CN105165167B - Method for desalting salinized soil - Google Patents

Method for desalting salinized soil Download PDF

Info

Publication number
CN105165167B
CN105165167B CN201510612311.8A CN201510612311A CN105165167B CN 105165167 B CN105165167 B CN 105165167B CN 201510612311 A CN201510612311 A CN 201510612311A CN 105165167 B CN105165167 B CN 105165167B
Authority
CN
China
Prior art keywords
saliferous
index
salt
salt content
volume index
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.)
Active
Application number
CN201510612311.8A
Other languages
Chinese (zh)
Other versions
CN105165167A (en
Inventor
王胜
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.)
Shandong Sunway Saline Alkali Soil Technology Co Ltd
Original Assignee
Weifang Yourong Industry 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
Application filed by Weifang Yourong Industry Co Ltd filed Critical Weifang Yourong Industry Co Ltd
Priority to CN201510612311.8A priority Critical patent/CN105165167B/en
Publication of CN105165167A publication Critical patent/CN105165167A/en
Application granted granted Critical
Publication of CN105165167B publication Critical patent/CN105165167B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • 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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture

Abstract

The invention provides a kind of method for desalting salinized soil, comprise the following steps:Ditching is carried out in the salt-soda soil for treating desalination, channel and growing area is formed;Halophytes is planted in channel;Desalting processing is carried out to growing area;In plantation layer, salt content monitor probe is set, determine saliferous volume index and monitor supervision platform is sent to by Internet Server, monitor supervision platform is judged by presetting the first salt index and the second salt index with the salt index of detection, early warning or alarm signal are made, desalting processing is periodically irrigated to plantation layer according to the signal made.Whereby, the present invention i.e. can be with the saliferous volume index on accurate detection plantation layer bottom, middle part and top, it is monitored by Network Information platform, periodically carry out the irrigation desalinization of soil by flooding or leaching, increase salt discharge effect, shorten the salt discharge cycle, improve the survival rate of plant, the salt solution plantation halophytes of collection is used simultaneously, resource is reached rational utilization.

Description

Method for desalting salinized soil
Technical field
The present invention relates to technical field of land improvement, more particularly to a kind of method for desalting salinized soil.
Background technology
More than 18000 kilometers of China's seashore line length.It is the ground for moving back sea that coastal saline-alkali area is mostly, and it is strand salt that its soil is most of Alkaline earth, directly develops on beach salt marsh mud.This kind of salt-soda soil heavy texture, not only upper soll layer salification weight, It is close with original salt marsh mud and heart subsoil salt content is also very high.Simultaneously as coastal region underground water buried depth is shallow and shallow Layer underground water is salt water, and high salinity underground water is accumulated in upper layer of soil with strong terramycin dregs, and soil salt content exists more Between 0.4-2%, even up to 3-4%.Another feature of coastal saline-alkali soil, is soil and groundwater salinity chemistry Composition is consistent with seawater, and sodium chloride salt has comparative advantage, and soil sodium adsorption ratio is very high, adds and is formed at salt marsh mud, causes soil Earth heavy texture, structure are poor, gas permeability is bad, in addition to the extremely strong a small number of halophytes of salt tolerance, common crops, grass Level ground, flowers, tree and shrubs etc. can not grow.
At present, the area in salt-soda soil is constantly expanding, the universities and colleges of lot of domestic and foreign, and scientific research institutions are being studied always should To the governing problem in salt-soda soil, most of hydraulic engineering methods for using, biological harnessing method, chemical-agent technique and Chinese scholar are permitted Will it is female at the beginning of the eighties in last century it is also proposed that flush discharge order by " it is light after first weighing, i.e., first wash heavy saline, after wash light salt-soda soil With downstream behind upstream first in the range of the sublateral canal " desalinization of soil by flooding or leaching method etc..
But, these methods also achieve certain effect on the basis of certain, but numerous technical sides for showing Case and construction technology are more delayed, and to China, urgently land resource leaved for development is slower and relatively costly, and salt discharge effect is not Substantially.
In summary, prior art there will naturally be inconvenience and defect in actual use, it is therefore necessary to be improved.
The content of the invention
For above-mentioned defect, it is an object of the invention to provide a kind of method for desalting salinized soil, it can accurately be examined The saliferous volume index of plantation layer is surveyed, is monitored by Network Information platform, periodically carry out the irrigation desalinization of soil by flooding or leaching, increase salt discharge effect Really, shorten the salt discharge cycle, improve the survival rate of plant, while the salt solution plant utilization that will be collected, makes resource reach rationalization Utilize.
To achieve these goals, the present invention provides a kind of method for desalting salinized soil, comprises the following steps:
A, carry out ditching in the salt-soda soil for treating desalination, form channel and growing area;
B, halophytes is planted in channel;
C, desalting processing is carried out to growing area, step c is specifically included:
C1, metalling is laid in the middle of growing area, blocking growing area forms capillary, it is to avoid saline-alkali water is returned to;
C2, metalling top lay salt discharge alkali pipe, for the saline-alkali water returned on growing area bottom to be expelled into canal in time Road;
C3, salt discharge alkali pipe top cover saline-alkali soil, formed plantation layer, to plantation layer carry out 24~48 hours fresh water irrigations Desalination.
D, to plantation layer carry out desalting effect detection process, step d is specifically included:
D1, salt content monitor probe is respectively provided with the plantation bottom of layer, middle part and top, is visited by the salt content Chaining pin determines the saliferous volume index of plantation layer, obtains salt content detection index;
D2, salt content detection index in step d1 is sent to monitor supervision platform by the webserver;
D3, the monitor supervision platform preset the first saliferous volume index and the second saliferous volume index, the first saliferous volume index Less than the second saliferous volume index, the monitor supervision platform by the first saliferous volume index, the second saliferous volume index with it is described Salt content detection index compares size;
The salt content detection index higher than the first saliferous volume index and during less than the second saliferous volume index, institute State monitor supervision platform and send early warning signal;
When the salt content detection index is higher than the second saliferous volume index, the monitor supervision platform sends alarm signal;
D4, the early warning signal in step d3 and the alarm signal, desalting processing is periodically irrigated to plantation layer.
As preferred technical scheme, in the step d1 salt content detection index include bottom salt content Monitoring Index, Middle part salt content Monitoring Index and top salt content Monitoring Index.
Used as preferred technical scheme, early warning signal includes bottom early warning signal, middle part early warning signal in the step d3 With top early warning signal, the alarm signal include bottom alarm signal, middle part alarm signal and top alarm signal.
Used as preferred technical scheme, saliferous volume index described in the step d is the solubility for determining plantation layer soil Salt content, sodium ions content, calculate the first factor value for obtaining saliferous volume index.
Used as preferred technical scheme, the first saliferous volume index described in the step d3 is 2g/L~3g/L, described the Two saliferous volume indexes are 5g/L~6g/L.
Used as preferred technical scheme, the salt discharge alkali pipe and the channel can be laid in the same direction, also can vertically lay.
As preferred technical scheme, straw layer is provided between the metalling and the salt discharge alkali pipe.
Used as preferred technical scheme, the halophytes includes salicornia europaeal.
Used as preferred technical scheme, the channel can dig a plurality of, and the channel intersects around growing area, the salt discharge Alkali pipe can both ends open simultaneously to both sides channel salt discharge buck.
Used as preferred technical scheme, the salt content monitor probe can spacing 20~30 on plantation layer surface direction Rice interval setting.
Beneficial effects of the present invention:By providing a kind of method for desalting salinized soil, the method can be examined accurately the present invention The saliferous volume index on plantation layer bottom, middle part and top is surveyed, is monitored by Network Information platform, periodically carried out irrigation and wash Salt, increases salt discharge effect, shortens the salt discharge cycle, improves the survival rate of plant, while the salt solution plant utilization that will be collected, makes money Source reaches rational utilization.
Specific 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.
The present invention provides a kind of method for desalting salinized soil, comprises the following steps:
A, carry out ditching in the salt-soda soil for treating desalination, form channel and growing area;
B, halophytes is planted in channel;
C, desalting processing is carried out to growing area, step c is specifically included:
C1, metalling is laid in the middle of growing area, blocking growing area forms capillary, it is to avoid saline-alkali water is returned to;
C2, metalling top lay salt discharge alkali pipe, for the saline-alkali water returned on growing area bottom to be expelled into canal in time Road;
C3, salt discharge alkali pipe top cover saline-alkali soil, formed plantation layer, to plantation layer carry out 24~48 hours fresh water irrigations Desalination.
D, to plantation layer carry out desalting effect detection process, step d is specifically included:
D1, salt content monitor probe is respectively provided with the plantation bottom of layer, middle part and top, is visited by the salt content Chaining pin determines the saliferous volume index of plantation layer, obtains salt content detection index;
D2, salt content detection index in step d1 is sent to monitor supervision platform by the webserver;
D3, the monitor supervision platform preset the first saliferous volume index and the second saliferous volume index, the first saliferous volume index Less than the second saliferous volume index, the monitor supervision platform by the first saliferous volume index, the second saliferous volume index with it is described Salt content detection index compares size;
The salt content detection index higher than the first saliferous volume index and during less than the second saliferous volume index, institute State monitor supervision platform and send early warning signal;
When the salt content detection index is higher than the second saliferous volume index, the monitor supervision platform sends alarm signal;
D4, the early warning signal in step d3 and the alarm signal, desalting processing is periodically irrigated to plantation layer.
Preferably, salt content detection index includes bottom salt content Monitoring Index, middle part salt content in the step d1 Monitoring Index and top salt content Monitoring Index.
Preferably, early warning signal includes bottom early warning signal, middle part early warning signal and top early warning in the step d3 Signal, the alarm signal includes bottom alarm signal, middle part alarm signal and top alarm signal.
Preferably, saliferous volume index described in the step d be determine the plantation soluble-salt content of layer soil, sodium from Sub- content, calculates the first factor value for obtaining saliferous volume index.
Preferably, the first saliferous volume index described in the step d3 is 3g/L, and the second saliferous volume index is 6g/ L。
Preferably, the salt discharge alkali pipe and the channel can be laid in the same direction, also can vertically lay.
Preferably, it is provided with straw layer between the metalling and the salt discharge alkali pipe.
Preferably, the halophytes includes salicornia europaeal.
Preferably, the channel can dig a plurality of, and the channel intersects around growing area, and the salt discharge alkali pipe can two ends Opening is simultaneously to the channel salt discharge buck of both sides.
Preferably, the salt content monitor probe on plantation layer surface direction can 20~30 meters of intervals of spacing set Put.
Embodiment one:
Ditching is carried out on the salt-soda soil for treat desalination, channel and growing area is formed, various channels can be dug, intersected around kind Growing area, can be used for the halophytes such as plantation salicornia europaeal in channel.Metalling is laid in the middle of growing area, capillary is formed to block Pipe, it is to avoid saline-alkali water is returned to, on metalling top, laying straw layer re-lays laying salt discharge alkali pipe, and it is saline and alkaline that straw layer plays protection The effect of pipe.Laying or the vertical laying in the same direction of salt discharge alkali Guan Keyu channels, salt discharge alkali pipe can one end or both ends open, be easy to On the saline-alkali water that returns be expelled to channel in time, cover saline-alkali soil on saline and alkaline pipe top, carry out the irrigation of 24~48 hours, it is real Existing desalting processing.
Salt content monitor probe is respectively provided with the bottom of plantation layer, middle part and top, from plantation layer just face direction, The salt content survey meter probe of top plantation layer can 20~30 meters of interval settings of spacing, the setting phase on bottom and noon and top Together, such setting can more accurately detect the salt content of plantation layer.Pin is detected by the salt content and determines plantation layer Saliferous volume index, the saliferous volume index is soluble-salt content, the sodium ions content for determining plantation layer soil, calculates acquisition and contains The first factor value of salt volume index, detects pin and measures bottom salt content detection index, middle part salt content and detect by salt content Index and top salt content detection index.The bottom salt content detection index, middle part salt content detection index and top are contained Salt amount detection index is sent to monitor supervision platform by the webserver.The monitor supervision platform default first is 3g/L containing saline and alkaline index It is 6g/L containing saline and alkaline index with second, described first contains saline and alkaline index, the monitor supervision platform less than described second containing saline and alkaline index Detected by the first saliferous volume index, the second saliferous volume index and the bottom salt content detection index, middle part salt content Index and top salt content detection index compare size.Comparative result is as follows:
When the bottom salt content Monitoring Index refers to more than the first saliferous volume index 3g/L and less than the second salt content Number 6g/L, the middle part salt content detection index and top salt content detection index are respectively less than the first saliferous volume index 3g/L When, the monitor supervision platform sends bottom early warning signal;
When the middle part salt content Monitoring Index refers to more than the first saliferous volume index 3g/L and less than the second salt content Number 6g/L, the bottom salt content detection index and top salt content detection index are respectively less than the first saliferous volume index 3g/L When, the monitor supervision platform sends middle part early warning signal;
When the top salt content Monitoring Index refers to more than the first saliferous volume index 3g/L and less than the second salt content Number 6g/L, the bottom salt content detection index and middle part salt content detection index are respectively less than the first saliferous volume index 3g/L When, the monitor supervision platform sends top early warning signal;
When the bottom salt content Monitoring Index and middle part salt content detection index are all higher than the first saliferous volume index 3g/L and less than the second saliferous volume index 6g/L, the top salt content detection index is less than the first saliferous volume index 3g/L When, the monitor supervision platform sends bottom early warning signal and middle part early warning signal;
When the bottom salt content Monitoring Index and top salt content detection index are all higher than the first saliferous volume index 3g/L and less than the second saliferous volume index 6g/L, the middle part salt content detection index is less than the first saliferous volume index 3g/L When, the monitor supervision platform sends bottom early warning signal and top early warning signal;
When the middle part salt content Monitoring Index and top salt content detection index are all higher than the first saliferous volume index 3g/L and less than the second saliferous volume index 6g/L, the bottom salt content detection index is less than the first saliferous volume index 3g/L When, the monitor supervision platform sends middle part early warning signal and top early warning signal;
When the bottom salt content Monitoring Index, middle part salt content detection index and top salt content detection index are all higher than The first saliferous volume index 3g/L and during less than the second saliferous volume index 6g/L, the monitor supervision platform sends bottom early warning letter Number, middle part early warning signal and top early warning signal;
When the bottom salt content detection index, middle part saliferous volume index or top salt content detection index are more than described the During two saliferous volume index 6g/L, the monitor supervision platform sends bottom alarm signal, middle part alarm signal or top alarm signal;
When the bottom salt content detection index and middle part saliferous volume index are more than the second saliferous volume index 6g/L, The monitor supervision platform sends bottom alarm signal and middle part alarm signal;
When the bottom salt content detection index and top saliferous volume index are more than the second saliferous volume index 6g/L, The monitor supervision platform sends bottom alarm signal and top alarm signal;
When the middle part salt content detection index and top saliferous volume index are more than the second saliferous volume index 6g/L, The monitor supervision platform sends middle part alarm signal and top alarm signal;
Described in being all higher than when the bottom salt content detection index, middle part salt content detection index and top saliferous volume index During the second saliferous volume index 6g/L, the monitor supervision platform sends bottom alarm signal middle part alarm signal and top alarm signal;
The early warning signal and alarm signal sent according to monitor supervision platform described above, periodically irrigate at desalination plantation layer Reason.Irrigated according to above-mentioned steps, not only rationally using freshwater resources but also can be carried out scientific application of irrigation, be conducive to planting layer Plant growth.
In sum, the present invention is that can plant layer with accurate detection by providing a kind of method for desalting salinized soil, the method The saliferous volume index on bottom, middle part and top, is monitored by Network Information platform, periodically carries out the irrigation desalinization of soil by flooding or leaching, is increased Salt discharge effect, shortens the salt discharge cycle, improves the survival rate of plant, while the salt solution plantation halophytes of collection is subject into profit With making resource reach rational utilization.
Certainly, the present invention can also have other various embodiments, ripe in the case of without departing substantially from spirit of the invention and its essence Know those skilled in the art and work as and various corresponding changes and deformation, but these corresponding changes and change can be made according to the present invention Shape should all belong to the protection domain of appended claims of the invention.

Claims (9)

1. a kind of method for desalting salinized soil, it is characterised in that comprise the following steps:
A, carry out ditching in the salt-soda soil for treating desalination, form channel and growing area;
B, halophytes is planted in channel;
C, desalting processing is carried out to growing area, step c is specifically included:
C1, metalling is laid in the middle of growing area, blocking growing area forms capillary, it is to avoid saline-alkali water is returned to;
C2, metalling top lay salt discharge alkali pipe, for the saline-alkali water returned on growing area bottom to be expelled into channel in time;
C3, saline-alkali soil is covered on salt discharge alkali pipe top, form plantation layer, carrying out 24~48 hours fresh water irrigations to plantation layer takes off Salt;
D, to plantation layer carry out desalting effect detection process, step d is specifically included:
D1, salt content monitor probe is respectively provided with the plantation bottom of layer, middle part and top, pin is detected by the salt content The saliferous volume index of plantation layer is determined, salt content detection index is obtained;
D2, salt content detection index in step d1 is sent to monitor supervision platform by the webserver;
D3, the monitor supervision platform preset the first saliferous volume index and the second saliferous volume index, and the first saliferous volume index is less than The second saliferous volume index, the monitor supervision platform is by the first saliferous volume index, the second saliferous volume index and the saliferous Amount detection index compares size;
The salt content detection index higher than the first saliferous volume index and during less than the second saliferous volume index, the prison Control platform sends early warning signal;
When the salt content detection index is higher than the second saliferous volume index, the monitor supervision platform sends alarm signal;
D4, the early warning signal in step d3 and the alarm signal, desalting processing is periodically irrigated to plantation layer.
2. method for desalting salinized soil according to claim 1, it is characterised in that salt content detection index in the step d1 Including bottom salt content Monitoring Index, middle part salt content Monitoring Index and top salt content Monitoring Index.
3. method for desalting salinized soil according to claim 2, its feature with early warning signal includes in the step d3 Portion's early warning signal, middle part early warning signal and top early warning signal, the alarm signal include bottom alarm signal, middle part alarm signal Number and top alarm signal.
4. the method for desalting salinized soil according to claim 1 or 2 or 3, it is characterised in that saliferous described in the step d Volume index is soluble-salt content, the sodium ions content for determining plantation layer soil, calculates the first master point for obtaining saliferous volume index Value.
5. the method for desalting salinized soil according to claim 1 or 2 or 3, it is characterised in that first described in the step d3 Saliferous volume index is 2g/L~3g/L, and the second saliferous volume index is 5g/L~6g/L.
6. the method for desalting salinized soil according to claim 1 or 2 or 3, it is characterised in that the salt discharge alkali pipe and the canal Road is laying or vertical laying in the same direction.
7. the method for desalting salinized soil according to claim 1 or 2 or 3, it is characterised in that the metalling and the salt discharge Straw layer is provided between alkali pipe.
8. the method for desalting salinized soil according to claim 1 or 2 or 3, it is characterised in that the halophytes is salt angle Grass.
9. the method for desalting salinized soil according to claim 1 or 2 or 3, it is characterised in that the salt content monitor probe Spacing is 20~30 meters of interval settings on plantation layer surface direction.
CN201510612311.8A 2015-09-23 2015-09-23 Method for desalting salinized soil Active CN105165167B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201510612311.8A CN105165167B (en) 2015-09-23 2015-09-23 Method for desalting salinized soil

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201510612311.8A CN105165167B (en) 2015-09-23 2015-09-23 Method for desalting salinized soil

Publications (2)

Publication Number Publication Date
CN105165167A CN105165167A (en) 2015-12-23
CN105165167B true CN105165167B (en) 2017-07-07

Family

ID=54888062

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201510612311.8A Active CN105165167B (en) 2015-09-23 2015-09-23 Method for desalting salinized soil

Country Status (1)

Country Link
CN (1) CN105165167B (en)

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107318290A (en) * 2017-07-27 2017-11-07 郭婷 It is capable of the salt-soda soil restorative procedure of Planting Crops
CN107371431A (en) * 2017-07-27 2017-11-24 郭婷 The salt-soda soil restorative procedure of timely salt discharge
CN108513871A (en) * 2018-04-16 2018-09-11 上海市园林科学规划研究院 Method for planting of the halophytes salt grass on brown ground saline-alkali soil
CN108781576B (en) * 2018-05-25 2021-06-01 河海大学 Beach desalting method coupling water circulation
CN112655306A (en) * 2020-12-24 2021-04-16 常熟康艺建设有限公司 Saline-alkali soil greening method and greening system

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101647336A (en) * 2009-08-28 2010-02-17 中国科学院南京土壤研究所 Topsoil salt-control method of planting salt-tolerant plant in mudflat kaline soil
CN102037805A (en) * 2010-09-29 2011-05-04 中国科学院南京土壤研究所 Method for controlling salt and saving water of nutritional soil for planting crops on mudflat saline-alkali land
CN102057775A (en) * 2010-11-15 2011-05-18 中国科学院南京土壤研究所 Controlled-salinity cultivation method for plating crop on moderate and medium and severe saline-alkali soil
CN102900059A (en) * 2012-11-06 2013-01-30 河海大学 Combined draining and saline controlling system for saline and alkaline land
CN104206064A (en) * 2013-06-04 2014-12-17 河南山水园林绿化工程有限公司 Underground salt elimination method for saline and alkali land

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101647336A (en) * 2009-08-28 2010-02-17 中国科学院南京土壤研究所 Topsoil salt-control method of planting salt-tolerant plant in mudflat kaline soil
CN102037805A (en) * 2010-09-29 2011-05-04 中国科学院南京土壤研究所 Method for controlling salt and saving water of nutritional soil for planting crops on mudflat saline-alkali land
CN102057775A (en) * 2010-11-15 2011-05-18 中国科学院南京土壤研究所 Controlled-salinity cultivation method for plating crop on moderate and medium and severe saline-alkali soil
CN102900059A (en) * 2012-11-06 2013-01-30 河海大学 Combined draining and saline controlling system for saline and alkaline land
CN104206064A (en) * 2013-06-04 2014-12-17 河南山水园林绿化工程有限公司 Underground salt elimination method for saline and alkali land

Also Published As

Publication number Publication date
CN105165167A (en) 2015-12-23

Similar Documents

Publication Publication Date Title
CN105165167B (en) Method for desalting salinized soil
Foster et al. Impact of irrigated agriculture on groundwater-recharge salinity: a major sustainability concern in semi-arid regions
CN103460843B (en) Quick saline-alkali land desalting system method by means of concealed-tube irrigation and drainage
Liu et al. Analysis of the contribution of groundwater to evapotranspiration in an arid irrigation district with shallow water table
CN100479641C (en) Process for improving alkaline land by utilizing brackish water natural freezing
CN201649063U (en) Shallow-embedding alkali-removing and drainage device of concealed pipe in alkaline waterlogged lowland
El Bastawesy et al. Assessment of waterlogging in agricultural megaprojects in the closed drainage basins of the Western Desert of Egypt
Danierhan et al. Effects of emitter discharge rates on soil salinity distribution and cotton (Gossypium hirsutum L.) yield under drip irrigation with plastic mulch in an arid region of Northwest China
Silburn et al. The Australian Cotton Industry and four decades of deep drainage research: a review
Cetin et al. Assessing drainage problem areas by GIS: A case study in the Eastern Mediterranean Region of Turkey
Xinlin et al. Comparative investigation on soil salinity leaching under subsurface drainage and ditch drainage in Xinjiang arid region
CN102160482B (en) Salt-resistant type terrace planting method for seaside salt wasteland
CN106961864A (en) The alkaline land improving system and its modification method of a kind of wells connecting with canals
CN106358479A (en) Open trench-concealed conduit combined water discharging and salt reducing method
Robinson 30 years of forest hydrology changes at Coalburn: water balance and extreme flows
CN105144888A (en) Saline land improvement method and improvement system
CN106376267A (en) Internet of Things saline-alkali land improving method with video scanning function
CN103548440B (en) Hair row formula pipe drainage method under a kind of shallow embedding condition
CN102612883B (en) Saline discharge and alkali reduction concealed conduit device for saline-alkali soil
Han et al. Runoff formation from experimental plot, field, to small catchment scales in agricultural North Huaihe River Plain, China
CN112012164A (en) Ecological riverway restoration system in northwest desert area based on branch of a river infiltrating wheel irrigation and construction method
CN106134560A (en) A kind of improve beach saline-alkali ground the polymerization that plants economic crops
CN110063242A (en) Winter wheat brackish water irrigation method and system
Smith Rainfall and irrigation controls on groundwater rise and salinity risk in the Ord River Irrigation Area, northern Australia
CN204968403U (en) Saline soil reclamation system

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
TR01 Transfer of patent right

Effective date of registration: 20190505

Address after: 261108 7th Floor, 99 Xiangjiang Street, Weifang Binhai Economic Development Zone, Shandong Province

Patentee after: Shandong Sheng Wei salt alkali land Technology Co., Ltd.

Address before: 261106 99 Xiangjiang street, Binhai Economic Development Zone, Weifang, Shandong

Patentee before: Weifang You Rong Industrial Co., Ltd.

TR01 Transfer of patent right