CN115310550B - Atmospheric carbon dioxide dry air column concentration calculation method and system - Google Patents

Atmospheric carbon dioxide dry air column concentration calculation method and system Download PDF

Info

Publication number
CN115310550B
CN115310550B CN202210980540.5A CN202210980540A CN115310550B CN 115310550 B CN115310550 B CN 115310550B CN 202210980540 A CN202210980540 A CN 202210980540A CN 115310550 B CN115310550 B CN 115310550B
Authority
CN
China
Prior art keywords
data
xco
environment
covariate
oco
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
CN202210980540.5A
Other languages
Chinese (zh)
Other versions
CN115310550A (en
Inventor
陈玉敏
魏阳
常政威
张凌浩
徐厚东
唐伟
刘洪利
沈军
刘雪原
赵瑞祥
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.)
Electric Power Research Institute of State Grid Sichuan Electric Power Co Ltd
Original Assignee
Electric Power Research Institute of State Grid Sichuan Electric Power 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 Electric Power Research Institute of State Grid Sichuan Electric Power Co Ltd filed Critical Electric Power Research Institute of State Grid Sichuan Electric Power Co Ltd
Priority to CN202210980540.5A priority Critical patent/CN115310550B/en
Publication of CN115310550A publication Critical patent/CN115310550A/en
Application granted granted Critical
Publication of CN115310550B publication Critical patent/CN115310550B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • GPHYSICS
    • G06COMPUTING; CALCULATING OR COUNTING
    • G06FELECTRIC DIGITAL DATA PROCESSING
    • G06F17/00Digital computing or data processing equipment or methods, specially adapted for specific functions
    • G06F17/10Complex mathematical operations

Landscapes

  • Engineering & Computer Science (AREA)
  • Physics & Mathematics (AREA)
  • Theoretical Computer Science (AREA)
  • Mathematical Physics (AREA)
  • Data Mining & Analysis (AREA)
  • General Physics & Mathematics (AREA)
  • Mathematical Analysis (AREA)
  • Mathematical Optimization (AREA)
  • Computational Mathematics (AREA)
  • Pure & Applied Mathematics (AREA)
  • Databases & Information Systems (AREA)
  • Software Systems (AREA)
  • General Engineering & Computer Science (AREA)
  • Algebra (AREA)
  • Testing Or Calibration Of Command Recording Devices (AREA)

Abstract

The invention provides a method and a system for calculating the concentration of an atmospheric carbon dioxide dry air column, and relates to atmospheric carbon dioxide (CO) 2 ) The technical field of monitoring. The method comprises collecting XCO of three remote sensing monitoring in the research area 2 Preprocessing such as meshing, space-time matching and the like is performed on the data set and the environment covariate data; with environment covariates, for these three XCO 2 Fusing the data sets to obtain XCO 2 Fusing data; XCO is to be XCO 2 Fusing data as dependent variables, taking environment covariates as independent variables, and establishing a machine learning model based on an XGBoost algorithm; inputting environment covariate data into the XGBoost model, and calculating to obtain XCO 2 Is used for reconstructing the data set. The invention fuses three remote sensing monitoring XCO 2 Data set and reconstruction of XCO using machine learning model 2 Provides support for the carbon accounting of "two-carbon actions".

Description

Atmospheric carbon dioxide dry air column concentration calculation method and system
Technical Field
The invention relates to an atmospheric carbon dioxide dry air column concentration (XCO) 2 ) The technical field of monitoring, in particular to a method for detecting the position of a target objectMethod and system for calculating concentration of atmospheric carbon dioxide dry air column.
Background
Remote sensing monitoring using sensors mounted on satellites or space stations, is to obtain XCO 2 Important means of space-time distribution mainly include satellite orbital carbon observation No. 2 (OCO-2), greenhouse Gas Observation Satellite (GOSAT), and sensor orbital carbon observation No. 3 (OCO-3) mounted on international space stations. The OCO-2 and OCO-3 sensors are almost identical, and three high-resolution spectrometers are mounted to measure the reflected solar light spectra near 0.76,1.61, and 2.06 microns, respectively. GOSAT is equipped with a spectrometer for measuring the reflected solar spectrum at 0.76,1.61 and 2.06 microns, and also measures the reflected solar spectrum in the 5.56-14.3 micron band.
XCO for satellite monitoring 2 The method is relatively sparse in space, and the missing part can be filled by using a model simulation method. Current reconstruction full-field XCO 2 The method comprises the following steps of Carbon Tracker model simulation, and monitoring CO by using ground, airship, satellite and the like 2 Concentration, for bottom-up estimated atmospheric CO 2 The concentration is corrected. However, due to computer power limitations, the resulting XCO is simulated 2 The data resolution is low, typically only 3 ° x 2 ° on the global scale. At the same time, the method relies on carbon emission list, however, statistics, collection and correction of emission list data take a long time, thus leading to current XCO 2 There is some lag in the computation of the spatiotemporal distribution of the model simulation.
In recent years, studies have been made on the use of statistical methods in combination with satellite monitoring XCO 2 Data reconstruction XCO 2 Space-time distribution but due to XCO 2 The satellite monitoring data of (2) are distributed relatively sparsely in space, and XCO is obtained by using a Kriging interpolation method 2 Is relatively low. According to the previous research, the machine learning of the reconstructed air pollutant space-time distribution often has higher accuracy compared with the kriging interpolation. Reconstructing the atmospheric pollutants through machine learning modeling by utilizing the relevance between the atmospheric pollutants and environment covariates such as weather, altitude, land utilization type and the likeAnd (5) full-domain space-time distribution. Meanwhile, the machine learning method is often used for fusion application of homologous data, and can well make up for the limitation of a single data source.
The invention applies the machine learning method to a plurality of remote sensing monitoring XCO 2 Fusion of data sets and reconstruction of XCO 2 Is distributed in space-time in the whole domain, overcomes XCO 2 Monitoring has the problem of a large amount of missing data.
Disclosure of Invention
The invention aims to provide a method and a system for calculating the concentration of an atmospheric carbon dioxide dry air column, which are used for overcoming the problem in the prior art that XCO 2 Monitoring has the problem of a large amount of missing data.
In a first aspect, an embodiment of the present application provides a method for calculating a concentration of an atmospheric carbon dioxide dry air column, including the steps of:
collecting XCO monitored by three remote sensing in research area 2 The method comprises the steps of preprocessing a data set and environment covariate data;
XCO for three remote sensing monitoring 2 Fusing the data sets to obtain XCO 2 Fusing data;
by XCO 2 Fusing the data and the environment covariate data, and training to obtain an XGBoost model;
inputting environment covariate data into the XGBoost model, and calculating to obtain XCO 2 Is used for reconstructing the data set.
In the implementation process, XCO (X-ray diffraction) of three remote sensing monitoring in a research area is collected 2 Preprocessing the data set and the environment covariate data, and performing gridding, space-time matching and the like; XCO for three remote sensing monitoring 2 Fusing the data sets to obtain XCO 2 Fusing data; using XCO 2 Fusing the data and the environment covariate data, and training to obtain an XGBoost model; inputting environment covariate data into the XGBoost model, and calculating to obtain XCO 2 Is used for reconstructing the data set. XCO for three remote sensing monitoring 2 Data fusion with XCO 2 With weather, altitude, land use type, road density,Correlation among environment covariates such as vegetation normalization index and the like is calculated to obtain XCO through machine learning modeling 2 Is used for reconstructing a data set by comprehensive domain space-time distribution, and overcomes XCO 2 Monitoring has the problem of a large amount of missing data.
Based on the first aspect, in some embodiments of the invention, XCO for three telemetry monitors 2 Data fusion is carried out on the data set to obtain XCO 2 The procedure for fusing data was as follows:
input:
XCO of OCO-2 2 Monitor data a= { a 1 ,...,a j ,...,a J };
XCO of OCO-3 2 Monitor data b= { B 1 ,...,b j ,...,b J };
XCO of GOSAT 2 Monitor data c= { C 1 ,…,c j ,…,c J };
Environment covariate dataset D= { D 1 ,...,d j ,...,d J };
Note that: wherein d is j Representing the set of values of all environment covariates at j, but not the jth environment covariate. d, d j And a j 、b j C j Spatially and spatially correspond to each other, i.e. observations of three sensors on the same day, on the same grid. A is due to the different degree of deletion of OCO-2, OCO-3 and GOSAT data j 、b j C j There may be missing values but not at the same time.
And (3) outputting: fusion dataset e= { E 1 ,...,e j ,...,e J };
The method comprises the following steps:
(1) fusion A and B is O:
wherein o= { O 1 ,...,o j ,...,o J },o j =f 1 (a j ,b j ) Wherein a is j ,b j At least one of which is non-empty;
f 1 is a fusion function:
Figure BDA0003800256040000041
(2) linear transformation of GOSAT dataset C:
S={j|O j non-empty and C j Non-null };
M={c s |s∈S},N={o s |s∈S};
establishing a linear model f 3 :N←M;
Based on f 3 Transformation c j
J is from 1 to J:
when c j Non-empty and
Figure BDA0003800256040000042
c′ j =f 3 (c j );
the transformed dataset was C '= { C' 1 ,...,c′ j ,...,c′ J };
(3) Taking the union of the data set O and the data set C' to obtain the final XCO 2 The dataset E is fused.
Based on the first aspect, XCO is used in some embodiments of the invention 2 The steps of establishing the XGBoost model by fusing the data and the environment covariate data are as follows:
XCO is to be XCO 2 And (5) taking the fusion data as a dependent variable, taking an environment covariate as an independent variable, and training to obtain an XGBoost model.
Based on the first aspect, in some embodiments of the present invention, preprocessing environment covariate data of a study area includes the steps of:
carrying out space division on a research area to obtain a space grid with 1km resolution;
assigning values to the predefined grids by adopting methods such as space resampling and the like for the environment covariate data;
in a second aspect, embodiments of the present application provide an atmospheric carbon dioxide dry air column concentration calculation system, comprising:
the data acquisition module is used for collecting XCO (X-ray computer operation) monitored by three remote sensing in the research area 2 Data sets and environment covariate data;
data preprocessing module for XCO of three remote sensing monitoring in research area 2 The data set and the environment covariate data are subjected to preprocessing such as meshing, space-time matching and the like, and a preprocessed data set is obtained;
the data fusion module is used for XCO (X-ray computer operation) for three remote sensing monitoring 2 Data fusion is carried out on the data set to obtain XCO 2 Fusing the data sets;
XGBoost model building module for XCO-based 2 Training the fusion data and the environment covariate data to obtain an XGBoost model;
the concentration calculation module is used for inputting the environment covariate data into the XGBoost model to calculate and obtain XCO 2 Is used for reconstructing the data set.
In the implementation process, XCO (X-ray diffraction) of three remote sensing monitoring in a research area is collected 2 Preprocessing the data set and the environment covariate data, and performing gridding, space-time matching and the like; XCO for three remote sensing monitoring 2 Fusing the data sets to obtain XCO 2 Fusing data; using XCO 2 Fusing the data and the environment covariate data, and training to obtain an XGBoost model; inputting environment covariate data into the XGBoost model, and calculating to obtain XCO 2 Is used for reconstructing the data set. XCO for three remote sensing monitoring 2 Data fusion with XCO 2 Correlation with environment covariates such as meteorological, elevation, land utilization type, road density, vegetation normalization index and the like, and calculating to obtain XCO through machine learning modeling 2 Is used for reconstructing a data set by comprehensive domain space-time distribution, and overcomes XCO 2 Monitoring has the problem of a large amount of missing data.
The embodiment of the invention has at least the following advantages or beneficial effects:
the embodiment of the invention provides a method and a system for calculating the concentration of an atmospheric carbon dioxide dry air column, which are implemented by collecting three air columns in a research areaXCO for remote sensing monitoring 2 Preprocessing the data set and the environment covariate data, and performing gridding, space-time matching and the like; XCO for three remote sensing monitoring 2 Data fusion is carried out on the data set to obtain XCO 2 Fusing data; using XCO 2 Fusing the data and the environment covariate data, and training to obtain an XGBoost model; inputting the environment covariate number set into the XGBoost model, and calculating to obtain XCO 2 Is used for reconstructing the data set. XCO for three remote sensing monitoring 2 Data sets are fused while using XCO 2 Correlation with environment covariates such as weather, altitude, land utilization type, road density, vegetation normalization index and the like, and calculating to obtain XCO through machine learning modeling 2 Is used for reconstructing a data set by comprehensive domain space-time distribution, and overcomes XCO 2 Monitoring has the problem of a large amount of missing data.
Drawings
In order to more clearly illustrate the technical solutions of the embodiments of the present invention, the drawings that are needed in the embodiments will be briefly described below, it being understood that the following drawings only illustrate some embodiments of the present invention and therefore should not be considered as limiting the scope, and other related drawings may be obtained according to these drawings without inventive effort for a person skilled in the art.
FIG. 1 is a flow chart of a method for calculating the concentration of an atmospheric carbon dioxide dry air column provided by an embodiment of the invention;
FIG. 2 is a schematic diagram of a data fusion process according to an embodiment of the present invention;
FIG. 3 is a schematic diagram of the distribution of each remote sensing data and the spatial and temporal composition of the fused data according to an embodiment of the present invention;
fig. 4 is a block diagram of a system for calculating the concentration of an atmospheric carbon dioxide dry air column according to an embodiment of the present invention.
Icon: 110-a data acquisition module; 120-a data preprocessing module; 130-a data fusion module; 140-XGBoost model building module; 150-concentration calculation module.
Detailed Description
For the purposes of making the objects, technical solutions and advantages of the embodiments of the present application more clear, the technical solutions of the embodiments of the present application will be clearly and completely described below with reference to the drawings in the embodiments of the present application, and it is apparent that the described embodiments are some embodiments of the present application, but not all embodiments. The components of the embodiments of the present application, which are generally described and illustrated in the figures herein, may be arranged and designed in a wide variety of different configurations.
Thus, the following detailed description of the embodiments of the present application, as provided in the accompanying drawings, is not intended to limit the scope of the application, as claimed, but is merely representative of selected embodiments of the application. All other embodiments, which can be made by one of ordinary skill in the art based on the embodiments herein without making any inventive effort, are intended to be within the scope of the present application.
Examples
Some embodiments of the present application are described in detail below with reference to the accompanying drawings. The various embodiments and features of the embodiments described below may be combined with one another without conflict.
Referring to fig. 1-2, fig. 1 is a flowchart of a method for calculating a dry air column concentration of atmospheric carbon dioxide according to an embodiment of the present invention, and fig. 2 is a schematic diagram of a data fusion process according to an embodiment of the present invention. The method for calculating the concentration of the atmospheric carbon dioxide dry air column comprises the following steps:
step S110: collecting remote sensing monitoring XCO in research area 2 Data and environment covariate data. The XCO described above 2 The data comprises three remote sensing monitored XCO 2 Data set comprising XCO from satellite orbital carbon observation No. 2 (OCO-2) 2 Data, XCO from a greenhouse Gas Observation Satellite (GOSAT) 2 Data, and XCO from sensor orbital carbon observation No. 3 (OCO-3) mounted on international space station 2 Data. The data sets include weather, population density, planet boundary layer height, land utilization type, normalized vegetation index, altitude, road information, etc. Wherein the meteorological data comes from the European middle weather forecast center, and the land use type data comes from the European space agencyThe climate change institute, the elevation data comes from the space plane radar topography mission, and the population density data comes from the gridded world population.
The environmental covariate data of the study area is preprocessed. The preprocessing is to process environment covariate data into a predefined 1km grid through a gridding method, a space-time matching method and the like for training and calculating a machine learning model, wherein the data set usually comprises tens to hundreds of variables. The method specifically comprises the following steps:
firstly, space division is carried out on a research area, and a space grid with 1km resolution is obtained.
And then, assigning the environment covariate data to a predefined 1km grid by adopting methods such as meshing, space-time matching and the like to obtain a preprocessed environment covariate data set.
Step S120: XCO for three remote sensing monitoring 2 Data fusion is carried out on the data set to obtain XCO 2 The data are fused, and the steps are as follows:
input:
XCO of OCO-2 2 Monitor data a= { a 1 ,...,a j ,...,a J };
XCO of OCO-3 2 Monitor data b= { B 1 ,...,b j ,...,b J };
XCO of GOSAT 2 Monitor data c= { C 1 ,…,c j ,…,c J };
Environment covariate dataset D= { D 1 ,...,d j ,...,d J };
Note that: wherein d is j Representing the set of values of all environment covariates at j, but not the jth environment covariate. d, d j And a j 、b j C j Spatially and spatially correspond to each other, i.e. observations of three sensors on the same day, on the same grid. A is due to the different degree of deletion of OCO-2, OCO-3 and GOSAT data j 、b j C j There may be missing values but not at the same time.
And (3) outputting: fusion dataset e= { E 1 ,...,e j ,...,e J };
The method comprises the following steps:
(1) fusion A and B is O:
wherein o= { O 1 ,...,o j ,...,o J },o j =f 1 (a j ,b j ) Wherein a is j ,b j At least one of which is non-empty;
f 1 is a fusion function:
Figure BDA0003800256040000091
(2) linear transformation of GOSAT dataset C:
S={j|O j non-empty and C j Non-null };
M={c s |s∈S},N={o s |s∈S};
establishing a linear model f 3 :N←M;
Based on f 3 Transformation c j
J is from 1 to J:
when c j Non-empty and
Figure BDA0003800256040000092
c′ j =f 3 (c j );
the transformed dataset was C '= { C' 1 ,...,c′ j ,...,c′ J };
(3) Taking the union of the data set O and the data set C' to obtain the final XCO 2 The dataset E is fused.
Step S130: using XCO 2 Fusing data as dependent variables, taking environment covariates as independent variables, and training to obtain a machine learning model based on an XGBoost algorithm;
step S140: inputting environment covariate data into the XGBoost model, and calculating to obtain XCO 2 Is used for reconstructing the data set.
In the implementation process, XCO (X-ray diffraction) of three remote sensing monitoring in a research area is collected 2 Preprocessing the data set and the environment covariate data, and performing gridding, space-time matching and the like; XCO for three remote sensing monitoring 2 Fusing the data sets to obtain XCO 2 Fusing data; using XCO 2 Fusing the data and the environment covariate data, and training to obtain an XGBoost model; inputting environment covariate data into the XGBoost model, and calculating to obtain XCO 2 Is used for reconstructing the data set. XCO for three remote sensing monitoring 2 Data sets are fused while using XCO 2 Correlation with environment covariates such as weather, altitude, land utilization type, road density, vegetation normalization index and the like, and calculating to obtain XCO through machine learning modeling 2 Is used for reconstructing the data set.
Referring to fig. 3, fig. 3 is a schematic diagram of a data fusion process according to an embodiment of the present invention, where a horizontal axis represents space and a vertical axis represents time. In the schematic, c=g+s represents XCO for GOSAT monitoring 2 The data set has data in the whole time interval P; o=t+s represents XCO monitored by OCO (OCO-2 and OCO-3) 2 Data set, only in time interval P 1 There is data. At P 1 XCO for GOSAT monitoring in time interval 2 XCO for monitoring with OCO 2 There is a distribution of data points. Due to the orbits of satellites and space stations, unfavorable meteorological conditions and the like, the satellite data of the daily scale is spatially missing, and the OCO is monitored by XCO 2 Covering only the O space-time interval, while GOSAT-monitored XCO 2 In the P period, only the space-time section C is covered, and the space-time section S is the portion where the two sections overlap in space. And (3) performing linear fitting on the GOSAT monitoring value and the OCO monitoring value in the S space-time interval, taking the GOSAT monitoring value as an independent variable and taking the OCO monitoring value as an independent variable, and establishing a linear model. Converting GOSAT monitoring value of G part into OCO monitoring value by using the linear model, so that the OCO monitoring value approximately covers G space interval, and the time interval covers the whole P period to realize multiple XCOs 2 Fusion of the data was monitored.
Based on the same inventive concept, the invention also provides an atmospheric carbon dioxide dry air column concentration calculating system, referring to fig. 4, and fig. 4 is a block diagram of an atmospheric carbon dioxide dry air column concentration calculating system according to an embodiment of the invention. The atmospheric carbon dioxide dry air column concentration calculation system comprises:
a data acquisition module 110 for collecting XCO for three remote sensing monitoring in the investigation region 2 Data sets and environment covariate data;
a data preprocessing module 120 for preprocessing XCO in the investigation region 2 Preprocessing the data and environment covariate data to obtain preprocessed XCO 2 A data set and an environment covariate data set;
XGBoost model building module 140 for XCO-based 2 Establishing an XGBoost model by fusing the data and the environment covariate data;
a concentration calculation module 150 for inputting the environment covariate data into the XGBoost model, and calculating to obtain XCO 2 Is used for reconstructing the data set.
In the implementation process, XCO (X-ray diffraction) of three remote sensing monitoring in a research area is collected 2 Preprocessing the data set and the environment covariate data, and performing gridding, space-time matching and the like; XCO for three remote sensing monitoring 2 Fusing the data sets to obtain XCO 2 Fusing data; using XCO 2 Fusing the data and the environment covariate data, and training to obtain an XGBoost model; inputting environment covariate data into the XGBoost model, and calculating to obtain XCO 2 Is used for reconstructing the data set. XCO for three remote sensing monitoring 2 Data fusion with XCO 2 Correlation with environment covariates such as weather, altitude, land utilization type, road density, vegetation normalization index and the like, and calculating to obtain XCO through machine learning modeling 2 Is used for reconstructing the data set.
The foregoing description is only of the preferred embodiments of the present application and is not intended to limit the same, but rather, various modifications and variations may be made by those skilled in the art. Any modification, equivalent replacement, improvement, etc. made within the spirit and principles of the present application should be included in the protection scope of the present application.
It will be evident to those skilled in the art that the present application is not limited to the details of the foregoing illustrative embodiments, and that the present application may be embodied in other specific forms without departing from the spirit or essential characteristics thereof. The present embodiments are, therefore, to be considered in all respects as illustrative and not restrictive, the scope of the application being indicated by the appended claims rather than by the foregoing description, and all changes which come within the meaning and range of equivalency of the claims are therefore intended to be embraced therein. Any reference sign in a claim should not be construed as limiting the claim concerned.

Claims (4)

1. The method for calculating the concentration of the atmospheric carbon dioxide dry air column is characterized by comprising the following steps of:
collecting XCO monitored by three remote sensing in research area 2 The method comprises the steps of preprocessing a data set and environment covariate data in an area; the XCO 2 The data set comprises OCO-2, OCO-3 and GOSAT;
XCO for three remote sensing monitoring 2 Fusing the data sets to obtain XCO 2 Fusing the data sets, comprising: input:
XCO of OCO-2 2 Monitor data a= { a 1 ,...,a j ,...,a J };
XCO of OCO-3 2 Monitor data b= { B 1 ,...,b j ,...,b J };
XCO of GOSAT 2 Monitor data c= { C 1 ,...,c j ,...,c J };
Environment covariate dataset D= { D 1 ,...,d j ,...,d J };
Wherein d is j Representing the set of values of all environment covariates at j, but not the jth environment covariate, d j And a j 、b j C j In space-timeAre mutually corresponding, namely, the observation values of three sensors on the same day and same grid; a is due to the different degree of deletion of OCO-2, OCO-3 and GOSAT data j 、b j C j There is a possibility that missing values are present, but not at the same time;
and (3) outputting: fusion dataset e= { E 1 ,...,e j ,...,e J };
The method comprises the following steps:
(1) fusion A and B is O:
wherein o= { O 1 ,...,o j ,...,o J },o j =f 1 (a j ,b j ) Wherein a is j ,b j At least one of which is non-empty;
f 1 is a fusion function:
Figure FDA0004279740850000021
(2) linear transformation of GOSAT dataset C:
S={j|o j non-empty and c j Non-null };
M={c s |s∈S},N={o s |s∈S};
establishing a linear model f 3 : N≡M; establishing a linear model by taking a GOSAT monitoring value as an independent variable and an OCO monitoring value as a dependent variable;
based on f 3 Transformation c j
J is from 1 to J:
when c j Non-empty and
Figure FDA0004279740850000022
c′ j =f 3 (c j )
the transformed dataset was C '= { C' 1 ,...,c′ j ,...,c′ J }
(3) Taking the union of the data set O and the data set C' to obtain the final XCO 2 Fusing the data set E;
using XCO 2 Fusing data as dependent variables, taking environment covariates as independent variables, and training to obtain a machine learning model based on an XGBoost algorithm;
inputting environment covariate data into the XGBoost model, and calculating to obtain XCO 2 Is used for reconstructing the data set.
2. The method for calculating the concentration of dry air column of atmospheric carbon dioxide according to claim 1, wherein XCO is used 2 The steps of establishing the XGBoost model by fusing the data and the environment covariates are as follows:
XCO is to be XCO 2 And (5) taking the fusion data as a dependent variable, taking an environment covariate as an independent variable, and training to obtain an XGBoost model.
3. The method for calculating the concentration of the atmospheric carbon dioxide dry air column according to claim 1, which is characterized by comprising the following steps of:
carrying out space division on a research area to obtain a space grid with 1km resolution;
and (3) adopting a spatial resampling method to the environment covariate data, and assigning values to a predefined grid.
4. An atmospheric carbon dioxide dry air column concentration calculation system, characterized by comprising:
the data acquisition module is used for collecting XCO (X-ray computer operation) monitored by three remote sensing in the research area 2 Data sets and environment covariate data; the XCO 2 The data set comprises OCO-2, OCO-3 and GOSAT;
data preprocessing module for XCO of three remote sensing monitoring in research area 2 The data set and the environment covariate data are subjected to preprocessing such as meshing, space-time matching and the like, and a preprocessed data set is obtained;
the data fusion module is used for XCO (X-ray computer operation) for three remote sensing monitoring 2 Data fusion is carried out on the data set to obtain XCO 2 Fusing the data sets, comprising: input:
XCO of OCO-2 2 Monitor data a= { a 1 ,...,a j ,...,a J };
XCO of OCO-3 2 Monitor data b= { B 1 ,...,b j ,...,b J };
XCO of GOSAT 2 Monitor data c= { C 1 ,...,c j ,...,c J };
Environment covariate dataset D= { D 1 ,...,d j ,...,d J };
Wherein d is j Representing the set of values of all environment covariates at j, but not the jth environment covariate, d j And a j 、b j C j The three sensors are corresponding to each other in time and space, namely, the three sensors observe the same grid on the same day; a is due to the different degree of deletion of OCO-2, OCO-3 and GOSAT data j 、b j C j There is a possibility that missing values are present, but not at the same time;
and (3) outputting: fusion dataset e= { E 1 ,...,e j ,...,e J };
The method comprises the following steps:
(1) fusion A and B is O:
wherein o= { O 1 ,...,o j ,...,o J },o j =f 1 (a j ,b j ) Wherein a is j ,b j At least one of which is non-empty;
f 1 is a fusion function:
Figure FDA0004279740850000041
(2) linear transformation of GOSAT dataset C:
S={j|o j non-empty and c j Non-null };
M={c s |s∈S},N={o s |s∈S};
establishing a linear model f 3 : N≡M; establishing a linear model by taking a GOSAT monitoring value as an independent variable and an OCO monitoring value as a dependent variable;
based on f 3 Transformation c j
J is from 1 to J:
when c j Non-empty and
Figure FDA0004279740850000042
c′ j =f 3 (c j )
the transformed dataset was C '= { C' 1 ,...,c′ j ,...,c′ J }
(3) Taking the union of the data set O and the data set C' to obtain the final XCO 2 Fusing the data set E;
XGBoost model building module for XCO-based 2 Training the fusion data and the environment covariate data to obtain an XGBoost model;
the concentration calculation module is used for inputting the environment covariate data into the XGBoost model to calculate and obtain XCO 2 Is used for reconstructing the data set.
CN202210980540.5A 2022-08-16 2022-08-16 Atmospheric carbon dioxide dry air column concentration calculation method and system Active CN115310550B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202210980540.5A CN115310550B (en) 2022-08-16 2022-08-16 Atmospheric carbon dioxide dry air column concentration calculation method and system

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202210980540.5A CN115310550B (en) 2022-08-16 2022-08-16 Atmospheric carbon dioxide dry air column concentration calculation method and system

Publications (2)

Publication Number Publication Date
CN115310550A CN115310550A (en) 2022-11-08
CN115310550B true CN115310550B (en) 2023-07-14

Family

ID=83862862

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202210980540.5A Active CN115310550B (en) 2022-08-16 2022-08-16 Atmospheric carbon dioxide dry air column concentration calculation method and system

Country Status (1)

Country Link
CN (1) CN115310550B (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN116882261B (en) * 2023-05-30 2024-08-09 中国矿业大学 Atmospheric XCO integrating land surface environment variables2Concentration refinement inversion method
CN117556953B (en) * 2023-11-21 2024-08-06 中国气象局沈阳大气环境研究所 Automatic processing and predicting system based on satellite remote sensing inversion data
CN117574155A (en) * 2023-11-29 2024-02-20 海南省气象科学研究所 Prediction method for near-ground atmospheric carbon dioxide concentration in sea area based on satellite remote sensing

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112884079A (en) * 2021-03-30 2021-06-01 河南大学 Method for estimating near-surface nitrogen dioxide concentration based on Stacking integrated model
CN114861882A (en) * 2022-05-07 2022-08-05 国网四川省电力公司电力科学研究院 CO (carbon monoxide) 2 Space-time distribution reconstruction method and system

Family Cites Families (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR2827200B1 (en) * 2001-07-12 2003-09-12 Usinor METHOD AND DEVICE FOR CONTINUOUSLY COATING A STRIP WITH A FLUID FILM OF PREDETERMINED THICKNESS IN CROSSLINKABLE POLYMER FREE OF SOLVENT OR DILUENT
AU2015201877B2 (en) * 2006-05-31 2016-08-25 TRX Systems, Inc, Method and system for locating and monitoring first responders
FR2953021B1 (en) * 2009-11-26 2011-12-09 Tanguy Griffon METHOD FOR MEASURING WEEKLY AND ANNUAL EMISSIONS OF A GREENHOUSE GAS ON A DATA SURFACE
CN109716128B (en) * 2016-12-06 2022-05-10 曾宁 Networked environment monitoring system, method and computer readable storage medium
CN111893237B (en) * 2020-07-08 2021-11-09 北京科技大学 Method for predicting carbon content and temperature of molten pool of converter steelmaking in whole process in real time
CN113297527B (en) * 2021-06-09 2022-07-26 四川大学 PM based on multisource city big data 2.5 Overall domain space-time calculation inference method
CN113297528B (en) * 2021-06-10 2022-07-01 四川大学 NO based on multi-source big data2High-resolution space-time distribution calculation method
CN113435511A (en) * 2021-06-28 2021-09-24 中国科学院地理科学与资源研究所 XCO based on HASM2Data fusion method and system

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112884079A (en) * 2021-03-30 2021-06-01 河南大学 Method for estimating near-surface nitrogen dioxide concentration based on Stacking integrated model
CN114861882A (en) * 2022-05-07 2022-08-05 国网四川省电力公司电力科学研究院 CO (carbon monoxide) 2 Space-time distribution reconstruction method and system

Also Published As

Publication number Publication date
CN115310550A (en) 2022-11-08

Similar Documents

Publication Publication Date Title
CN115310550B (en) Atmospheric carbon dioxide dry air column concentration calculation method and system
CN113297527B (en) PM based on multisource city big data 2.5 Overall domain space-time calculation inference method
Michel et al. The WACMOS-ET project–Part 1: Tower-scale evaluation of four remote-sensing-based evapotranspiration algorithms
CN113297528B (en) NO based on multi-source big data2High-resolution space-time distribution calculation method
Yang et al. Geographical and temporal encoding for improving the estimation of PM2. 5 concentrations in China using end-to-end gradient boosting
CN112884079A (en) Method for estimating near-surface nitrogen dioxide concentration based on Stacking integrated model
De Wachter et al. Retrieval of MetOp-A/IASI CO profiles and validation with MOZAIC data
Yang et al. Investigation of the spatially varying relationships of PM2. 5 with meteorology, topography, and emissions over China in 2015 by using modified geographically weighted regression
Wei et al. Spatial–temporal variations of NDVI and its response to climate in China from 2001 to 2020
Song et al. Long-term record of top-of-atmosphere albedo over land generated from AVHRR data
Jin et al. Global validation and hybrid calibration of CAMS and MERRA-2 PM2. 5 reanalysis products based on OpenAQ platform
CN111652404A (en) All-weather earth surface temperature inversion method and system
Bai et al. Multiscale and multisource data fusion for full-coverage PM2. 5 concentration mapping: Can spatial pattern recognition come with modeling accuracy?
Liu et al. Prediction of PM2. 5 concentrations at unsampled points using multiscale geographically and temporally weighted regression
Chen et al. High spatiotemporal resolution estimation of AOD from Himawari-8 using an ensemble machine learning gap-filling method
Flückiger et al. Modelling daily air temperature at a fine spatial resolution dealing with challenging meteorological phenomena and topography in Switzerland
Pereira et al. Solar irradiance modelling using an offline coupling procedure for the Weather Research and Forecasting (WRF) model
Wei et al. Extending the EOS long-term PM 2.5 data records since 2013 in China: Application to the VIIRS deep blue aerosol products
Yu et al. Surface downward longwave radiation estimation from new generation geostationary satellite data
Jing et al. Estimating PM2. 5 concentrations in a central region of China using a three-stage model
He et al. Seamless reconstruction and spatiotemporal analysis of satellite-based XCO2 incorporating temporal characteristics: A case study in China during 2015–2020
Chen et al. High-spatiotemporal-resolution estimation of solar energy component in the United States using a new satellite-based model
Huang et al. PM2. 5 concentration estimation with 1-km resolution at high coverage over urban agglomerations in China using the BPNN-KED approach and potential application
CN115267066A (en) Fossil fuel carbon dioxide emission calculation method based on satellite observation of concentration of pollution gas
CN116188705A (en) Reconstruction method for kilometer-level resolution stereo distribution of regional atmospheric pollutants

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
GR01 Patent grant
GR01 Patent grant