CN204824447U - Secondary treatment device that ferro -manganese exceeds standard in groundwater - Google Patents
Secondary treatment device that ferro -manganese exceeds standard in groundwater Download PDFInfo
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- CN204824447U CN204824447U CN201520505038.4U CN201520505038U CN204824447U CN 204824447 U CN204824447 U CN 204824447U CN 201520505038 U CN201520505038 U CN 201520505038U CN 204824447 U CN204824447 U CN 204824447U
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- filter vat
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Abstract
The utility model relates to a secondary treatment device that ferro -manganese exceeds standard in groundwater, including shower nozzle aerator, expose to the sun oxygen pond, filter -tank and sedimentation tank, the shower nozzle aerator is located the oxygen pond of exposing to the sun directly over, and the filter -tank includes first filter -tank and second filter -tank, has laid in proper order in the first filter -tank and has kept off sand net, bearing gravel and quartz sand, has laid in proper order in the second filter -tank and has kept off that sand is netted, bearing gravel and manganese sand, the raw water sprays the oxygen pond of exposing to the sun through the shower nozzle aerator, carries out catalytic oxidation with abundant aeration, filters, adsorbs through first filter -tank and second filter -tank in proper order again, flows in the sedimentation tank at last and deposits the back and supply the life use, in addition, open the sedimentation tank bottom has the mudhole, installs the outlet pipe on the lateral wall. Simple structure, material cost is cheap, maneuverability is strong, the maintenance is convenient, purifying effect is showing, can ensure the urban residents domestic water's that vast dispersion lived in safety, also the effectual red beds area puzzlement groundwater ferromanganese problem of exceeding standard for many years of having solved.
Description
Technical field
The utility model relates to Water warfare field, the second-stage treatment device that particularly in a kind of underground water, ferrimanganic exceeds standard.
Background technology
In recent years, government has carried out a large amount of " red beds well-digging " people's livelihood engineerings in water-deficient area, vast western countryside, many lack of water peasant households are made to have had motor-pumped well, and submersible pump has been installed, use " tap water ", but there is content of iron and manganese in a big chunk red beds underground water higher, considerably beyond safe standard for drinking.
Make a general survey of technical field of water purification, for solving underground water ferrimanganic excessive problem, multiple efficient water technology and device are developed at home at present, but in groundwater treatment engineering, often need to use biological uniform filtration device or add deferrization and demanganization bacterium liquid etc., all there is use cost higher, the problems such as complicated operation and water treatment effect instability; And the Poor Farmers Household being mostly to disperse lived in vast Based on Red Bed, buy complete water processing establishment expensive, both uneconomical also unrealistic, therefore, in daily life when using underground water, namely people often only by using after simple precipitation, filtration, and in water, iron, manganese element and other foreign matter contents are higher, long-term drinking health risk.
Utility model content
The utility model aims to provide a kind of with low cost, workable, easy to maintenance, and the second-stage treatment device that the significant underground water ferrimanganic of decontamination effect improving exceeds standard.
For this reason, the technical scheme that the utility model adopts is: the second-stage treatment device that in a kind of underground water, ferrimanganic exceeds standard, comprise shower nozzle aerator, expose to the sun oxygen pond, filter vat and settling tank, described shower nozzle aerator is positioned at directly over oxygen pond of exposing to the sun, described filter vat comprises the first filter vat and the second filter vat, be equipped with sand grid, support gravel and quartz sand in described first filter vat successively, in the second filter vat, be equipped with sand grid, support gravel and manganese sand successively; Former water sprays through shower nozzle aerator oxygen pond of exposing to the sun, and carries out catalytic oxidation with abundant aeration, then carries out filtering, adsorbing through the first filter vat and the second filter vat successively, finally flows into settling tank and carries out precipitating rear for living; Have mudhole bottom described settling tank, the sidewall of settling tank is provided with rising pipe.
Further, described oxygen pond of exposing to the sun is arranged at left side, first filter vat, the second filter vat and settling tank are arranged at right side and interval setting successively from top to bottom, in addition, exposing to the sun the bottom in oxygen pond must not lower than the top of the first filter vat, and oxygen pond of exposing to the sun, the first filter vat, the second filter vat, settling tank are successively by pipeline connection, this arranges compact construction, rationally, can be farthest cost-saving.
Further, the cone apex angle of described shower nozzle aerator 60 °, basal diameter 0.1m, eye diameter 4mm, percentage of open area 15%, eyelet flow velocity is 2.5m/s, mounting height distance is exposed to the sun oxygen pond top 0.6m, the parameters combination of this shower nozzle aerator can make that former water is more large-area to be contacted with oxygen, and the aeration better effects if played, promotes subsequent filter and absorption.
On the basis of such scheme, the laying depth of described quartz sand, manganese sand and support gravel is 0.2m, and the grain size of gravel of support gravel is 8 ~ 16mm, described quartz sand, manganese sand and gravel laying order are first path grain, rear particle size grain, the filtering layer be laid to thus can better filter and adsorption effect, and manganese, ferro element and other impurity in the former water of the more effective reduction of energy, provide the domestic water of more high-quality.
The beneficial effects of the utility model are: structure is simple, lower cost for material, workable, safeguard convenient, decontamination effect improving is remarkable, and in use, do not need to add biological or chemical degerming agent, the secondary pollution of water quality is avoided while reducing costs, guarantee the safety of urban residents' domestic water of vast scattered settlement, also effectively solve Based on Red Bed puzzlement underground water ferromanganese excessive problem for many years.
Accompanying drawing explanation
Fig. 1 is the utility model structural representation.
Embodiment
Below by embodiment also by reference to the accompanying drawings, the utility model is described in further detail:
As shown in Figure 1, the second-stage treatment device that in a kind of underground water, ferrimanganic exceeds standard, primarily of shower nozzle aerator 1, to expose to the sun oxygen pond 2, filter vat and settling tank 5 form, shower nozzle aerator 1 is positioned at directly over oxygen pond 2 of exposing to the sun, filter vat comprises the first filter vat 3 and the second filter vat 4, expose to the sun oxygen pond 2 be arranged at left side, first filter vat 3, second filter vat 4 and settling tank 5 are arranged at right side and interval setting successively from top to bottom, in addition, exposing to the sun the bottom in oxygen pond 2 must not lower than the top of the first filter vat 3, and oxygen pond 2 of exposing to the sun, first filter vat 3, second filter vat 4, settling tank 5 passes through pipeline connection successively.
Be equipped with sand grid, support gravel and quartz sand in first filter vat 3 successively, in the second filter vat 4, be equipped with sand grid, support gravel and manganese sand successively; Former water sprays through shower nozzle aerator 1 oxygen pond 2 of exposing to the sun, and carries out catalytic oxidation with abundant aeration, then carries out filtering, adsorbing through the first filter vat 3 and the second filter vat 4 successively, finally flows into settling tank 5 and carries out precipitating rear for living; Settling tank 5 has mudhole 6, and sidewall is provided with water tap with two outlet 7.
Better, the first filter vat 3 and the second filter vat 4 are square filter pocket.
Better, the material selection stainless steel of sand grid.
The some processes technical parameter of the present embodiment is below provided to be:
1. shower nozzle aerator: for single head designs, is welded into by purple steel and brass, can lose by anti-saw, cone apex angle 60 °, basal diameter 0.1m, eye diameter 4mm, percentage of open area 15%, eyelet flow velocity is 2.5m/s, mounting height distance is exposed to the sun oxygen pond top 0.6m, and thus, spray area can reach 1m
2.
2. to expose to the sun oxygen pond: be about 1.2m, the cement pit (all refer to interior dimensions, do not comprise wall size) of wide about 0.7m, high 0.7m.
3. filter vat: be respectively the first filter vat and the second filter vat, each groove width is 0.2m, dark 0.3m, overall length 2.2m (each right angle length of side 1.1m, all refers to interior dimensions).
4. settling tank: be about 1.1m, wide about 0.9m, the cement pit (all referring to interior dimensions) of high about 0.6m.
5. sand grid: about 2m
2, be placed in filter vat for filling out paving filtrate.
6. quartz sand or manganese sand: particle diameter is respectively 0.6 ~ 1.2mm and 1.2 ~ 2mm, tap density is 1800kg/m3.Ulking thickness is 0.2m, and length is 1m.
7. support gravel: be filled on the right side of trough with straight angle, the long 0.1m of stack size, wide 0.2m, high 0.2m, single grain size of gravel be 8 ~ 16mm not etc.
8. back flushing frequency: carry out back flushing, backwash rate: 16 ~ 20L/sm every 10 days filtrates to filter vat
2, flush time: 5 ~ 15 minutes (from economic use angle, backwashing manner can be artificial flushing).
Claims (4)
1. the second-stage treatment device that in a underground water, ferrimanganic exceeds standard, comprise shower nozzle aerator (1), oxygen pond (2) of exposing to the sun, filter vat and settling tank (5), described shower nozzle aerator (1) is positioned at directly over oxygen pond (2) of exposing to the sun, it is characterized in that: described filter vat comprises the first filter vat (3) and the second filter vat (4), be equipped with sand grid, support gravel and quartz sand successively in described first filter vat (3), in the second filter vat (4), be equipped with sand grid, support gravel and manganese sand successively; Former water sprays to oxygen pond (2) of exposing to the sun through shower nozzle aerator (1), carry out catalytic oxidation with abundant aeration, carry out filtering, adsorbing through the first filter vat (3) and the second filter vat (4) successively again, finally flow into settling tank (5) and carry out precipitating rear for life; Described settling tank (5) bottom has mudhole (6), the sidewall of settling tank (5) is provided with rising pipe (7).
2. the second-stage treatment device that in underground water according to claim 1, ferrimanganic exceeds standard, it is characterized in that: described in expose to the sun oxygen pond (2) be arranged at left side, first filter vat (3), the second filter vat (4) and settling tank (5) are arranged at right side and interval setting successively from top to bottom, in addition, exposing to the sun the bottom in oxygen pond (2) must not lower than the top of the first filter vat (3), and oxygen pond (2) of exposing to the sun, the first filter vat (3), the second filter vat (4), settling tank (5) pass through pipeline connection successively.
3. the second-stage treatment device that in underground water according to claim 1 and 2, ferrimanganic exceeds standard, it is characterized in that: the cone apex angle 60 ° of described shower nozzle aerator (1), basal diameter 0.1m, eye diameter 4mm, percentage of open area 15%, eyelet flow velocity is 2.5m/s, and mounting height distance is exposed to the sun oxygen pond (2) top 0.6m.
4. the second-stage treatment device that in underground water according to claim 1 and 2, ferrimanganic exceeds standard, it is characterized in that: the laying depth of described quartz sand, manganese sand and support gravel is 0.2m, and the grain size of gravel of support gravel is 8 ~ 16mm, described quartz sand, manganese sand and gravel laying order are first path grain, rear particle size grain.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
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CN201520505038.4U CN204824447U (en) | 2015-07-10 | 2015-07-10 | Secondary treatment device that ferro -manganese exceeds standard in groundwater |
Applications Claiming Priority (1)
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CN201520505038.4U CN204824447U (en) | 2015-07-10 | 2015-07-10 | Secondary treatment device that ferro -manganese exceeds standard in groundwater |
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN107416964A (en) * | 2017-06-13 | 2017-12-01 | 重庆市铜梁区宝山源矿泉水厂 | Underground water well and groundwater treatment system |
CN115594318A (en) * | 2022-12-13 | 2023-01-13 | 毅康科技有限公司(Cn) | Underground water aeration tower device for sewage treatment |
-
2015
- 2015-07-10 CN CN201520505038.4U patent/CN204824447U/en active Active
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN107416964A (en) * | 2017-06-13 | 2017-12-01 | 重庆市铜梁区宝山源矿泉水厂 | Underground water well and groundwater treatment system |
CN107416964B (en) * | 2017-06-13 | 2021-02-02 | 重庆市铜梁区宝山源矿泉水厂 | Groundwater well and groundwater treatment system |
CN115594318A (en) * | 2022-12-13 | 2023-01-13 | 毅康科技有限公司(Cn) | Underground water aeration tower device for sewage treatment |
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Legal Events
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C14 | Grant of patent or utility model | ||
GR01 | Patent grant | ||
CP03 | Change of name, title or address |
Address after: 400799 No. 10 Labor Village, Beibei District, Chongqing Patentee after: Chongqing Municipal Bureau of Geology and mineral resources exploration and development 208 hydrogeology and Engineering Geology Team (Chongqing geological disaster prevention engineering survey and Design Institute) Address before: 400 700 No. 10 Natural Labor Village, Beibei District, Chongqing Patentee before: Chongqing hydrogeology and engineering geological team, bureau of Geology and mineral resources exploration and development, 208 |
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CP03 | Change of name, title or address |