CN109516642A - A kind of river sewage treatment process - Google Patents

A kind of river sewage treatment process Download PDF

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Publication number
CN109516642A
CN109516642A CN201811562016.6A CN201811562016A CN109516642A CN 109516642 A CN109516642 A CN 109516642A CN 201811562016 A CN201811562016 A CN 201811562016A CN 109516642 A CN109516642 A CN 109516642A
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CN
China
Prior art keywords
layer
tributary
main stem
treatment process
river
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
Application number
CN201811562016.6A
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Chinese (zh)
Inventor
许凤刚
沈科
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.)
Hangzhou Bo Tian Environmental Protection Technology Co Ltd
Original Assignee
Hangzhou Bo Tian 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
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Priority to CN201811562016.6A priority Critical patent/CN109516642A/en
Publication of CN109516642A publication Critical patent/CN109516642A/en
Pending legal-status Critical Current

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Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09CRECLAMATION OF CONTAMINATED SOIL
    • B09C1/00Reclamation of contaminated soil
    • B09C1/08Reclamation of contaminated soil chemically
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/283Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
    • 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
    • C02F2101/20Heavy metals or heavy metal compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/06Controlling or monitoring parameters in water treatment pH
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/04Disinfection
    • 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
    • C02F3/32Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
    • 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
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • C02F3/347Use of yeasts or fungi

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Soil Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Biological Treatment Of Waste Water (AREA)

Abstract

The invention discloses a kind of river sewage treatment process, comprising: filter layer is arranged at sewage draining exit and carries out primary filtration;Calcium lime powder and humus are launched at tributary in sewage draining exit, the mass ratio of calcium lime powder, humus and sewage is 1: 1: (1600~1700);Microorganism is launched later;Soil conditioner is added in the soil of bottom at tributary to sewage draining exit;Tributary is connect with main stem;In tributary and main stem junction, dykes and dams are set;Dykes and dams include: preceding barricade and rear barricade, and multistage filtering area is arranged between preceding barricade and rear barricade;Overflow port is provided on preceding shelves wall, multistage filtering area from top to bottom sets gradually water distributing plate, haydite floor, zeolite layer, coconut activated layer of charcoal and quartz sand layer;Aerating system is installed in main stem, is oxygenated into water body, bacteria group is launched;Ecological protection band is planted in tributary and main stem dykes and dams both sides, emergent aquactic plant, floating plant and submerged plant are launched in main stem.

Description

A kind of river sewage treatment process
Technical field
The present invention relates to technical field of sewage, more particularly to a kind of river sewage treatment process.
Background technique
Water is that human society depends on for existence and develops irreplaceable material base, is the lifeblood of economic development.Water resource Sustainable use is a most important problem in all natural resources sustainable uses, and shortage of water resources and water environment pollution are The principal element of world economy sustainable development is restricted through becoming.Since 20th century, with Social expanding economy, people " explosivity " of mouth increases, and the emergence of countries in the world water crisis, people are to water resource self-value and water resource pollution Caused various harm and loss have deep understanding.
The river of river, especially Chengzhong District, usual river basin area is smaller, and river body self-purification capacity is poor, and a large amount of residents are raw Sewage living and littoral food and drink waste water are directly discharged into, and feature is nitrogen and phosphorus content height, and water body self-purification ability is poor, and river surface landscape is poor.
Therefore, how the problem of processing is those skilled in the art's urgent need to resolve is carried out to the sewage in river.
Summary of the invention
In view of this, the entire water in river can not only be promoted the present invention provides a kind of river sewage treatment process The metabolism of body promotes self-purification capacity, and also without the external structure in excessive transformation river, construction cost is low, and the period is short, has Good application prospect.
To achieve the goals above, the present invention adopts the following technical scheme:
A kind of river sewage treatment process, comprising:
S1: filter layer is set at sewage draining exit and carries out primary filtration;
S2: calcium lime powder and humus, the matter of calcium lime powder, humus and sewage are launched at tributary in sewage draining exit Amount is than being 1: 1:(1600~1700);Microorganism is launched later;
S3: soil conditioner is added in the soil of bottom at tributary to sewage draining exit;The tributary and main river Road connection;
S4: dykes and dams are set in tributary and main stem junction;The dykes and dams include: preceding barricade and rear barricade, described Multistage filtering area is set between preceding barricade and rear barricade;Wherein, it is provided with overflow port on preceding shelves wall, multistage filtering area is from top to bottom Set gradually water distributing plate, haydite layer, zeolite layer, coconut activated layer of charcoal and quartz sand layer;
S5: installing aerating system in main stem, is oxygenated into water body, launches bacteria group;
S6: ecological protection band is planted in tributary and main stem dykes and dams both sides, emergent aquactic plant is launched in main stem, is floated Water plant and submerged plant.
Preferably, inspection cover is provided at the top of the preceding barricade and the rear barricade.
Preferably, the haydite layer, the zeolite layer, the thickness proportion of the coconut activated layer of charcoal and the quartz sand layer It is 3: 3: 4: 4.
Preferably, the microorganism includes: bacillus megaterium, denitrifying bacteria, lactic acid bacteria, brown rot fungus and anaerobism shuttle Bacterium.
Preferably, bacteria group includes: saccharomycete, nitrobacteria, denitrifying bacterium, photosynthetic bacteria and sulfide-oxidizing enzyme, ratio 6 ∶3∶4∶4∶3。
Preferably, the emergent aquactic plant includes: Scirpus tabernaemontani, cattail and/or canna;The floating plant include: water lily and/ Or floating heart;The submerged plant includes: the climing algae in river and/or comb tooth bog pondweed.
Preferably, humus is made of stalk, algae and animal waste.
Preferably, by holding between the haydite layer, the zeolite layer, the coconut activated layer of charcoal and the quartz sand layer Supporting plate separates.
It can be seen via above technical scheme that compared with prior art, the present disclosure provides at a kind of river sewage Science and engineering skill combines source and cuts the dual regulation of dirty processing, water quality and soil pH value, establishes dykes and dams, artificial oxygenation and launch benefit The many kinds of measures such as flora and water plant repair water quality, construct the river water body ecosystem, can not only promote in river The metabolism of entire water body, promotes self-purification capacity, and also without the external structure in excessive transformation river, construction cost is low, the period It is short, it has a good application prospect.
Detailed description of the invention
In order to more clearly explain the embodiment of the invention or the technical proposal in the existing technology, to embodiment or will show below There is attached drawing needed in technical description to be briefly described, it should be apparent that, the accompanying drawings in the following description is only this The embodiment of invention for those of ordinary skill in the art without creative efforts, can also basis The attached drawing of offer obtains other attached drawings.
Fig. 1 is a kind of flow chart of river sewage treatment process provided by the invention;
Fig. 2 is the structural schematic diagram of dykes and dams provided by the invention.
Specific embodiment
Following will be combined with the drawings in the embodiments of the present invention, and technical solution in the embodiment of the present invention carries out clear, complete Site preparation description, it is clear that described embodiments are only a part of the embodiments of the present invention, instead of all the embodiments.It is based on Embodiment in the present invention, it is obtained by those of ordinary skill in the art without making creative efforts every other Embodiment shall fall within the protection scope of the present invention.
Referring to attached drawing 1 and attached drawing 2, the embodiment of the present invention one discloses a kind of river sewage treatment process, comprising:
S1: filter layer is set at sewage draining exit and carries out primary filtration;Firstly, from being carried out in advance from source to the water of sewage draining exit Reason;
S2: calcium lime powder and humus, the matter of calcium lime powder, humus and sewage are launched at tributary in sewage draining exit Amount is than being 1: 1: 1600;Microorganism is launched later;
Secondly, improving the pH value of sewage by putting into calcium lime powder and humus into water, the acidity of sewage is neutralized, is gone out Germ is killed, it is heavy metal-passivated, play the role of filter and purification, and persistent, easy to implement, quick.Then, it utilizes Microorganism is adjusted again.
S3: soil conditioner is added in the soil of bottom at tributary to sewage draining exit;Wherein, tributary and main river Road connection;Later, consider also to improve the pH value of the soil of bottom, realize the dual improvement of water quality and soil.
S4: dykes and dams are constructed in tributary and main stem junction;Dykes and dams include: preceding barricade and rear barricade, preceding barricade and Multistage filtering area is set between barricade afterwards;Wherein, overflow port 6 is provided on preceding shelves wall, rear barricade bottom is provided with outflux 7, And it is provided with strainer at outflux 7, prevent quartz sand from spilling.Multistage filtering area from top to bottom sets gradually water distributing plate 1, haydite Layer 2, zeolite layer 3, coconut activated layer of charcoal 4 and quartz sand layer 5;
Here the junction of tributary and main stem is transformed, dykes and dams is added, to tributary and main stem Rest part does not make biggish change, and without changing the external structure in river, construction cost is low.And it uses from top to bottom Set gradually water distributing plate, haydite floor, zeolite layer, coconut activated layer of charcoal and quartz sand layer multistage filtering area, high treating effect.
S5: installing aerating system in main stem, is oxygenated into water body, launches bacteria group;Using artificial oxygenation and benefit The mode that flora combines.
S6: ecological protection band is planted in tributary and main stem dykes and dams both sides, emergent aquactic plant is launched in main stem, is floated Water plant and submerged plant.The self-purification capacity in river is promoted by emergent aquactic plant, floating plant and submerged plant, and more raw State.River two sides plant protection band, can near river environment and soil improve, prevent river two sides to water Body impacts.
River sewage processing method provided by the invention combines the Double regulating that dirty processing, water quality and soil pH value are cut in source The many kinds of measures such as bacteria group and water plant are saved, establish dykes and dams, artificial oxygenation and launched to repair water quality, building river water body is raw State system can not only promote the metabolism of the entire water body in river, promote self-purification capacity, also without excessive transformation river External structure, construction cost is low, and the period is short, has a good application prospect.
The invention also discloses embodiment two, embodiment two discloses a kind of river sewage treatment process, with embodiment one The difference is that the mass ratio of calcium lime powder, humus and sewage is 1: 1: 1700, same in conjunction with step S1-S6 in step S2 Sample is able to solve technical problem of the invention.
In order to further optimize the above technical scheme, multiple inspection covers are provided at the top of preceding barricade and rear barricade.
The situation in multistage filtering area can be checked for river management personnel by inspection cover.
In order to further optimize the above technical scheme, haydite layer, zeolite layer, coconut activated layer of charcoal and quartz sand layer thickness Ratio is 3: 3: 4: 4.
In order to further optimize the above technical scheme, microorganism include: bacillus megaterium, denitrifying bacteria, lactic acid bacteria, Brown rot fungus and anaerobism clostridium.
In order to further optimize the above technical scheme, bacteria group include: saccharomycete, it is nitrobacteria, denitrifying bacterium, photosynthetic thin Bacterium and sulfide-oxidizing enzyme, ratio 6: 3: 4: 4: 3.
These strains are all from nature, have stronger degradation capability, the mechanism of action is with photosynthetic bacteria group and saccharomycete Group be it is leading, cooperate with other beneficial microbe collective effects, generation antioxidant, decomposition oxidation of organic compounds, harmful poisonous It is converted into nontoxic.Meanwhile by this proportion, photosynthetic bacteria carries out photosynthesis, generates oxygen, using carbon dioxide, The substances such as nitrogen synthesize the substances such as carbohydrate, amino acid, utilize for other biological, promote the growth and breeding of other biological, in water body Establish a harmonious biological flora.
In order to further optimize the above technical scheme, emergent aquactic plant includes: Scirpus tabernaemontani, cattail and/or canna;Floating plant It include: water lily and/or floating heart;Submerged plant includes: the climing algae in river and/or comb tooth bog pondweed.
In order to further optimize the above technical scheme, humus is made of stalk, algae and animal waste.
The source of humus for people's lives in common substance, make full use of resource, more ecology.
In order to further optimize the above technical scheme, lead between haydite layer, zeolite layer, coconut activated layer of charcoal and quartz sand layer It crosses supporting plate to separate, prevents each layer loose.
Each embodiment in this specification is described in a progressive manner, the highlights of each of the examples are with other The difference of embodiment, the same or similar parts in each embodiment may refer to each other.For device disclosed in embodiment For, since it is corresponded to the methods disclosed in the examples, so being described relatively simple, related place is said referring to method part It is bright.
The foregoing description of the disclosed embodiments enables those skilled in the art to implement or use the present invention. Various modifications to these embodiments will be readily apparent to those skilled in the art, as defined herein General Principle can be realized in other embodiments without departing from the spirit or scope of the present invention.Therefore, of the invention It is not intended to be limited to the embodiments shown herein, and is to fit to and the principles and novel features disclosed herein phase one The widest scope of cause.

Claims (8)

1. a kind of river sewage treatment process characterized by comprising
S1: filter layer is set at sewage draining exit and carries out primary filtration;
S2: calcium lime powder and humus, the mass ratio of calcium lime powder, humus and sewage are launched at tributary in sewage draining exit It is 1: 1: (1600~1700);Microorganism is launched later;
S3: soil conditioner is added in the soil of bottom at tributary to sewage draining exit;The tributary and main stem connect It connects;
S4: dykes and dams are set in tributary and main stem junction;The dykes and dams include: preceding barricade and rear barricade, the front Multistage filtering area is set between wall and rear barricade;Wherein, it is provided with overflow port on preceding shelves wall, multistage filtering area is from top to bottom successively Water distributing plate, haydite layer, zeolite layer, coconut activated layer of charcoal and quartz sand layer are set;
S5: installing aerating system in main stem, is oxygenated into water body, launches bacteria group;
S6: ecological protection band is planted in tributary and main stem dykes and dams both sides, emergent aquactic plant is launched in main stem, swims to plant Object and submerged plant.
2. a kind of river sewage treatment process according to claim 1, which is characterized in that the preceding barricade and the rear gear Wall top portion is provided with inspection cover.
3. a kind of river sewage treatment process according to claim 1, which is characterized in that the haydite layer, the zeolite The thickness proportion of layer, the coconut activated layer of charcoal and the quartz sand layer is 3: 3: 4: 4.
4. a kind of river sewage treatment process according to claim 1, which is characterized in that the microorganism includes: huge Bacillus, denitrifying bacteria, lactic acid bacteria, brown rot fungus and anaerobism clostridium.
5. a kind of river sewage treatment process according to claim 1, which is characterized in that bacteria group includes: saccharomycete, nitre Change bacterium, denitrifying bacterium, photosynthetic bacteria and sulfide-oxidizing enzyme, ratio 6: 3: 4: 4: 3.
6. a kind of river sewage treatment process according to claim 1, which is characterized in that the emergent aquactic plant includes: water Green onion, cattail and/or canna;The floating plant includes: water lily and/or floating heart;The submerged plant include: the climing algae in river and/ Or comb tooth bog pondweed.
7. a kind of river sewage treatment process according to claim 1, which is characterized in that humus by stalk, algae and Animal waste is made.
8. a kind of river sewage treatment process according to claim 4, which is characterized in that the haydite layer, the zeolite It is separated between layer, the coconut activated layer of charcoal and the quartz sand layer by supporting plate.
CN201811562016.6A 2018-12-19 2018-12-19 A kind of river sewage treatment process Pending CN109516642A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201811562016.6A CN109516642A (en) 2018-12-19 2018-12-19 A kind of river sewage treatment process

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201811562016.6A CN109516642A (en) 2018-12-19 2018-12-19 A kind of river sewage treatment process

Publications (1)

Publication Number Publication Date
CN109516642A true CN109516642A (en) 2019-03-26

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Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105384305A (en) * 2015-11-20 2016-03-09 太仓市振锋化工设备有限公司 Domestic sewage treatment process
CN105906150A (en) * 2016-06-06 2016-08-31 李丹丹 Sewage treatment system and technology for river ways in city
CN205874019U (en) * 2016-06-29 2017-01-11 惠州市东江园林工程有限公司 Comprehensive repair system in cities and towns river course
CN207130109U (en) * 2017-08-22 2018-03-23 武汉水之国环保科技有限公司 A kind of Drain contamination for river channel mouth integrated treatment unit

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105384305A (en) * 2015-11-20 2016-03-09 太仓市振锋化工设备有限公司 Domestic sewage treatment process
CN105906150A (en) * 2016-06-06 2016-08-31 李丹丹 Sewage treatment system and technology for river ways in city
CN205874019U (en) * 2016-06-29 2017-01-11 惠州市东江园林工程有限公司 Comprehensive repair system in cities and towns river course
CN207130109U (en) * 2017-08-22 2018-03-23 武汉水之国环保科技有限公司 A kind of Drain contamination for river channel mouth integrated treatment unit

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Application publication date: 20190326