CN110216139A - A kind of water transfer heavy metals in farmland of improving the soil removes the construction method of system - Google Patents

A kind of water transfer heavy metals in farmland of improving the soil removes the construction method of system Download PDF

Info

Publication number
CN110216139A
CN110216139A CN201910437967.9A CN201910437967A CN110216139A CN 110216139 A CN110216139 A CN 110216139A CN 201910437967 A CN201910437967 A CN 201910437967A CN 110216139 A CN110216139 A CN 110216139A
Authority
CN
China
Prior art keywords
layer
water
double
soil
farmland
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
CN201910437967.9A
Other languages
Chinese (zh)
Inventor
余建新
张川
王东杰
李海丛
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.)
Guangzhou South China Institute Of Natural Resources Science And Technology
Yunnan Agricultural University
Original Assignee
Guangzhou South China Institute Of Natural Resources Science And Technology
Yunnan Agricultural University
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
Application filed by Guangzhou South China Institute Of Natural Resources Science And Technology, Yunnan Agricultural University filed Critical Guangzhou South China Institute Of Natural Resources Science And Technology
Priority to CN201910437967.9A priority Critical patent/CN110216139A/en
Publication of CN110216139A publication Critical patent/CN110216139A/en
Pending legal-status Critical Current

Links

Classifications

    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01BSOIL WORKING IN AGRICULTURE OR FORESTRY; PARTS, DETAILS, OR ACCESSORIES OF AGRICULTURAL MACHINES OR IMPLEMENTS, IN GENERAL
    • A01B79/00Methods for working soil
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09CRECLAMATION OF CONTAMINATED SOIL
    • B09C1/00Reclamation of contaminated soil
    • 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
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5236Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
    • EFIXED CONSTRUCTIONS
    • E02HYDRAULIC ENGINEERING; FOUNDATIONS; SOIL SHIFTING
    • E02BHYDRAULIC ENGINEERING
    • E02B11/00Drainage of soil, e.g. for agricultural purposes
    • EFIXED CONSTRUCTIONS
    • E03WATER SUPPLY; SEWERAGE
    • E03BINSTALLATIONS OR METHODS FOR OBTAINING, COLLECTING, OR DISTRIBUTING WATER
    • E03B11/00Arrangements or adaptations of tanks for water supply
    • E03B11/10Arrangements or adaptations of tanks for water supply for public or like main water supply
    • 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
    • C02F2001/007Processes including a sedimentation step
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P60/00Technologies relating to agriculture, livestock or agroalimentary industries
    • Y02P60/20Reduction of greenhouse gas [GHG] emissions in agriculture, e.g. CO2

Abstract

The invention discloses the construction methods that a kind of water transfer heavy metals in farmland of improving the soil removes system, and specific construction step is successively are as follows: farmland soil weight structure, building double-layer drainage ditch, building processing pond, building stirring pool, building sedimentation basin, building reservoir, building alkaline precipitating agent automatic adding device, building wind stirring device and building irrigation system;The rainwash of field imports reservoir by the runoff gutter of double-layer drainage ditch, alkaline precipitating agent is added automatically by processing pond behind the hydrops gutter of the soil hydrops inflow double-layer drainage ditch of field, it is sufficiently stirred after reaching stirring pool with wind-force, precipitating flows into reservoir after eventually arriving at sedimentation basin, and the water of reservoir is used for field irrigation.The present invention can gradually remove the heavy metal in agricultural land soil, effectively avoid heavy metal re-activation, and the hydrops and rainwash water source after removing removing heavy metals can be used as crop irrigation water circulation use, efficiently avoid loss of soil nutrient and save water resource.

Description

A kind of water transfer heavy metals in farmland of improving the soil removes the construction method of system
Technical field
The present invention relates to farmland soil heavy metals pollution remediation technology field, in particular to one kind improves the soil water transfer farmland with much money Belong to the construction method of removal system.
Background technique
China belongs to one of country of serious water shortage, in addition economic rapid development and population base increase and industrial or agricultural from Industry population quality is low and supervises not strict in enforcing the law or missing, keeps the surface water resources originally lacked seriously polluted, more exacerbates water resource Shortage becomes the country of contamination type water shortage.
It investigates and shows according to Ministry of Agriculture's soil environment monitoring, develop faster 320 emphasis contaminated areas in provinces and cities, 24, China In, field crops pollute exceeded agricultural cultivation area and account for the 20% of the monitoring and surveying gross area;Wherein content of beary metal is super Target agricultural output and area account for about 80% or more of the exceeded agricultural product total amount of pollutant and the gross area, especially Pb, Cd, Hg, Cu and its combined pollution are the most prominent.Cadmium in irrigating region soil, nickel, the content of zinc and copper are exceeded, and average content is respectively 65.31mg/kg, 1196.64mg/kg, 2799.25mg/kg and 145.78mg/kg are national soil environment secondary standard respectively 108.85,19.94,9.33 and 1.46 times.Cadmium pollution most serious in wheat, rice grain, wheat average content are 2.55mg/ Kg, is 25.5 times of national food hygienic standard, and nickel, chromium and Zn content are the 12.98 of national food hygienic standard, 6.12 respectively With 1.32 times.To ensure country's arable land red line and quality and security of agricultural products, farmland soil heavy metals pollution remediation technology is urgently Research.
Currently, the recovery technique of heavy metal pollution of soil, according to varied using method, wherein effect is preferably: logical It crosses to the alkaline fertilizers such as the alkaline matters such as using in farmland lime, slag or calcium magnesium phosphate, suction of the crops to heavy metal can be reduced It receives, the effect of chemical remediation is more satisfactory and expense is little, but stability is not strong, and heavy metal is stored in soil always, exists The problem of heavy metal reactivation.
Summary of the invention
It, can will be in agricultural land soil the object of the present invention is to provide a kind of farmland soil heavy metals pollution remediation technology field Heavy metal gradually remove, effectively avoid heavy metal re-activation, can will remove soil hydrops and earth's surface diameter after removing heavy metals Flow liquid is for irrigating, avoiding soil hydrops nutrient loss and saving water resource.
Above-mentioned technical purpose of the invention has the technical scheme that one kind improves the soil water transfer farmland with much money Belong to the construction method of removal system, specific construction step are as follows:
1) farmland soil weight structure
Firstly, the arable layer of field is removed, then remove remaining effective soil layer;Secondly, being put down if after removing being clay layer After whole with coarse sand be layered on clay layer surface formed passage of water layer, if removing after non-clay layer, need to roll the soil body, it is smooth after One layer of alkaline precipitating agent of surface spreading, then passage of water layer is formed on its surface with coarse sand paving;It is removed in advance finally, first replying Effective soil layer is on the surface of passage of water layer, then replys the arable layer removed in advance on the surface of effective soil layer;
2) double-layer drainage ditch is constructed
It excavates to form double-layer drainage ditch in field, bottom of trench casting concrete forms waterproof bottom of trench, the ditch of two sides after smoothing out Wall is poured to form permeable furrow bank bottom-up with non-fine concrete, and the permeable furrow bank is connect with passage of water layer, described The upper end of ditch wall is formed in parallel with the impermeable ditch body interlayer of the waterproof bottom of trench, the ditch body interlayer with concreting Double-layer drainage ditch is divided into the hydrops gutter of lower layer and the runoff gutter on upper layer, the upper surface of the ditch body interlayer two sides Waterproof furrow bank is formed with concreting, the upper end of the double-layer drainage ditch is erected with dismountable double-layer drainage trench cover, The double-layer drainage trench cover is equipped with several leakage holes;
3) processing pond is constructed
Buried hydrops processing pond, the processing pond and the hydrops are constructed in the water (flow) direction end of double-layer drainage ditch Gutter connection, as concrete structure, Chi Ding is provided with dismountable processing pond cover board in pond, the processing pond cover board with it is described The ditch body interlayer of double-layer drainage ditch is located at same elevation face;
4) stirring pool is constructed
The stirring pool of the buried connection processing pond water outlet is constructed, pond is as concrete structure;
5) sedimentation basin is constructed
The sedimentation basin of the buried connection stirring pool water outlet is constructed, pond is as concrete structure;
6) reservoir is constructed
Construct the reservoir of opened type, the reservoir and the intercepting drain of the double-layer drainage ditch and the water outlet of sedimentation basin Connection, pond is as concrete structure;
7) alkaline precipitating agent automatic adding device is constructed
Precipitating reagent automatic adding device is installed in the processing pond, precipitating reagent automatic adding device includes being set to hydrops Waterwheel below the end of gutter, with waterwheel by the precipitating reagent addition wheel of the first transmission axis connection, be set to precipitating reagent addition The precipitating reagent placing box of top is taken turns, the periphery of precipitating reagent addition wheel offers several adding troughs, and the lower end of precipitating reagent placing box is opened The adding mouth to match equipped with one with adding trough, precipitating reagent placing groove is interior to be added with alkaline precipitating agent;
8) wind stirring device is constructed
Field face above the stirring pool is equipped with wind stirring device, and the wind stirring device includes being set to Blender in the stirring pool, the leaf for being connect with the blender by second driving shaft and being set to field surface upper end Wheel;
9) irrigation system is constructed
Water pump, the irrigation system in the water pump connection field are laid in the reservoir.
By using above-mentioned technical proposal, the heavy metal ion in soil is seeped into the coarse sand passage of water under acting on by lower infiltration Layer reaches no longer lower infiltration after impermeable stratum, and passes through passage of water layer lateral transfer to the hydrops gutter of double-layer drainage ditch Interior, rainwash is imported into the runoff gutter of double-layer drainage ditch, is imported in reservoir eventually by intercepting drain, hydrops draining Hydrops in ditch flows to one end of waterwheel, and part flows into waterwheel, partially flows directly into processing pond, drives waterwheel rotation, and waterwheel is logical It crosses the first transmission shaft and drives precipitating reagent addition wheel rotation, when adding trough turns to opposite with adding mouth, alkaline precipitating agent, which is fallen into, to be added Add slot, alkaline precipitating agent is added to gutter with sink rotation, the water of processing pond is flowed to gutter drives alkaline precipitating agent Flow to stirring pool, wind-force drives the stirring of wind stirring device, and the water that alkaline precipitating agent is mixed with after stirring flows into sedimentation basin, in water Heavy metal exists in the form of cation, and alkaline precipitating agent forms anion after being dissolved in water, the heavy metal in precipitating pool inner water Cation occurs reversed formed with the anion that alkaline precipitating agent is formed and precipitates, when the hydrops in sedimentation basin reaches certain water level It will be flowed into reservoir;When needing to irrigate, irrigated by the irrigation system of water pump water delivery to field in reservoir.
The further setting of the present invention are as follows: the processing pond, stirring pool, sedimentation basin fall progressively connection in ladder.
The further setting of the present invention are as follows: the arable layer with a thickness of 15~20cm, the effective soil layer with a thickness of 40~60cm, the passage of water layer with a thickness of 15~20cm, the thickness of the passage of water layer and the permeable furrow bank and Elevation is all the same.
The further setting of the present invention are as follows: the alkaline precipitating agent is quick lime.
The further setting of the present invention are as follows: the wind power generation plant that the water pump power supply installed in the field is, wind-force hair Electric installation includes wind-driven generator and battery.
The further setting of the present invention are as follows: the double-layer drainage ditch double-layer drainage trench cover is opened in inverted v-shaped and leakage hole Set on double-layer drainage trench cover close to the two sides of waterproof side wall.
The further setting of the present invention are as follows: the quantity of the adding trough is identical as the quantity of the sink and position is along first Propeller shaft length direction corresponds.
In conclusion the invention has the following advantages:
One, the present apparatus can be by multistage, the multiple removals by the soil water of the heavy metal in farmland, gradually will be in farmland Heavy-metal movement remove, effectively avoid heavy metal re-activation;
Secondly, double-layer drainage ditch be made of hydrops gutter and runoff gutter, hydrops is separately discharged with rainwash, It prevents from leading to the excessive removal for influencing hydrops heavy metal of water flow due to rainfall, while being used to irrigate after rainwash being collected;
Thirdly, go in sedimentation basin the water source of the hydrops after removing heavy metals and rainwash to can be used as crop irrigation water circulation benefit With efficiently avoiding the loss of soil nutrient.
Detailed description of the invention
Fig. 1 the structural representation of present invention;
The cross-sectional view of Fig. 2 precipitating reagent addition wheel and precipitating reagent placing groove relationship;
The annexation figure of Fig. 3 waterwheel and precipitating reagent addition wheel;
Fig. 4 wind stirring apparatus structure schematic diagram;
The cross-sectional view of Fig. 5 field and double-layer drainage ditch structure.
In figure: 1, field;11, passage of water layer;12, effective soil layer, 13, arable layer;2, double-layer drainage ditch;21, impermeable Ditch bottom;22, permeable furrow bank;23, waterproof furrow bank;24, impermeable ditch body interlayer;25, hydrops gutter;26, runoff drains Ditch;3, double-layer drainage trench cover;31, leakage hole;41, waterwheel;42, the first transmission shaft;43, precipitating reagent addition wheel;44, precipitating reagent Placing groove;45, adding trough;46, adding mouth;47, processing pond cover board;5, processing pond;7, stirring pool;8, wind stirring device;81, Blender;82, second driving shaft;83, impeller;9, sedimentation basin;10, reservoir;101, intercepting drain;102, water pump;103, wind-force Power generator.
Specific embodiment
Below in conjunction with attached drawing, invention is further described in detail.
Embodiment, a kind of water transfer heavy metals in farmland of improving the soil remove the construction method of system, referring to Fig.1-5, specific to construct Step are as follows:
1) farmland soil weight structure
Firstly, 20cm is removed in the arable layer 13 of field, then remove the effective soil layer 12 of remaining thickness 50cm;Secondly, If removing after be clay layer, it is smooth after with coarse sand be layered on clay layer surface 20cm formed passage of water layer 11, clay layer have compared with Good impermeability, can effectively prevent seeping under hydrops, if non-clay layer after removing, need to roll the soil body, it is smooth after in surface spreading One layer of alkaline precipitating agent, then be layered on its surface 20cm with coarse sand and form passage of water layer 11, still there is underwater infiltration after preventing compacting, The hydrops permeated downwards heavy metal ion after alkaline precipitating agent forms precipitating, can reduce alkaline heavy metal and flow into rivers and lakes Amount;Finally, first replying the effective soil layer 12 removed in advance on the surface of passage of water layer 11, then reply the farming removed in advance Layer 13 is on the surface of effective soil layer 12.
2) double-layer drainage ditch is constructed
It is excavated between two pieces of fields 1 and forms double-layer drainage ditch 2, if field face ridging when farming, ridge is towards double-layer drainage ditch 2, rainwash of being more convenient for flows to double-layer drainage ditch 2, and bottom of trench casting concrete forms waterproof bottom of trench 21, the ditch of two sides after smoothing out Wall is poured to form permeable furrow bank 22 bottom-up with non-fine concrete, and the cement consumption in the non-fine concrete wall is 200kg/m3, aggregate are the gravel that partial size is 15mm, and permeable furrow bank 22 is connect with passage of water layer 11, passage of water layer 11 and thoroughly The thickness and elevation of ditch wall 22 are all the same, and the upper end concreting of permeable furrow bank 22 forms one layer and is parallel to impermeable ditch Double-layer drainage ditch 2 is divided into the hydrops gutter 25 of lower layer by the impermeable ditch body interlayer 24 at bottom 21, impermeable ditch body interlayer 24 And the runoff gutter 26 on upper layer, the upper surface of impermeable 24 two sides of ditch body interlayer form waterproof furrow bank with concreting 23, the upper end of double-layer drainage ditch 2 is erected with a dismountable double-layer drainage trench cover 3, if double-layer drainage trench cover 3 offers Dry leakage hole 31, double-layer drainage trench cover 3 are opened in double-layer drainage trench cover 3 close to waterproof in inverted v-shaped and leakage hole 31 The two sides of furrow bank 23.
3) processing pond is constructed
A buried processing pond 5 is constructed in the water (flow) direction end of double-layer drainage ditch 2, processing pond 5 and hydrops drain Ditch 25 is connected to, and as concrete structure, Chi Ding is provided with one piece of dismountable processing pond cover board 47 in pond, processing pond cover board 47 and not Permeable ditch body interlayer 24 is located at sustained height plane.
4) stirring pool is constructed
The stirring pool 7 of buried connection 5 water outlet of drainage pool of building one, pond is as concrete structure.
5) sedimentation basin is constructed
The sedimentation basin 9 of buried connection 7 water outlet of stirring pool of building one, pond is as concrete structure.
6) reservoir is constructed
Construct the reservoir 10 of an opened type, the runoff gutter 26 and sedimentation basin 9 of reservoir 10 and double-layer drainage ditch 2 Rainwash is imported reservoir 10 by intercepting drain 101 by connection, runoff gutter 26, and pond is as concrete structure.
7) alkaline precipitating agent automatic adding device is constructed
Precipitating reagent automatic adding device is installed in drainage pool 5, precipitating reagent automatic adding device includes one and is set to product 41, one, waterwheel below 25 end of liquid gutter and the precipitating reagent addition that waterwheel 41 connect by the first transmission shaft 42 take turns 43, One is set to the precipitating reagent placing box of 43 top of precipitating reagent addition wheel, and the periphery of precipitating reagent addition wheel 43 offers several additions Slot 45, and the quantity of sink is identical and position is corresponded along 42 length direction of the first transmission shaft, water flow for the quantity of adding trough 45 Waterwheel 41 is driven to rotate, waterwheel 41 drives 43 rotation of precipitating reagent addition wheel, enables the additive amount of alkaline precipitating agent with dampening The change of flow and change, effectively ensure to add suitable alkaline precipitating agent, the lower end of precipitating reagent placing box offer one with The adding mouth 46 that adding trough 45 matches, precipitating reagent placing groove 44 is interior to be added with alkaline precipitating agent, and alkaline precipitating agent is quick lime.
8) wind stirring device is constructed
Field face above stirring pool 7 is equipped with wind stirring device 8, and wind stirring device 8 includes one and is set to 81, one, blender in stirring pool 7 are connect by second driving shaft 82 with blender 81 and are set to the impeller of field face upper end 83。
9) irrigation system is constructed
A water pump 102 is provided in reservoir 10, water pump 102 is connected to the irrigation system (figure omits) in field 1, field One wind power generation plant 103 powered for water pump 102 is installed, wind power generation plant 103 includes wind-driven generator and storage on 1 Battery (figure omits).
Wherein, processing pond 5, stirring pool 7, sedimentation basin 9 fall progressively connection in ladder.
Working principle: the hydrops in soil is seeped into coarse sand passage of water layer 11 under acting on by lower infiltration, reaches impermeable stratum It is no longer lower after 11 to seep, and pass through in passage of water layer lateral transfer to the hydrops gutter 25 of double-layer drainage ditch 2, rainwash It is imported into the runoff gutter 26 of double-layer drainage ditch 2, is flowed into reservoir 10 eventually by intercepting drain, in hydrops gutter 25 Hydrops flow to one end of waterwheel 41, part flows into waterwheel 41, partially flows directly into diversion pond, drives waterwheel 41 to rotate, waterwheel 41 drive 43 rotation of precipitating reagent addition wheel, when adding trough 45 turns to opposite with adding mouth 46, alkalinity by the first transmission shaft 42 Precipitating reagent falls into adding trough 45, alkaline precipitating agent is added to gutter with sink rotation, the water of processing pond is flowed to gutter Alkaline precipitating agent is driven to flow to stirring pool 7, wind-force drives wind stirring device 8 to stir, the water of alkaline precipitating agent is mixed with after stirring Sedimentation basin 9 is flowed into, the heavy metal in water exists in the form of cation, and alkaline precipitating agent forms anion after being dissolved in water, heavy The anion that heavy metal cation and alkaline precipitating agent in shallow lake pond 9 in water are formed occurs reversed formed and precipitates, when in sedimentation basin 9 Hydrops will be flowed into reservoir 10 when reaching certain water level;When needing to irrigate, start the water pump 102 in reservoir 10, It is the irrigation of field 1 by irrigation system.
The effect detection of this system is carried out, its step are as follows:
Common field and the soil for being provided with heavy metals removal recharge system field respectively take 1kg in the identical period, carry out soil Cadmium in earth, nickel, zinc and copper content detected, monthly detection is primary, continues 6 months, testing result is as follows:
Be provided with it can be seen from upper table comparing result the content of the heavy metal of heavy metals removal recharge system field with The passage of time gradually decreases, and the content of the heavy metal of common field as a comparison does not change substantially.
This specific embodiment is only explanation of the invention, is not limitation of the present invention, those skilled in the art Member can according to need the modification that not creative contribution is made to the present embodiment after reading this specification, but as long as at this All by the protection of Patent Law in the scope of the claims of invention.

Claims (7)

1. the construction method that a kind of water transfer heavy metals in farmland of improving the soil removes system, which is characterized in that specific construction step are as follows:
1) farmland soil weight structure
Firstly, the arable layer (13) of field (1) is removed, then remove remaining effective soil layer (12);Secondly, if being glutinous after removing Soil layer is layered on surface formation passage of water layer (11) of clay layer, if non-clay layer after removing, need to roll soil with coarse sand after smooth Body, it is smooth after in one layer of alkaline precipitating agent of surface spreading, then with coarse sand paving be formed on its surface passage of water layer (11);Finally, The effective soil layer (12) removed in advance is first replied on the surface of passage of water layer (11), then replys the arable layer (13) removed in advance On the surface of effective soil layer (12);
2) double-layer drainage ditch is constructed
It excavating and is formed double-layer drainage ditch (2) in field (1), bottom of trench casting concrete is formed waterproof bottom of trench (21) after smoothing out, and two The furrow bank of side is poured to be formed permeable furrow bank (22) bottom-up with non-fine concrete, the permeable furrow bank (22) and the passage of water Layer (11) connection, the upper end of the permeable furrow bank (22) is formed in parallel with the waterproof bottom of trench (21) no with concreting Double-layer drainage ditch (2) is divided into the hydrops gutter of lower layer by permeable ditch body interlayer (24), the impermeable ditch body interlayer (24) (25) and the runoff gutter (26) on upper layer, the upper surface of impermeable ditch body interlayer (24) two sides are formed with concreting Waterproof furrow bank (23), the upper end of the double-layer drainage ditch (2) is equipped with dismountable double-layer drainage trench cover (3), described double Layer drainage ditch cover plate (3) offers several leakage holes (31);
3) processing pond is constructed
It is constructed buried processing pond (5) in the water (flow) direction end of double-layer drainage ditch (2), the processing pond (5) and the product Liquid gutter (25) connection, as concrete structure, Chi Ding is provided with dismountable processing pond cover board (47), the processing pond in pond Cover board (47) and the impermeable ditch body interlayer (24) are located at sustained height plane;
4) stirring pool is constructed
The stirring pool (7) of buried connection processing pond (5) water outlet is constructed, pond is as concrete structure;
5) sedimentation basin is constructed
The sedimentation basin (9) of buried connection stirring pool (7) water outlet is constructed, pond is as concrete structure;
6) reservoir is constructed
Construct the reservoir (10) of opened type, the intercepting drain (101) of the reservoir (10) and the double-layer drainage ditch (2) and heavy The water outlet in shallow lake pond (9) is connected to, and pond is as concrete structure;
7) alkaline precipitating agent automatic adding device is constructed
Precipitating reagent automatic adding device is installed in the processing pond (5), precipitating reagent automatic adding device includes being set to draining Waterwheel (41) below ditch (6) end takes turns (43) with the precipitating reagent addition that waterwheel (41) connects by the first transmission shaft (42), sets The periphery of the precipitating reagent placing box being placed in above precipitating reagent addition wheel (43), precipitating reagent addition wheel (43) offers several adding troughs (45), the lower end of precipitating reagent placing box offers the adding mouth (46) to match with adding trough (45), precipitating reagent placing groove (44) alkaline precipitating agent is added in;
8) wind stirring device is constructed
Field face above the stirring pool (7) is equipped with wind stirring device (8), and the wind stirring device (8) includes The blender (81) that is set in the stirring pool (7) is connect and is set by second driving shaft (82) with the blender (81) It is placed in the impeller (83) of field face upper end;
9) irrigation system is constructed
It is provided with water pump (102) in the reservoir (10), the irrigation system on water pump (102) connection field (1).
2. the construction method that a kind of water transfer heavy metals in farmland of improving the soil according to claim 1 removes system, it is characterised in that: The processing pond (5), stirring pool (7), sedimentation basin (9) fall progressively connection in ladder.
3. the construction method that a kind of water transfer heavy metals in farmland of improving the soil according to claim 1 removes system, it is characterised in that: The arable layer (13) with a thickness of 15~20cm, the effective soil layer (12) with a thickness of 40~60cm, the passage of water Layer (11) with a thickness of 15~20cm, the thickness and elevation of the passage of water layer (11) and the permeable furrow bank (22) are homogeneous Together.
4. the construction method that a kind of water transfer heavy metals in farmland of improving the soil according to claim 1 removes system, it is characterised in that: The alkaline precipitating agent is quick lime.
5. the construction method that a kind of water transfer heavy metals in farmland of improving the soil according to claim 1 removes system, it is characterised in that: The wind power generation plant (103) of promising water pump (102) power supply is installed, wind power generation plant (103) includes wind on the field (1) Power generator and battery.
6. the construction method that a kind of water transfer heavy metals in farmland of improving the soil according to claim 1 removes system, it is characterised in that: The double-layer drainage ditch double-layer drainage trench cover (3) is opened in double-layer drainage ditch double-layer drainage in inverted v-shaped and leakage hole (31) Two sides of the trench cover (3) close to waterproof furrow bank (23).
7. the construction method that a kind of water transfer heavy metals in farmland of improving the soil according to claim 1 removes system, it is characterised in that: The quantity of the adding trough (45) is identical as the quantity of the sink and position is a pair of along the first transmission shaft (42) length direction one It answers.
CN201910437967.9A 2019-05-24 2019-05-24 A kind of water transfer heavy metals in farmland of improving the soil removes the construction method of system Pending CN110216139A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201910437967.9A CN110216139A (en) 2019-05-24 2019-05-24 A kind of water transfer heavy metals in farmland of improving the soil removes the construction method of system

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201910437967.9A CN110216139A (en) 2019-05-24 2019-05-24 A kind of water transfer heavy metals in farmland of improving the soil removes the construction method of system

Publications (1)

Publication Number Publication Date
CN110216139A true CN110216139A (en) 2019-09-10

Family

ID=67817903

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201910437967.9A Pending CN110216139A (en) 2019-05-24 2019-05-24 A kind of water transfer heavy metals in farmland of improving the soil removes the construction method of system

Country Status (1)

Country Link
CN (1) CN110216139A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114279899A (en) * 2021-12-28 2022-04-05 珠江水利委员会珠江水利科学研究院 Device for researching migration of heavy metals in sediment under different hydrodynamic conditions
CN114653743A (en) * 2022-03-08 2022-06-24 云南农业大学 Heavy metal contaminated soil treatment equipment

Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN203594009U (en) * 2013-11-08 2014-05-14 云南农业大学 Novel farmland drainage ditch
CN103858552A (en) * 2013-09-09 2014-06-18 轻工业环境保护研究所 Method for constructing soil of plough layer on coarse sand earth surface by heavy metal polluted sediment
CN104259192A (en) * 2014-09-24 2015-01-07 长江水利委员会长江科学院 Ecological water conservancy restoration system and method for heavy metal polluted farmland soil
CN105421314A (en) * 2015-12-11 2016-03-23 云南农业大学 Constructing method of waterlogged farmland water three-dimensional regulating and controlling system
CN106216370A (en) * 2016-08-04 2016-12-14 北京高能时代环境技术股份有限公司 A kind of method for repairing heavy metal polluted soil of farmland
CN206474502U (en) * 2017-01-16 2017-09-08 王迎春 Heavy-metal contaminated soil original position, which is stabilized, repairs field test system
CN107710940A (en) * 2017-09-05 2018-02-23 广东省生态环境技术研究所 One kind cultivates the organic reconstructing method of soil body when causing paddy field
CN108672482A (en) * 2018-04-20 2018-10-19 南安市创培电子科技有限公司 One heavy metal species fixative and heavy-metal contaminated soil curing
CN109626723A (en) * 2018-12-19 2019-04-16 北京建筑大学 A kind of ecological treatment system controlling agricultural non -point pollution

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103858552A (en) * 2013-09-09 2014-06-18 轻工业环境保护研究所 Method for constructing soil of plough layer on coarse sand earth surface by heavy metal polluted sediment
CN203594009U (en) * 2013-11-08 2014-05-14 云南农业大学 Novel farmland drainage ditch
CN104259192A (en) * 2014-09-24 2015-01-07 长江水利委员会长江科学院 Ecological water conservancy restoration system and method for heavy metal polluted farmland soil
CN105421314A (en) * 2015-12-11 2016-03-23 云南农业大学 Constructing method of waterlogged farmland water three-dimensional regulating and controlling system
CN106216370A (en) * 2016-08-04 2016-12-14 北京高能时代环境技术股份有限公司 A kind of method for repairing heavy metal polluted soil of farmland
CN206474502U (en) * 2017-01-16 2017-09-08 王迎春 Heavy-metal contaminated soil original position, which is stabilized, repairs field test system
CN107710940A (en) * 2017-09-05 2018-02-23 广东省生态环境技术研究所 One kind cultivates the organic reconstructing method of soil body when causing paddy field
CN108672482A (en) * 2018-04-20 2018-10-19 南安市创培电子科技有限公司 One heavy metal species fixative and heavy-metal contaminated soil curing
CN109626723A (en) * 2018-12-19 2019-04-16 北京建筑大学 A kind of ecological treatment system controlling agricultural non -point pollution

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114279899A (en) * 2021-12-28 2022-04-05 珠江水利委员会珠江水利科学研究院 Device for researching migration of heavy metals in sediment under different hydrodynamic conditions
CN114279899B (en) * 2021-12-28 2022-07-12 珠江水利委员会珠江水利科学研究院 Device for researching migration of heavy metals in sediment under different hydrodynamic conditions
CN114653743A (en) * 2022-03-08 2022-06-24 云南农业大学 Heavy metal contaminated soil treatment equipment

Similar Documents

Publication Publication Date Title
CN104174191B (en) Integral grit chamber for treating rainwater and treating method
CN105625549B (en) A kind of multifunction system for oozing worry available for sponge urban rainwater, harvesting and purifying
CN105735455B (en) One kind enters river pollution complex ecological closure works system
CN103334469B (en) The treatment system removed for inner city pollution of river bed mud and treatment process
CN106193261B (en) A kind of Collapsible Loess District rain flood harvests step man-made lake system and design method
CN106759781A (en) A kind of intelligent city rainwater regulating pondage system and its construction method
CN203213085U (en) Saline and alkaline land greening salt elimination and soil moisture conservation waterscape constructing system
CN107761897A (en) Self contained underground stores and oozes system
CN111646574A (en) Urban river water environment treatment method
CN110216139A (en) A kind of water transfer heavy metals in farmland of improving the soil removes the construction method of system
CN110741910A (en) Water collecting and supplying system and method for mine refuse dump
CN108625453A (en) Skyscraper sponge City complex system
CN204982778U (en) High -efficient artifical lake system that adjusts that purifies
CN102605853B (en) Facility for ecologically treating and recycling rainwater in central business district and method therefor
CN208121939U (en) The device with processing is collected for road initial rainwater
CN211793411U (en) Water collecting and supplying system for mine refuse dump
CN202610028U (en) Facility for ecological treatment and recycle of rainwater in central business district
CN111328489A (en) System and method for efficiently improving coastal heavy saline soil by rainwater
CN107690861A (en) A kind of stalk groove and its method for embedding
CN108557988A (en) A kind of the dryland soil filtration system and method for agricultural non-point source pollution control
CN108374477A (en) A kind of device collected for road initial rainwater with processing
CN209443563U (en) A kind of large-scale water storage system of molten mound depression people and animals' drinking water
CN107842089A (en) A kind of water resources circulation system based on green building
CN207176866U (en) A kind of sunk type lawn watering structure
CN205024044U (en) Self -control type man -made lake system

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: 20190910