CN109270124A - A kind of Soil salinity prediction technique based on machine learning regression algorithm - Google Patents
A kind of Soil salinity prediction technique based on machine learning regression algorithm Download PDFInfo
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Abstract
The invention discloses a kind of Soil salinity prediction techniques based on machine learning regression algorithm, include the following steps: S1, using equilateral triangle as measuring point shape, using the actual measurement salinity of three angle points of EM38 the earth conductivity gauge acquisition triangle, when measurement, vertical reading EM is readVEM is read with levelH, it is averaged the salinity as delta-shaped region, measures the EM of several delta-shaped regionsHAnd EMVFor basic truth training set (TS);S2, soil constitution is obtained using the removal vegetation contribution of L-band Radar backscattering coefficients;S3, it plot will be surveyed by direct rasterizing is converted to grid and create training set (TS);S4, using above-mentioned training set (TS), (RFR) algorithm modelling application is returned using random forest and carries out salinity prediction in joint data set.
Description
Technical field
The present invention relates to Soil salinity detection fields, and in particular to a kind of Soil salinity based on machine learning regression algorithm
Prediction technique.
Background technique
The soil salinization is suppressed one of the important soil obstruction factor of crop growthing development.The soil salinization influences
Crop production and grain security.The spatial distribution and soil salinization severity for drawing salinity to agricultural management and are developed to
It closes important.
Summary of the invention
To solve the above problems, the present invention provides a kind of Soil salinity prediction sides based on machine learning regression algorithm
Method.
To achieve the above object, the technical scheme adopted by the invention is as follows:
A kind of Soil salinity prediction technique based on machine learning regression algorithm, includes the following steps:
S1, using equilateral triangle as measuring point shape, using EM38 the earth conductivity gauge acquisition triangle three angle points reality
Salinity is surveyed, when measurement, reads vertical reading EMVEM is read with levelH, it is averaged the salinity as delta-shaped region, if measurement
The EM of dry delta-shaped regionHAnd EMVFor basic truth training set (TS);
S2, soil constitution is obtained using the removal vegetation contribution of L-band Radar backscattering coefficients;
S3, it plot will be surveyed by direct rasterizing is converted to grid and create training set (TS);
S4, using above-mentioned training set (TS), using random forest return (RFR) algorithm modelling application in joint data set into
The prediction of row salinity.
Further, in the step S1,15-20 meters of the side length of the equilateral triangle, it is ensured that triangle can be approximate
Indicate a TM (thematic imager) pixel;Measure specification 1m × 1m of block.
Further, the step S2 specifically comprises the following steps:
S21, LANDSAT 5 (Landsat 5) the TM image obtained from European Space Agency is calibrated with Radio Measurement, and adopt
Additional atmospheric effect is eliminated with scattering method model, each wave band of generated reflectivity is reset to 0-1;
S22, geometric correction is carried out to the 1.5 grades of radar results obtained from European Space Agency, and pixel is readjusted
12.5 meters of size, the digital quantization value (DN) for receiving HH and horizontal emission vertical reception HV to horizontal emission level carry out respectively
Correction, according to formulaBe converted to backscattering coefficient (σ0 HH、σ0 Hv);Then
Spot or noise are removed using enhanced Lee filter (the Enhanced Lee size of filter3 × 3, Lee 1980), exports σ0 HH
And σ0 Hv, lay equal stress on and be amplified to 30m pixel for matching TM data;
The water-cloud model that S23, building vegetation water content (VWC) influence Radar backscattering coefficients:
L2=exp (- 2BV2sec(θi))
Wherein, σ0It is total backscattering coefficient (σ from Vegetation canopy and soil0 HH、σ0 Hv);σ0 vegIt is the backward of vegetation
Contribution of scatters, σ0 soilIt is the contribution of scatters of soil;L2It is two-way vegetation decaying;θiThe incidence angle of radar beam, A and B are vegetation
Parameter;V1And V2It is vegetation description, V1It is applicable in leaf area index LAI (m2m-2), V2It is applicable in volumetric water content of soil VWC (kgm-2);
S24, it takes:
LAI=0.091exp (3.7579GDVI2) (R2=0.932)
VWC=192.64NDVI5-417.46NDVI4+347.96NDVI3-138.93NDVI2+30.699NDVI-2.822
(kg·m-2)(R2=0.990);
A=0.0045, B=0.4179;
With 34.3 ° for θiiThe incidence angle of radar beam calculates vegetation and removes backscattering coefficient (σ0 HH、σ0 Hv)。
Further, the step S3 specifically comprises the following steps:
Using the point in ArcGIS to grid crossover tool, it is 30,60 that average field measurement figure, which is converted to raster unit,
With 90 meters of sizes, then resets and arrive 30m pixel, composition data collection.
Further, the step S4 specifically comprises the following steps:
S41, it is modeled using random forest regression algorithm RFR, using all 12 wave bands as input variable, utilizes observation
The preset value 100 of (training set (TS)) in EnMap-Box;
The square root of all features is chosen with the number of the randomly selected feature of each node or variable number;
Ending standard (be used for node split), wherein preset value is smallest sample number in node, 1, according to gini index meter
The minimum impurity of calculation, 0;
EM will be rasterizedVOr EMHAfter (EM38 is vertically read or horizontal reading) is TS (training set) parametrization, by generation
RFR model is applied to combined data set, to predict soil apparent salinity (Eca).
Further, further include the steps that soil apparent salinity Eca being converted to soil conductivity ece, wherein ECe-
Relationship between EM38 reading and (Eca) is expressed as follows:
ECe(dSm-1)=0.0005EMV 2-0.0779EMV+12.655(R2=0.850);
ECe(dSm-1)=0.0002EMH 2+0.0956EMH+0.0688(R2=0.791).
The invention has the following advantages:
The forecast analysis for realizing Soil salinity to agricultural management and develops significant, random forest regression algorithm
RFR charts for Soil salinity, there is higher precision and lower normalization root-mean-square error.
Specific embodiment
The present invention is described in detail combined with specific embodiments below.Following embodiment will be helpful to the technology of this field
Personnel further understand the present invention, but the invention is not limited in any way.It should be pointed out that the ordinary skill of this field
For personnel, without departing from the inventive concept of the premise, various modifications and improvements can be made.These belong to the present invention
Protection scope.
A kind of Soil salinity prediction technique based on machine learning regression algorithm of the embodiment of the present invention, including walk as follows
It is rapid:
S1, using equilateral triangle as measuring point shape, using EM38 the earth conductivity gauge acquisition triangle three angle points reality
Survey salinity, 15-20 meters of the side length of the equilateral triangle, it is ensured that triangle can with one TM of approximate representation (thematic imager) as
Element;Measure specification 1m × 1m of block;When measurement, vertical reading EM is readVEM is read with levelH, it is averaged as triangle
The salinity in region measures the EM of several delta-shaped regionsHAnd EMVFor basic truth training set (TS);
S2, soil constitution is obtained using the removal vegetation contribution of L-band Radar backscattering coefficients;
S21, it is calibrated with Radio Measurement from European Space Agency LANDSAT 5 (Landsat 5) TM image, and using scattering
Method model eliminates additional atmospheric effect, and each wave band of generated reflectivity is reset to 0-1;
S22, geometric correction is carried out to from 1.5 grades of radar results of European Space Agency, and pixel is readjusted 12.5 meters
Size, to horizontal emission level receive HH and horizontal emission vertical reception HV digital quantization value (DN) be corrected respectively,
According to formulaBe converted to backscattering coefficient (σ0 HH、σ0 Hv);Then it applies
Enhanced Lee filter (3 × 3 size of Enhanced Lee filter, Lee 1980) removes spot or noise, exports σ0 HHWith
σ0 Hv, lay equal stress on and be amplified to 30m pixel for matching TM data;
The water-cloud model that S23, building vegetation water content (VWC) influence Radar backscattering coefficients:
L2=exp (- 2BV2sec(θi))
Wherein, σ0It is total backscattering coefficient (σ from Vegetation canopy and soil0 HH、σ0 Hv);σ0 vegIt is the backward of vegetation
Contribution of scatters, σ0 soilIt is the contribution of scatters of soil;L2It is two-way vegetation decaying;θiThe incidence angle of radar beam, A and B are vegetation
Parameter;V1And V2It is vegetation description, V1It is applicable in leaf area index LAI (m2m-2), V2It is applicable in volumetric water content of soil VWC (kgm-2);
S24, it takes:
LAI=0.091exp (3.7579GDVI2) (R2=0.932)
VWC=192.64NDVI5-417.46NDVI4+347.96NDVI3-138.93NDVI2+30.699NDVI-2.822
(kg·m-2)(R2=0.990);
A=0.0045, B=0.4179;
With 34.3 ° for θiThe incidence angle of radar beam calculates vegetation and removes backscattering coefficient (σ0 HH、σ0 Hv)。
S3, it plot will be surveyed by direct rasterizing is converted to grid and create training set (TS);
Using the point in ArcGIS to grid crossover tool, it is 30,60 that average field measurement figure, which is converted to raster unit,
With 90 meters of sizes, then resets and arrive 30m pixel, composition data collection;
S4, using above-mentioned training set (TS), using random forest return (RFR) algorithm modelling application in joint data set into
The prediction of row salinity.
S41, it is modeled using random forest regression algorithm RFR, using all 12 wave bands as input variable, is seen using 24
Preset value 100 of the measured value (training set (TS)) in EnMap-Box;
The square root of all features is chosen with the number of the randomly selected feature of each node or variable number;
Ending standard (be used for node split), wherein preset value is smallest sample number in node, 1, according to gini index meter
The minimum impurity of calculation, 0.
EM will be rasterizedVOr EMHAfter (EM38 is vertically read or horizontal reading) is TS (training set) parametrization, by generation
RFR model is applied to combined data set, to predict soil apparent salinity (Eca).
S5, the step of soil apparent salinity Eca is converted into soil conductivity ece, wherein ECe-EM38 reading with
(Eca) relationship between is expressed as follows:
ECe(dSm-1)=0.0005EMV 2-0.0779EMV+12.655(R2=0.850);
ECe(dSm-1)=0.0002EMH 2+0.0956EMH+0.0688(R2=0.791).
Specific embodiments of the present invention are described above.It is to be appreciated that the invention is not limited to above-mentioned
Particular implementation, those skilled in the art can make a variety of changes or modify within the scope of the claims, this not shadow
Ring substantive content of the invention.In the absence of conflict, the feature in embodiments herein and embodiment can any phase
Mutually combination.
Claims (6)
1. a kind of Soil salinity prediction technique based on machine learning regression algorithm, characterized by the following steps:
S1, using equilateral triangle as measuring point shape, using EM38 the earth conductivity gauge acquisition triangle three angle points actual measurement salt
Degree when measurement, reads vertical reading EMVEM is read with levelH, it is averaged the salinity as delta-shaped region, measures several
The EM of delta-shaped regionHAnd EMVFor basic truth training set (TS);
S2, soil constitution is obtained using the removal vegetation contribution of L-band Radar backscattering coefficients;
S3, it plot will be surveyed by direct rasterizing is converted to grid and create training set (TS);
S4, using above-mentioned training set (TS), (RFR) algorithm modelling application is returned using random forest and carries out salt in joint data set
Degree prediction.
2. a kind of Soil salinity prediction technique based on machine learning regression algorithm as described in claim 1, it is characterised in that:
In the step S1,15-20 meters of the side length of the equilateral triangle, it is ensured that triangle can be with one TM pixel of approximate representation;It surveys
Measure specification 1m × 1m of block.
3. a kind of Soil salinity prediction technique based on machine learning regression algorithm as described in claim 1, it is characterised in that:
The step S2 specifically comprises the following steps:
S21, the LANDSAT5TM image obtained from European Space Agency is calibrated with Radio Measurement, and eliminated using scattering method model
The each wave band of generated reflectivity is reset to 0-1 by additional atmospheric effect;
S22, geometric correction is carried out to the 1.5 grades of radar results obtained from European Space Agency, and pixel is readjusted 12.5
The size of rice, the digital quantization value for receiving HH and horizontal emission vertical reception HV to horizontal emission level are corrected respectively, press
According to formulaBe converted to backscattering coefficient (σ0 HH、σ0 Hv);Then application enhancing
Lee filter (the Enhanced Lee size of filter3 × 3, Lee 1980) removes spot or noise, exports σ0 HHAnd σ0 Hv, and
30m pixel is amplified to again to be used to match TM data;
The water-cloud model that S23, building vegetation water content (VWC) influence Radar backscattering coefficients:
L2=exp (- 2BV2sec(θi))
Wherein, σ0It is total backscattering coefficient (σ from Vegetation canopy and soil0 HH、σ0 Hv);σ0 vegIt is the back scattering of vegetation
Contribution, σ0 soilIt is the contribution of scatters of soil;L2It is two-way vegetation decaying;θiThe incidence angle of radar beam, A and B are vegetation parameters;
V1And V2It is vegetation description, V1It is applicable in leaf area index LAI (m2m-2), V2It is applicable in volumetric water content of soil VWC (kgm-2);
S24, it takes:
LAI=0.091exp (3.7579GDVI2) (R2=0.932)
VWC=192.64NDVI5-417.46NDVI4+347.96NDVI3-138.93NDVI2+30.699NDVI-2.822
(kg·m-2)(R2=0.990);
A=0.0045, B=0.4179;
With 34.3 ° for θiThe incidence angle of radar beam calculates vegetation and removes backscattering coefficient (σ0 HH、σ0 Hv)。
4. a kind of Soil salinity prediction technique based on machine learning regression algorithm as described in claim 1, it is characterised in that:
The step S3 specifically comprises the following steps:
Using the point in ArcGIS to grid crossover tool, it is 30,60 and 90 that average field measurement figure, which is converted to raster unit,
Then meter great little resets and arrives 30m pixel, composition data collection.
5. a kind of Soil salinity prediction technique based on machine learning regression algorithm as described in claim 1, it is characterised in that:
The step S4 specifically comprises the following steps:
S41, it is modeled using random forest regression algorithm RFR, using all 12 wave bands as input variable, is existed using observation
Preset value 100 in EnMap-Box;The flat of all features is chosen with the number of the randomly selected feature of each node or variable number
Root;Ending standard, be used for node split, wherein preset value be node in smallest sample number, 1, according to gini index calculate
Minimum impurity, 0;
EM will be rasterizedVOr EMHAfter TS (training set) parametrization, the RFR model of generation is applied to combined data set, is come pre-
It surveys soil apparent salinity (Eca).
6. a kind of Soil salinity prediction technique based on machine learning regression algorithm as described in claim 1, it is characterised in that:
Further include the steps that soil apparent salinity Eca being converted to soil conductivity ece, wherein between ECe-EM38 reading and (Eca)
Relationship be expressed as follows:
ECe(dSm-1)=0.0005EMV 2-0.0779EMV+12.655(R2=0.850);
ECe(dSm-1)=0.0002EMH 2+0.0956EMH+0.0688(R2=0.791).
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CN111879915A (en) * | 2020-08-04 | 2020-11-03 | 北京师范大学 | High-resolution monthly soil salinity monitoring method and system for coastal wetland |
CN112162016A (en) * | 2020-09-15 | 2021-01-01 | 塔里木大学 | Regional scale soil profile salinization detection method based on electromagnetic induction data |
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