CN107512777A - Sewage-treating agent - Google Patents
Sewage-treating agent Download PDFInfo
- Publication number
- CN107512777A CN107512777A CN201710758768.9A CN201710758768A CN107512777A CN 107512777 A CN107512777 A CN 107512777A CN 201710758768 A CN201710758768 A CN 201710758768A CN 107512777 A CN107512777 A CN 107512777A
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- CN
- China
- Prior art keywords
- parts
- weight
- sewage
- treating agent
- bacterium solution
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
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Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
-
- C—CHEMISTRY; METALLURGY
- 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
- C02F1/288—Treatment of water, waste water, or sewage by sorption using composite sorbents, e.g. coated, impregnated, multi-layered
-
- 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
- C02F3/342—Biological treatment of water, waste water, or sewage characterised by the microorganisms used characterised by the enzymes used
-
- 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
- C02F3/347—Use of yeasts or fungi
Abstract
The invention discloses a kind of sewage-treating agent, including the parts by weight of biological bacterium solution 50, the parts by weight of starch 90~130, the parts by weight of polymeric aluminum sulfate silicate 15~50, the parts by weight of bodied ferric sulfate 5~13, the parts by weight of activated sludge 60~100, the parts by weight of plant ash 20~60, the parts by weight of sodium acetate 18~36, the parts by weight of polyacrylamide 25~32, the parts by weight of ulexite 20~28, the parts by weight of sodium bentonite 20~30, the parts by weight of zeolite powder 15~33, the parts by weight of cocoanut active charcoal 16~41,3~19 parts of diatomite.The sewage-treating agent of the present invention includes chemical treatments and biological treatment agent, two-way interaction, cooperates so that the effect of sewage disposal greatly improves.
Description
Technical field
The present invention relates to technical field of sewage, and in particular to sewage-treating agent.
Background technology
With industrial expansion, the size of population increases, and the water consumption of production and living is also being on the increase, and is corresponded
, the discharge capacity of sewage is also improving constantly.Sewage mainly has sanitary sewage, industrial wastewater and early-stage rainwater.Sewage it is main
The ill pathogen contaminant of pollutant, oxygen consumption pollutant, plant nutrient and toxic pollutant etc..
The waste water of the discharge such as sanitary sewage, its feeding field sewage and process hides, scouring of wool, butchery and hospital, often contains
Various pathogen, such as virus, germ, parasite.Water body can be spread disease by the pollution of pathogen, as snail fever, cholera,
Typhoid fever, dysentery, virus hepatitis etc..Popular pestilence in history, some is exactly water-borne type infectious disease.After by pathogen contamination
Water body, microorganism increase sharply, and many of which is pathogenic bacteria, disease pest ovum and virus, and they are often total to other bacteriums and Escherichia coli
Deposit, be the characteristics of pathogen contamination:Quantity is big;Distribution is wide;Time-to-live is longer;Reproduction speed is fast;The resistance to the action of a drug is also easy to produce, it is difficult to
Die out.After traditional secondary biochemical sewage disposal and chlorination, some pathogenic microorganisms, virus remain to large number of viable.It is common
Coagulation, precipitation, filter, disinfect can go water removal in more than 99% virus, as delivery turbidity be more than 0.5 degree when, still can companion
With penetrating for virus.Pathogen contamination thing can enter water body by number of ways, once condition is adapted to, will cause human body disease
Disease.
Nitrogen, phosphorus equalenergy stimulus algae and pasture and water growth, interference purification of water quality in sewage, make the elevated materials of BOD5.Water
" eutrophication " in body caused by nutriment excess has turned into for the harm caused by lake and the slow water body of flowing
The serious problems of water resource protection.
Eutrophication (eutrophication) refers under the influence of mankind's activity, the nutrition such as the required nitrogen of biology, phosphorus
Material largely enters the slow flow water bodies such as lake, river mouth, bay, causes algae and other planktonic organisms to breed rapidly, water body dissolving
Oxygen amount declines, water quality deterioration, the phenomenon of fish and other biological mortality.Under field conditions (factors), lake also can be from poor nutrition
Status transition is on the increase to eutrophic state, deposit, is first changed into marsh, after be changed into land.This natural process is very slow
Slowly, even years up to ten thousand in thousands of years are often needed.And the water body caused by industrial wastewater and sanitary sewage of the anthropogenic discharge containing nutriment
Eutrophication, can occur in a short time.
The source of plant nutrient substance is wide, quantity is big, there is sanitary sewage (organic matter, detergent), agriculture (chemical fertilizer, farmers'
Fertilizer), industrial wastewater, rubbish etc..Bring the nitrogen about 50g in sewage into for each person every day.Phosphorus in sanitary sewage is mainly derived from washing
Waste water, and the chemical fertilizer for applying farmland has in 50% ~ 80% inflow rivers, Hu Hai and body of groundwater.Phosphorus and nitrogen are (special in natural water body
Phosphorus) content be to a certain extent planktonic organism growth governing factor.When a large amount of nitrogen, phosphorus plant nutrient substance are discharged into water
After body, promoting some biological (such as algae), drastically flourish, growth cycle shorten.Quilt after algae and other planktonic organism death
Aerobic biodegradability, the dissolved oxygen in water is constantly consumed, or is decomposed by anaerobe, constantly produce the gases such as hydrogen sulfide,
Make water quality deterioration, cause the mortality of fish and other aquatiles.Algae and other planktonic organism residuums are in putrefaction process
In, and the nutriments such as the required nitrogen of biology, phosphorus are discharged into water, for biological utilisations such as new generation algae.Therefore, water body
After eutrophication, even if the source of cut-out external nourishment material, it is also difficult to self-cleaning and return to normal level.Water body eutrophication is tight
During weight, lake can be silted up by some numerous plants and its remains, turn into marsh or even dry ground.Local sea area becomes " Dead Sea ",
Or there is " red tide " phenomenon.
The content of the invention
It is an object of the invention to provide a kind of sewage-treating agent, solves sewage quantity and gradually increases, existing sewage-treating agent
The problem of wastewater treatment efficiency is bad.
To solve above-mentioned technical problem, the present invention uses following technical scheme:
A kind of sewage-treating agent, including the parts by weight of biological bacterium solution 50, the parts by weight of starch 90~130, polymeric aluminum sulfate silicate 15~50
Parts by weight, the parts by weight of bodied ferric sulfate 5~13, the parts by weight of activated sludge 60~100, the parts by weight of plant ash 20~60, sodium acetate
18~36 parts by weight, the parts by weight of polyacrylamide 25~32, the parts by weight of ulexite 20~28, the weight of sodium bentonite 20~30
Part, the parts by weight of zeolite powder 15~33, the parts by weight of cocoanut active charcoal 16~41,3~19 parts of diatomite.
As preferable, including the parts by weight of biological bacterium solution 50, the parts by weight of starch 100~120, polymeric aluminum sulfate silicate 20~
40 parts by weight, the parts by weight of bodied ferric sulfate 7~10, the parts by weight of activated sludge 70~90, the parts by weight of plant ash 30~50, sodium acetate
24~30 parts by weight, the parts by weight of polyacrylamide 27~30, the parts by weight of ulexite 22~26, the weight of sodium bentonite 23~28
Part, the parts by weight of zeolite powder 20~30, the parts by weight of cocoanut active charcoal 20~30,8~15 parts of diatomite.
As preferable, the biological bacterium solution includes saccharomycete, rhodopseudomonas spheroid, cellulase and pectase.
As preferable, the number of saccharomycete and rhodopseudomonas spheroid ratio is 3-8 in the biological bacterium solution:1.
As preferable, the number of saccharomycete is more than 100,000,000 in every gram of biological bacterium solution.
As preferable, the concentration of the biological bacterium solution cellulase is 0.05~0.1g/ml, and the concentration of pectase is
0.03~0.7g/ml.
Compared with prior art, beneficial effects of the present invention are at least one of following:
The sewage-treating agent of the present invention includes chemical treatments and biological treatment agent, two-way interaction, cooperates so that
The effect of sewage disposal greatly improves.
Biological bacterium solution in the application includes saccharomycete, rhodopseudomonas spheroid, cellulase and pectase, can accelerate micro-
The speed of biological metabolism, promotes cell division, accelerates processing speed of the microorganism to water body, improves the efficiency of water process.
Take a variety of adsorbents to optimize combination, the nutritional ingredient more than needed in adsorbed water body, control nutritional ingredient
Release, it is more suitable for the growth and breeding of microorganism, so as to greatly improve the speed of sewage disposal.
Embodiment
In order to make the purpose , technical scheme and advantage of the present invention be clearer, with reference to embodiments, to the present invention
It is further elaborated.It should be appreciated that the specific embodiments described herein are merely illustrative of the present invention, it is not used to
Limit the present invention.
Embodiment 1:
Present embodiments provide a kind of sewage-treating agent, including the parts by weight of biological bacterium solution 50, the parts by weight of starch 90, polymeric aluminum sulfate silicate
It is 15 parts by weight, the parts by weight of bodied ferric sulfate 5, the parts by weight of activated sludge 60, the parts by weight of plant ash 20, the parts by weight of sodium acetate 18, poly-
It is the parts by weight of acrylamide 25, the parts by weight of ulexite 20, the parts by weight of sodium bentonite 20, the parts by weight of zeolite powder 15, coconut activated
3 parts of the parts by weight of charcoal 16, diatomite;The biological bacterium solution includes saccharomycete, rhodopseudomonas spheroid, cellulase and pectase,
Wherein, for the number of saccharomycete more than 100,000,000, the number ratio of saccharomycete and rhodopseudomonas spheroid is 3 in every gram of biological bacterium solution:
1, the concentration of cellulase is 0.05g/ml, and the concentration of pectase is 0.03g/ml.
Embodiment 2:
Present embodiments provide a kind of sewage-treating agent, including the parts by weight of biological bacterium solution 50, the parts by weight of starch 130, poly- silicon sulfuric acid
The parts by weight of aluminium 150, the parts by weight of bodied ferric sulfate 13, the parts by weight of activated sludge 100, the parts by weight of plant ash 60, the weight of sodium acetate 36
Measure part, the parts by weight of polyacrylamide 32, the parts by weight of ulexite 28, the parts by weight of sodium bentonite 30, the parts by weight of zeolite powder 33, coconut palm
19 parts of the parts by weight of shell activated carbon 41, diatomite;The biological bacterium solution include saccharomycete, rhodopseudomonas spheroid, cellulase and
Pectase, wherein, the number of saccharomycete is more than 100,000,000 in every gram of biological bacterium solution, of saccharomycete and rhodopseudomonas spheroid
Number is than being 8:1, the concentration of cellulase is 0.1g/ml, and the concentration of pectase is 0.7g/ml.
Embodiment 3:
Present embodiments provide a kind of sewage-treating agent, including the parts by weight of biological bacterium solution 50, the parts by weight of starch 100, poly- silicon sulfuric acid
The parts by weight of aluminium 20, the parts by weight of bodied ferric sulfate 7, the parts by weight of activated sludge 70, the parts by weight of plant ash 30, the weight of sodium acetate 24
Part, the parts by weight of polyacrylamide 27, the parts by weight of ulexite 22, the parts by weight of sodium bentonite 23, the parts by weight of zeolite powder 20, coconut husk
8 parts of the parts by weight of activated carbon 20, diatomite;The biological bacterium solution includes saccharomycete, rhodopseudomonas spheroid, cellulase and pectin
Enzyme, wherein, the number of saccharomycete is more than 100,000,000 in every gram of biological bacterium solution, the number ratio of saccharomycete and rhodopseudomonas spheroid
For 3:1, the concentration of cellulase is 0.1g/ml, and the concentration of pectase is 0.03g/ml.
Embodiment 4:
Present embodiments provide a kind of sewage-treating agent, including the parts by weight of biological bacterium solution 50, the parts by weight of starch 120, poly- silicon sulfuric acid
The parts by weight of aluminium 40, the parts by weight of bodied ferric sulfate 10, the parts by weight of activated sludge 90, the parts by weight of plant ash 50, the weight of sodium acetate 24~30
Measure part, the parts by weight of polyacrylamide 30, the parts by weight of ulexite 26, the parts by weight of sodium bentonite 28, the parts by weight of zeolite powder 30, coconut palm
15 parts of the parts by weight of shell activated carbon 30, diatomite;The biological bacterium solution include saccharomycete, rhodopseudomonas spheroid, cellulase and
Pectase, wherein, the number of saccharomycete is more than 100,000,000 in every gram of biological bacterium solution, of saccharomycete and rhodopseudomonas spheroid
Number is than being 8:1, the concentration of cellulase is 0.1g/ml, and the concentration of pectase is 0.1g/ml.
Embodiment 5:
Present embodiments provide a kind of sewage-treating agent, including the parts by weight of biological bacterium solution 50, the parts by weight of starch 110, poly- silicon sulfuric acid
The parts by weight of aluminium 30, the parts by weight of bodied ferric sulfate 8, the parts by weight of activated sludge 80, the parts by weight of plant ash 40, the weight of sodium acetate 27
Part, the parts by weight of polyacrylamide 28, the parts by weight of ulexite 24, the parts by weight of sodium bentonite 26, the parts by weight of zeolite powder 25, coconut husk
12 parts of the parts by weight of activated carbon 25, diatomite;The biological bacterium solution includes saccharomycete, rhodopseudomonas spheroid, cellulase and fruit
Glue enzyme, wherein, the number of saccharomycete is more than 100,000,000 in every gram of biological bacterium solution, the number of saccharomycete and rhodopseudomonas spheroid
Than for 5:1, the concentration of cellulase is 0.07g/ml, and the concentration of pectase is 0.4g/ml.
The effect of embodiment 5 in the embodiment of the present application is best, and the speech effect for sanitary sewage can reach ppm levels.
Although reference be made herein to invention has been described for multiple explanatory embodiments of the invention, however, it is to be understood that
Those skilled in the art can be designed that a lot of other modifications and embodiment, and these modifications and embodiment will fall in this Shen
Please be within disclosed spirit and spirit.More specifically, can be to master in the range of disclosure and claim
The building block and/or layout for inscribing composite configuration carry out a variety of variations and modifications.Except what is carried out to building block and/or layout
Outside modification and improvement, to those skilled in the art, other purposes also will be apparent.
Claims (6)
- A kind of 1. sewage-treating agent, it is characterised in that:Including the biological parts by weight of bacterium solution 50, the parts by weight of starch 90~130, poly- silicon sulphur The sour parts by weight of aluminium 15~50, the parts by weight of bodied ferric sulfate 5~13, the parts by weight of activated sludge 60~100, the weight of plant ash 20~60 Measure part, the parts by weight of sodium acetate 18~36, the parts by weight of polyacrylamide 25~32, the parts by weight of ulexite 20~28, Na-bentonite Native 20~30 parts by weight, the parts by weight of zeolite powder 15~33, the parts by weight of cocoanut active charcoal 16~41,3~19 parts of diatomite.
- 2. sewage-treating agent according to claim 1, it is characterised in that including the biological parts by weight of bacterium solution 50, starch 100~ 120 parts by weight, the parts by weight of polymeric aluminum sulfate silicate 20~40, the parts by weight of bodied ferric sulfate 7~10, the weight of activated sludge 70~90 Part, the parts by weight of plant ash 30~50, the parts by weight of sodium acetate 24~30, the parts by weight of polyacrylamide 27~30, ulexite 22~ 26 parts by weight, the parts by weight of sodium bentonite 23~28, the parts by weight of zeolite powder 20~30, the parts by weight of cocoanut active charcoal 20~30, silicon 8~15 parts of diatomaceous earth.
- 3. sewage-treating agent according to claim 1, it is characterised in that it is red that the biological bacterium solution includes saccharomycete, ball Pseudomonad, cellulase and pectase.
- 4. sewage-treating agent according to claim 3, it is characterised in that saccharomycete and ball are red false single in the biological bacterium solution The number ratio of born of the same parents bacterium is 3-8:1.
- 5. sewage-treating agent according to claim 3, it is characterised in that the number of saccharomycete in every gram of biological bacterium solution More than 100,000,000.
- 6. sewage-treating agent according to claim 3, it is characterised in that the concentration of the biological bacterium solution cellulase is 0.05~0.1g/ml, the concentration of pectase is 0.03~0.7g/ml.
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CN201710758768.9A CN107512777A (en) | 2017-08-29 | 2017-08-29 | Sewage-treating agent |
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CN201710758768.9A CN107512777A (en) | 2017-08-29 | 2017-08-29 | Sewage-treating agent |
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Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108178333A (en) * | 2018-01-10 | 2018-06-19 | 泰安市国泰民安生物科技有限公司 | A kind of biology cyanobacteria distintegrant |
CN108483529A (en) * | 2018-04-28 | 2018-09-04 | 上海应用技术大学 | A kind of formula and preparation method thereof of ecological environment construction sewage-treating agent |
CN109467145A (en) * | 2018-12-04 | 2019-03-15 | 湖南工程学院 | A kind of organic waste water treatment agent containing porous sepiolite |
CN110436644A (en) * | 2019-08-23 | 2019-11-12 | 河南亿群环保科技有限公司 | A kind of microorganism sewage water inorganic agent and preparation method thereof and sewage water treatment method |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103043803A (en) * | 2012-12-25 | 2013-04-17 | 东莞市水立芳水处理科技有限公司 | Water purifying agent and preparation method thereof |
CN104211162A (en) * | 2014-08-27 | 2014-12-17 | 镇江华域环保设备制造有限公司 | Sewage treating agent for treating heavy metal wastewater |
CN104445635A (en) * | 2014-10-31 | 2015-03-25 | 安徽华亿农牧科技发展有限公司 | Efficient biological water purifying agent as well as preparation method and use method thereof |
CN105967350A (en) * | 2016-07-07 | 2016-09-28 | 安徽国能亿盛环保科技有限公司 | Enzyme-containing sewage treating agent and preparation method thereof |
CN105967265A (en) * | 2016-07-07 | 2016-09-28 | 含山县科宇环境工程有限公司 | Sewage treating agent containing microbial strains and preparation method |
-
2017
- 2017-08-29 CN CN201710758768.9A patent/CN107512777A/en active Pending
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103043803A (en) * | 2012-12-25 | 2013-04-17 | 东莞市水立芳水处理科技有限公司 | Water purifying agent and preparation method thereof |
CN104211162A (en) * | 2014-08-27 | 2014-12-17 | 镇江华域环保设备制造有限公司 | Sewage treating agent for treating heavy metal wastewater |
CN104445635A (en) * | 2014-10-31 | 2015-03-25 | 安徽华亿农牧科技发展有限公司 | Efficient biological water purifying agent as well as preparation method and use method thereof |
CN105967350A (en) * | 2016-07-07 | 2016-09-28 | 安徽国能亿盛环保科技有限公司 | Enzyme-containing sewage treating agent and preparation method thereof |
CN105967265A (en) * | 2016-07-07 | 2016-09-28 | 含山县科宇环境工程有限公司 | Sewage treating agent containing microbial strains and preparation method |
Non-Patent Citations (1)
Title |
---|
和文祥等: "《环境微生物学》", 28 February 2007 * |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108178333A (en) * | 2018-01-10 | 2018-06-19 | 泰安市国泰民安生物科技有限公司 | A kind of biology cyanobacteria distintegrant |
CN108483529A (en) * | 2018-04-28 | 2018-09-04 | 上海应用技术大学 | A kind of formula and preparation method thereof of ecological environment construction sewage-treating agent |
CN109467145A (en) * | 2018-12-04 | 2019-03-15 | 湖南工程学院 | A kind of organic waste water treatment agent containing porous sepiolite |
CN110436644A (en) * | 2019-08-23 | 2019-11-12 | 河南亿群环保科技有限公司 | A kind of microorganism sewage water inorganic agent and preparation method thereof and sewage water treatment method |
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Application publication date: 20171226 |