CN114118785A - Urban cell carbon neutralization amount calculation method - Google Patents
Urban cell carbon neutralization amount calculation method Download PDFInfo
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Abstract
The invention discloses a carbon neutralization amount calculation method for an urban cell, relates to the technical field of carbon neutralization amount calculation, and solves the technical problem that in the prior art, the calculation error of the carbon neutralization amount is large because the same-grade emission and emission reduction can not be accurately matched for the cell; according to the invention, by collecting the carbon emission of the cell, the detection efficiency of the cell corresponding to the carbon emission is effectively improved, the pertinence of the carbon emission control is improved, and the carbon emission control efficiency is increased; the energy-saving emission-reducing process corresponding to the cell is graded, so that the situation that the carbon neutralization value is low due to the fact that the energy-saving emission-reducing process is not matched with the carbon emission of the corresponding cell, the carbon emission exceeds the standard, the content of greenhouse effect gas in the environment is increased, and the environment is damaged is prevented; comparing the energy-saving emission-reduction grade of the cell with the emission grade; the carbon neutralization efficiency is prevented from being reduced due to unnecessary errors caused by carbon neutralization amount due to the fact that the carbon emission grade of the cell is not matched with the energy-saving emission reduction grade.
Description
Technical Field
The invention relates to the technical field of carbon neutralization amount calculation, in particular to a method for calculating carbon neutralization amount of an urban community.
Background
Carbon neutralization means that enterprises, groups or individuals measure and calculate the total amount of greenhouse gas emission generated directly or indirectly within a certain time, and the emission amount of carbon dioxide generated by the enterprises, the groups or the individuals is offset through the forms of afforestation, energy conservation, emission reduction and the like, so that zero emission of the carbon dioxide is realized; it is meant that a neutral (i.e., zero) total carbon amount is released and equilibrium is achieved by taking more or less countermeasures with respect to how much carbon is discharged.
However, in the prior art, accurate emission analysis and emission reduction analysis cannot be performed on cells, so that the matching accuracy of emission and emission reduction of each cell is low, the carbon neutralization amount is inaccurate, and the greenhouse effect gas is excessively emitted; meanwhile, emission reduction cost cannot be controlled, and although gas emission can be controlled, investment cost cannot be controlled.
Disclosure of Invention
Aiming at the defects in the prior art, the invention provides a method for calculating the carbon neutralization amount of an urban cell, which effectively improves the detection efficiency of the carbon emission amount corresponding to the cell and the pertinence of the carbon emission amount control by collecting the carbon emission amount of the cell, so that the carbon emission control efficiency is increased; the energy-saving emission-reducing process corresponding to the cell is graded, so that the situation that the carbon neutralization value is low due to the fact that the energy-saving emission-reducing process is not matched with the carbon emission of the corresponding cell, the carbon emission exceeds the standard, the content of greenhouse effect gas in the environment is increased, and the environment is damaged is prevented; comparing the energy-saving emission-reduction grade of the cell with the emission grade; the carbon neutralization efficiency reduction caused by unnecessary errors brought by carbon neutralization due to mismatching of the carbon emission grade of the cell and the energy-saving emission reduction grade is avoided, the matching detection of the cell emission grade and the energy-saving emission reduction grade is verified, and the carbon neutralization efficiency reduction caused by abnormal matching detection is prevented.
The invention discloses a method for calculating carbon neutralization amount of an urban community, which comprises the following steps:
step 1, emission analysis: analyzing the carbon emission of the cell, and grading the carbon emission of the cell according to the analysis result;
step 2, emission reduction analysis: analyzing the corresponding processes of energy conservation and emission reduction of the cell, and grading the processes of energy conservation and emission reduction of the cell according to the analysis result;
step 3, grade comparison: comparing the energy saving and emission reduction grade of the cell with the carbon emission grade of the cell;
step 4, quantitative verification: carrying out quantitative analysis on the carbon emission of the cell, and judging the carbon neutralization value; and detecting the carbon neutralization value, and verifying the matching detection of the carbon emission grade and the energy-saving emission-reducing grade of the cell.
As a further improvement of the present invention, the step 1 specifically includes:
step 11, marking the cell subjected to carbon emission analysis as a detection cell, and setting a mark i which is a natural number greater than 1;
step 12, setting detection time, collecting the total carbon emission amount of the detection cell within the detection time, and marking the total carbon emission amount of the detection cell within the detection time as TPi;
acquiring the increase speed of the carbon emission corresponding to the detection cell in the detection time, and marking the increase speed of the carbon emission corresponding to the detection cell in the detection time as SDi;
collecting the type of the exhaust gas corresponding to the carbon emission of the detection cell in the detection time, and marking the type of the exhaust gas corresponding to the carbon emission of the detection cell in the detection time as ZLi;
step 13, acquiring a carbon emission analysis coefficient Xi of each detection cell through a carbon emission analysis formula, and comparing the carbon emission analysis coefficient of each detection cell with L1 and L2;
wherein L1 and L2 are both carbon emission analysis coefficient threshold values, and L1 is more than L2;
if the carbon emission analysis coefficient of the detection cell is larger than or equal to L1, marking the corresponding detection cell as a primary emission cell, and marking the corresponding carbon emission analysis coefficient as a primary emission coefficient;
if the carbon emission analysis coefficient of the detection cell is less than or equal to L2 and less than L1, marking the corresponding detection cell as a secondary emission cell, and marking the corresponding carbon emission analysis coefficient as a secondary emission coefficient;
and if the carbon emission analysis coefficient of the detection cell is less than L2, marking the corresponding detection cell as a tertiary emission cell, and marking the corresponding carbon emission analysis coefficient as a tertiary emission coefficient.
As a further improvement of the present invention, the carbon emission analysis formula is:
Xi=β(TPi×a1+SDi×a2+ZLi×a3)
in the formula, a1, a2 and a3 are all preset proportionality coefficients, and the values of a1, a2 and a3 are 0.71, 0.76 and 0.84 respectively; beta is an error correction factor and takes a value of 1.02.
As a further improvement of the present invention, the step 2 specifically includes:
step 21, collecting the number of energy-saving and emission-reducing processes of each detection cell and the average running time of the corresponding processes, and respectively marking the number of energy-saving and emission-reducing processes of each detection cell and the average running time of the corresponding processes as GSLi and GSCi;
step 22, collecting green planting areas and green planting frequencies in all detection cells, and respectively marking the green planting areas and the green planting frequencies in all the detection cells as LMJi and ZPLI;
step 23, obtaining emission reduction analysis coefficients Zi of each detection cell through an emission reduction analysis formula, and comparing the emission reduction analysis coefficients Zi of each detection cell with an emission reduction analysis coefficient threshold range;
if the emission reduction analysis coefficient Zi of the detection cell is larger than the emission reduction analysis coefficient threshold range, marking the corresponding detection cell as a primary emission reduction cell, and marking the corresponding emission reduction analysis coefficient as a primary emission reduction coefficient;
if the emission reduction analysis coefficient Zi of the detection cell is within the emission reduction analysis coefficient threshold range, marking the corresponding detection cell as a secondary emission reduction cell, and marking the corresponding emission reduction analysis coefficient as a secondary emission reduction coefficient;
if the emission reduction analysis coefficient Zi of the detection cell is smaller than the emission reduction analysis coefficient threshold range, marking the corresponding detection cell as a third-level emission reduction cell, and marking the corresponding emission reduction analysis coefficient as a third-level emission reduction coefficient.
As a further improvement of the present invention, the emission reduction analysis formula is:
in the formula, b1, b2, b3 and b4 are all preset proportionality coefficients, and b1 is more than b2 and more than b3 is more than b4 and more than 0.
As a further improvement of the present invention, the step 3 specifically includes:
step 31, comparing the emission coefficient of each detection cell with the emission reduction coefficient corresponding grade, if the emission coefficient grade of the detection cell is greater than the emission reduction coefficient grade, judging that the carbon neutralization of the corresponding detection cell does not reach the standard, and marking the corresponding detection cell as a carbon neutralization non-standard cell;
step 32, if the emission coefficient grade of the detection cell is smaller than the emission reduction coefficient grade, judging that the carbon neutralization of the corresponding detection cell reaches the standard, and marking the corresponding detection cell as a carbon neutralization standard cell;
and step 33, if the emission coefficient grade of the detection cell is equal to the emission reduction coefficient grade, judging that the carbon neutralization cost of the corresponding detection cell is unqualified, and marking the corresponding detection cell as a cell with unqualified carbon neutralization cost.
As a further improvement of the present invention, the step 4 specifically includes:
step 41, carrying out quantitative analysis on the carbon neutralization standard-reaching cell, collecting the carbon emission of the detection cell, and marking the carbon emission as the initial emission;
if the initial discharge amount is larger than the corresponding discharge amount threshold value, judging that the initial discharge amount exceeds the standard;
if the initial discharge amount is smaller than the corresponding discharge amount threshold value, judging that the initial discharge amount does not exceed the standard;
step 42, collecting the carbon emission of the detected cell after the energy-saving emission-reduction process, and marking the carbon emission as the rear end emission;
if the rear end discharge amount is larger than the corresponding discharge amount threshold value, judging that the rear end discharge amount exceeds the standard, collecting a difference value between the initial discharge amount and the rear end discharge amount, and if the difference value is larger than the corresponding difference value threshold value, generating a mismatching signal;
if the difference value is smaller than the corresponding difference value threshold value, generating an emission reduction abnormal signal;
and if the rear tail emission is smaller than the corresponding emission threshold, judging that the rear tail emission does not exceed the standard, and generating a normal emission reduction signal.
Compared with the prior art, the invention has the beneficial effects that:
according to the invention, by collecting the carbon emission of the cell, the detection efficiency of the cell corresponding to the carbon emission is effectively improved, the pertinence of the carbon emission control is enhanced, and the carbon emission control efficiency is increased;
according to the invention, the energy-saving emission reduction process corresponding to the cell is graded, so that the situation that the carbon neutralization quantity is low due to mismatching of energy-saving emission reduction and the carbon emission quantity of the corresponding cell, the carbon emission quantity exceeds the standard, the content of greenhouse effect gas in the environment is increased, and the environment is harmed is prevented;
the invention compares the energy-saving emission-reducing grade of the cell with the emission grade; the carbon neutralization efficiency reduction caused by unnecessary errors brought by carbon neutralization due to mismatching of the carbon emission grade of the cell and the energy-saving emission reduction grade is avoided, the matching detection of the cell emission grade and the energy-saving emission reduction grade is verified, and the carbon neutralization efficiency reduction caused by abnormal matching detection is prevented.
Drawings
Fig. 1 is a flowchart of a method for calculating carbon neutralization amount of an urban cell according to the present invention.
Detailed Description
In order to make the objects, technical solutions and advantages of the embodiments of the present invention clearer, the technical solutions in the embodiments of the present invention will be clearly and completely described below with reference to the drawings in the embodiments of the present invention, and it is obvious that the described embodiments are some, but not all, embodiments of the present invention. All other embodiments, which can be obtained by a person skilled in the art without any inventive step based on the embodiments of the present invention, are within the scope of the present invention.
In the description of the present invention, it should be noted that the terms "center", "upper", "lower", "left", "right", "vertical", "horizontal", "inner", "outer", etc., indicate orientations or positional relationships based on the orientations or positional relationships shown in the drawings, and are only for convenience of description and simplicity of description, but do not indicate or imply that the device or element being referred to must have a particular orientation, be constructed and operated in a particular orientation, and thus, should not be construed as limiting the present invention. Furthermore, the terms "first," "second," and "third" are used for descriptive purposes only and are not to be construed as indicating or implying relative importance.
In the description of the present invention, it should also be noted that, unless otherwise explicitly specified or limited, the terms "mounted," "connected," and "connected" are to be construed broadly, e.g., as meaning either a fixed connection, a removable connection, or an integral connection; can be mechanically or electrically connected; they may be connected directly or indirectly through intervening media, or they may be interconnected between two elements. The specific meanings of the above terms in the present invention can be understood in specific cases to those skilled in the art.
The invention is described in further detail below with reference to the attached drawing figures:
as shown in fig. 1, the invention discloses a method for calculating carbon neutralization amount of an urban cell, comprising the following steps:
step 1, emission analysis: the carbon emission of the cell is analyzed, and the carbon emission of the cell is graded according to the analysis result, so that the detection efficiency of the carbon emission corresponding to the cell is effectively improved by collecting the carbon emission of the cell, the pertinence of the carbon emission control is improved, and the carbon emission control efficiency is increased;
wherein, step 1 specifically includes:
step 11, marking the cell subjected to carbon emission analysis as a detection cell, and setting a mark i which is a natural number greater than 1;
step 12, setting detection time, collecting the total carbon emission amount of the detection cell within the detection time, and marking the total carbon emission amount of the detection cell within the detection time as TPi;
acquiring the increase speed of the carbon emission corresponding to the detection cell in the detection time, and marking the increase speed of the carbon emission corresponding to the detection cell in the detection time as SDi;
collecting the type of the exhaust gas corresponding to the carbon emission of the detection cell in the detection time, and marking the type of the exhaust gas corresponding to the carbon emission of the detection cell in the detection time as ZLi;
step 13, acquiring a carbon emission analysis coefficient Xi of each detection cell through a carbon emission analysis formula, and comparing the carbon emission analysis coefficient of each detection cell with L1 and L2;
wherein L1 and L2 are both carbon emission analysis coefficient threshold values, and L1 is more than L2;
if the carbon emission analysis coefficient of the detection cell is larger than or equal to L1, marking the corresponding detection cell as a primary emission cell, and marking the corresponding carbon emission analysis coefficient as a primary emission coefficient;
if the carbon emission analysis coefficient of the detection cell is less than or equal to L2 and less than L1, marking the corresponding detection cell as a secondary emission cell, and marking the corresponding carbon emission analysis coefficient as a secondary emission coefficient;
and if the carbon emission analysis coefficient of the detection cell is less than L2, marking the corresponding detection cell as a tertiary emission cell, and marking the corresponding carbon emission analysis coefficient as a tertiary emission coefficient.
Further, the carbon emission analysis formula in step 1 is as follows:
Xi=β(TPi×a1+SDi×a2+ZLi×a3)
in the formula, a1, a2 and a3 are all preset proportionality coefficients, and the values of a1, a2 and a3 are 0.71, 0.76 and 0.84 respectively; beta is an error correction factor and takes a value of 1.02.
Step 2, emission reduction analysis: the energy-saving emission-reduction corresponding processes of the cell are analyzed, and the energy-saving emission-reduction processes of the cell are graded according to the analysis result, so that the carbon neutralization quantity value is low due to the fact that the energy-saving emission reduction is not matched with the carbon emission quantity of the corresponding cell, the carbon emission quantity exceeds the standard, the content of greenhouse effect gas in the environment is increased, and the environment is damaged due to the carbon emission quantity;
wherein, step 2 specifically includes:
step 21, collecting the number of energy-saving and emission-reducing processes of each detection cell and the average running time of the corresponding processes, and respectively marking the number of energy-saving and emission-reducing processes of each detection cell and the average running time of the corresponding processes as GSLi and GSCi;
step 22, collecting green planting areas and green planting frequencies in all detection cells, and respectively marking the green planting areas and the green planting frequencies in all the detection cells as LMJi and ZPLI;
step 23, obtaining emission reduction analysis coefficients Zi of each detection cell through an emission reduction analysis formula, and comparing the emission reduction analysis coefficients Zi of each detection cell with an emission reduction analysis coefficient threshold range;
if the emission reduction analysis coefficient Zi of the detection cell is larger than the emission reduction analysis coefficient threshold range, marking the corresponding detection cell as a primary emission reduction cell, and marking the corresponding emission reduction analysis coefficient as a primary emission reduction coefficient;
if the emission reduction analysis coefficient Zi of the detection cell is within the emission reduction analysis coefficient threshold range, marking the corresponding detection cell as a secondary emission reduction cell, and marking the corresponding emission reduction analysis coefficient as a secondary emission reduction coefficient;
if the emission reduction analysis coefficient Zi of the detection cell is smaller than the emission reduction analysis coefficient threshold range, marking the corresponding detection cell as a third-level emission reduction cell, and marking the corresponding emission reduction analysis coefficient as a third-level emission reduction coefficient.
Further, the emission reduction analysis formula in step 2 is:
in the formula, b1, b2, b3 and b4 are all preset proportionality coefficients, and b1 is more than b2 and more than b3 is more than b4 and more than 0.
Step 3, comparing the energy saving and emission reduction grade of the cell with the carbon emission grade of the cell; according to the invention, through grade comparison, the carbon emission grade of the cell is effectively prevented from being not matched with the energy-saving emission reduction grade, so that unnecessary errors are brought to the carbon neutralization amount, and the carbon neutralization efficiency is reduced.
Wherein, step 3 specifically includes:
step 31, comparing the emission coefficient of each detection cell with the emission reduction coefficient corresponding grade, if the emission coefficient grade of the detection cell is greater than the emission reduction coefficient grade, judging that the carbon neutralization of the corresponding detection cell does not reach the standard, and marking the corresponding detection cell as a carbon neutralization non-standard cell;
step 32, if the emission coefficient grade of the detection cell is smaller than the emission reduction coefficient grade, judging that the carbon neutralization of the corresponding detection cell reaches the standard, and marking the corresponding detection cell as a carbon neutralization standard cell;
and step 33, if the emission coefficient grade of the detection cell is equal to the emission reduction coefficient grade, judging that the carbon neutralization cost of the corresponding detection cell is unqualified, and marking the corresponding detection cell as a cell with unqualified carbon neutralization cost.
Step 4, carrying out quantitative analysis on the carbon emission of the cell, and judging the carbon neutralization value; detecting the carbon neutralization value, verifying the matching detection of the carbon emission grade and the energy-saving emission reduction grade of the cell, and preventing the carbon neutralization efficiency from being reduced due to abnormal matching detection;
wherein, step 4 specifically includes:
step 41, carrying out quantitative analysis on the carbon neutralization standard-reaching cell, collecting the carbon emission of the detection cell, and marking the carbon emission as the initial emission;
if the initial discharge amount is larger than the corresponding discharge amount threshold value, judging that the initial discharge amount exceeds the standard;
if the initial discharge amount is smaller than the corresponding discharge amount threshold value, judging that the initial discharge amount does not exceed the standard;
step 42, collecting the carbon emission of the detected cell after the energy-saving emission-reduction process, and marking the carbon emission as the rear end emission;
if the rear end discharge amount is larger than the corresponding discharge amount threshold value, judging that the rear end discharge amount exceeds the standard, collecting a difference value between the initial discharge amount and the rear end discharge amount, and if the difference value is larger than the corresponding difference value threshold value, generating a mismatching signal;
if the difference value is smaller than the corresponding difference value threshold value, generating an emission reduction abnormal signal;
and if the rear tail emission is smaller than the corresponding emission threshold, judging that the rear tail emission does not exceed the standard, and generating a normal emission reduction signal.
The working principle of the invention is as follows:
in operation, emission analysis: analyzing the carbon emission of the cells, and grading the emission grades of the cells according to the carbon emission; emission reduction analysis: analyzing the energy-saving emission-reducing procedures of the cell, and grading the energy-saving emission-reducing procedures corresponding to the cell; grade comparison: comparing the energy-saving emission-reduction grade of the cell with the emission grade; and (3) quantitative verification: carrying out quantitative analysis on the discharge amount of the cell, and judging a carbon neutralization value; and detecting the carbon neutralization value, and verifying the matching detection of the community emission level and the energy-saving emission-reducing level.
The above formulas are all calculated by taking the numerical value of the dimension, the formula is a formula which obtains the latest real situation by acquiring a large amount of data and performing software simulation, and the preset parameters in the formula are set by the technical personnel in the field according to the actual situation.
The above is only a preferred embodiment of the present invention, and is not intended to limit the present invention, and various modifications and changes will occur to those skilled in the art. Any modification, equivalent replacement, or improvement made within the spirit and principle of the present invention should be included in the protection scope of the present invention.
Claims (7)
1. A method for calculating carbon neutralization amount of an urban cell is characterized by comprising the following steps:
step 1, emission analysis: analyzing the carbon emission of the cell, and grading the carbon emission of the cell according to the analysis result;
step 2, emission reduction analysis: analyzing the corresponding processes of energy conservation and emission reduction of the cell, and grading the processes of energy conservation and emission reduction of the cell according to the analysis result;
step 3, grade comparison: comparing the energy saving and emission reduction grade of the cell with the carbon emission grade of the cell;
step 4, quantitative verification: carrying out quantitative analysis on the carbon emission of the cell, and judging the carbon neutralization value; and detecting the carbon neutralization value, and verifying the matching detection of the carbon emission grade and the energy-saving emission-reducing grade of the cell.
2. The method for calculating carbon neutralization amount of urban cell according to claim 1, wherein the step 1 specifically comprises:
step 11, marking the cell subjected to carbon emission analysis as a detection cell, and setting a mark i which is a natural number greater than 1;
step 12, setting detection time, collecting the total carbon emission amount of the detection cell within the detection time, and marking the total carbon emission amount of the detection cell within the detection time as TPi;
acquiring the increase speed of the carbon emission corresponding to the detection cell in the detection time, and marking the increase speed of the carbon emission corresponding to the detection cell in the detection time as SDi;
collecting the type of the exhaust gas corresponding to the carbon emission of the detection cell in the detection time, and marking the type of the exhaust gas corresponding to the carbon emission of the detection cell in the detection time as ZLi;
step 13, acquiring a carbon emission analysis coefficient Xi of each detection cell through a carbon emission analysis formula, and comparing the carbon emission analysis coefficient of each detection cell with L1 and L2;
wherein L1 and L2 are both carbon emission analysis coefficient threshold values, and L1 is more than L2;
if the carbon emission analysis coefficient of the detection cell is larger than or equal to L1, marking the corresponding detection cell as a primary emission cell, and marking the corresponding carbon emission analysis coefficient as a primary emission coefficient;
if the carbon emission analysis coefficient of the detection cell is less than or equal to L2 and less than L1, marking the corresponding detection cell as a secondary emission cell, and marking the corresponding carbon emission analysis coefficient as a secondary emission coefficient;
and if the carbon emission analysis coefficient of the detection cell is less than L2, marking the corresponding detection cell as a tertiary emission cell, and marking the corresponding carbon emission analysis coefficient as a tertiary emission coefficient.
3. The method for calculating the carbon neutralization amount of the urban cell according to claim 2, wherein the carbon emission analysis formula is as follows:
Xi=β(TPi×a1+SDi×a2+ZLi×a3)
in the formula, a1, a2 and a3 are all preset proportionality coefficients, and the values of a1, a2 and a3 are 0.71, 0.76 and 0.84 respectively; beta is an error correction factor and takes a value of 1.02.
4. The urban cell carbon neutralization amount calculation method according to any one of claims 1 to 3, wherein the step 2 specifically comprises:
step 21, collecting the number of energy-saving and emission-reducing processes of each detection cell and the average running time of the corresponding processes, and respectively marking the number of energy-saving and emission-reducing processes of each detection cell and the average running time of the corresponding processes as GSLi and GSCi;
step 22, collecting green planting areas and green planting frequencies in all detection cells, and respectively marking the green planting areas and the green planting frequencies in all the detection cells as LMJi and ZPLI;
step 23, obtaining emission reduction analysis coefficients Zi of each detection cell through an emission reduction analysis formula, and comparing the emission reduction analysis coefficients Zi of each detection cell with an emission reduction analysis coefficient threshold range;
if the emission reduction analysis coefficient Zi of the detection cell is larger than the emission reduction analysis coefficient threshold range, marking the corresponding detection cell as a primary emission reduction cell, and marking the corresponding emission reduction analysis coefficient as a primary emission reduction coefficient;
if the emission reduction analysis coefficient Zi of the detection cell is within the emission reduction analysis coefficient threshold range, marking the corresponding detection cell as a secondary emission reduction cell, and marking the corresponding emission reduction analysis coefficient as a secondary emission reduction coefficient;
if the emission reduction analysis coefficient Zi of the detection cell is smaller than the emission reduction analysis coefficient threshold range, marking the corresponding detection cell as a third-level emission reduction cell, and marking the corresponding emission reduction analysis coefficient as a third-level emission reduction coefficient.
6. The urban cell carbon neutralization amount calculation method according to any one of claims 1 to 3, wherein the step 3 specifically comprises:
step 31, comparing the emission coefficient of each detection cell with the emission reduction coefficient corresponding grade, if the emission coefficient grade of the detection cell is greater than the emission reduction coefficient grade, judging that the carbon neutralization of the corresponding detection cell does not reach the standard, and marking the corresponding detection cell as a carbon neutralization non-standard cell;
step 32, if the emission coefficient grade of the detection cell is smaller than the emission reduction coefficient grade, judging that the carbon neutralization of the corresponding detection cell reaches the standard, and marking the corresponding detection cell as a carbon neutralization standard cell;
and step 33, if the emission coefficient grade of the detection cell is equal to the emission reduction coefficient grade, judging that the carbon neutralization cost of the corresponding detection cell is unqualified, and marking the corresponding detection cell as a cell with unqualified carbon neutralization cost.
7. The urban cell carbon neutralization amount calculation method according to any one of claims 1 to 3, wherein the step 4 specifically comprises:
step 41, carrying out quantitative analysis on the carbon neutralization standard-reaching cell, collecting the carbon emission of the detection cell, and marking the carbon emission as the initial emission;
if the initial discharge amount is larger than the corresponding discharge amount threshold value, judging that the initial discharge amount exceeds the standard;
if the initial discharge amount is smaller than the corresponding discharge amount threshold value, judging that the initial discharge amount does not exceed the standard;
step 42, collecting the carbon emission of the detected cell after the energy-saving emission-reduction process, and marking the carbon emission as the rear end emission;
if the rear end discharge amount is larger than the corresponding discharge amount threshold value, judging that the rear end discharge amount exceeds the standard, collecting a difference value between the initial discharge amount and the rear end discharge amount, and if the difference value is larger than the corresponding difference value threshold value, generating a mismatching signal;
if the difference value is smaller than the corresponding difference value threshold value, generating an emission reduction abnormal signal;
and if the rear tail emission is smaller than the corresponding emission threshold, judging that the rear tail emission does not exceed the standard, and generating a normal emission reduction signal.
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CN115600824A (en) * | 2022-12-09 | 2023-01-13 | 国网浙江省电力有限公司金华供电公司(Cn) | Early warning method and device for carbon emission, storage medium and electronic equipment |
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Publication number | Priority date | Publication date | Assignee | Title |
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CN115600824A (en) * | 2022-12-09 | 2023-01-13 | 国网浙江省电力有限公司金华供电公司(Cn) | Early warning method and device for carbon emission, storage medium and electronic equipment |
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