-29 华南理工大学 Device and method for culturing thiobacillus dephosphorization and phosphorus resource recovery based on composite filler
CN115636507A (en) * 2022-11-23 2023-01-24 山东建筑大学 Constructed wetland slow-release filler based on sulfur autotrophic denitrification
CN115636507B (en) * 2022-11-23 2023-08-11 山东建筑大学 Constructed wetland slow release filler based on sulfur autotrophic denitrification

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Application publication date: 20171229