Quantitative Comparison of China’s Multi-Level Carbon Peaking Policies Based on Natural Language Processing
Abstract
1. Introduction
2. Data and Methods
2.1. Data Source
2.2. Methodology
2.2.1. Natural Language Processing
- (1)
- Data cleaning [33]: Remove the guiding ideology, departments responsible for division of labor, etc. from the text and standardize the text format.
- (2)
- Use Jieba for word segmentation and extract the key words and their weights in each policy text. Jieba is a Python-based (Python 3.11.7) Chinese natural language processing toolkit widely used for Chinese text segmentation, keyword extraction, and weight calculation.
- (3)
- Policy classification: Extract policy instruments from the text based on key words and uniformly define the remaining policy content as policy objectives.
- (4)
- Policy instrument scoring: Existing studies primarily classify policy instruments into 3–4 categories, such as command-and-control, market-based incentives, public participation, and composite types [26,34,35]. Examples include taxes [27], subsidies [36], tradable permits [37], economic support, technological innovation, and management improvements [38]. The choice of policy instruments by governments is influenced by multiple factors [17], and different instruments have varying effects on policy implementation outcomes [39,40]. A preliminary analysis of carbon peaking implementation plans reveals that their policy instruments are highly concentrated in three dimensions: regulation establishment, market regulation, and execution supervision. This specificity leads to significant differences in the type composition, mechanism of action, and implementation pathways; command-and-control instruments lean toward legislation, while public participation instruments lean toward public oversight. Therefore, drawing on Liao (2018) [34], this paper classifies policy instruments into legal (rigid constraints through laws, standards, approvals, etc.), market (guidance through economic means like pricing, fiscal, taxation, and finance), and supervision (ensuring execution through mechanisms like assessment, evaluation, rewards, and penalties). The keywords and scores for each instrument type are 3, 2, and 1, respectively (Table 1). It is noteworthy that a single policy sentence may contain multiple instrument keywords. However, following the uniqueness principle, each sentence was assigned to only one instrument category, with prioritization in the order of legal > market > supervision.
- (5)
- Manual marking of policy targets: One third of the policy target documents are randomly selected for manual annotation. Most existing studies’ scores are based on the precision of textual descriptions. For instance, A 4-level scoring system (3, 2.25, 1.5, 0.75) for energy-saving targets was established based on the clarity of expression [26]. Building on this, this paper categorizes policy targets into three types based on whether the text contains precise numerical values and key elements. Sentences with specific quantified values were classified as the precise type and scored as 3; texts that did not contain key elements such as a time and place or were expressed ambiguously were classified as the vague type and received a score of 1. Texts that fell between the two were uniformly set as the general type and received a score of 2 (Table 1).
- (6)
- Calculation of policy intensity: At present, there is no unified standard for the definition of and calculation method for policy intensity in various studies. In existing research, policy intensity has been conceptualized primarily through two distinct approaches. One approach defines policy intensity as the product of the policy instrument intensity and policy target intensity, emphasizing that these two components together constitute the complete dimension of policy intervention [24]. Another approach expands this model by incorporating the factor of the policy level, defining policy intensity as the product of the policy instrument intensity, policy target intensity, and policy level intensity, thereby offering a more comprehensive characterization of a policy’s overall impact [26]. Since this study investigates hierarchical differences, it refers to the method of Zhang et al. (2022) [24], defining policy intensity as the product of the policy target intensity and policy instrument intensity:
2.2.2. Machine Learning
3. Results
3.1. Policy Keywords
3.2. Hierarchical Differences in Policy Instruments
3.3. Hierarchical Differences in Policy Targets
3.4. Hierarchical Differences in Policy Intensity
4. Discussion
5. Conclusions
5.1. Key Findings
5.2. Policy Implications
5.3. Limitations and Future Research Directions
Supplementary Materials
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Conflicts of Interest
References
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| Dimension | Category | Score | Keywords and Examples |
|---|---|---|---|
| Policy instrument | Legal | 3 | Laws, standards, approvals, violations, and irregularities, etc. |
| Market | 2 | Taxation, electricity prices, finance, loans, bonds, credit, etc. | |
| Supervision | 1 | Assessment, evaluation, commendation, rewards, criticism, etc. | |
| Policy target | Precise | 3 | By 2025, the proportion of non-fossil energy consumption will reach 24% |
| By 2025, the annual utilization volume of bulk solid waste will reach approximately 4 million tons | |||
| General | 2 | During the “15th Five-Year Plan” period, carbon emissions in the construction sector continued to decline | |
| By 2025, a provincial carbon benefit application platform will be initially established | |||
| Vague | 1 | Develop agricultural and forestry biomass power generation and waste incineration power generation in accordance with local conditions | |
| Develop hydropower in accordance with local conditions and encourage the expansion and potential tapping of hydropower capacity |
| Model Combination | Report | Best Parameters Found | |||||
|---|---|---|---|---|---|---|---|
| Parameter | Accuracy | Precision | Recall | F1 | C | Gamma | Kernel |
| TF-IDF+SVM | 0.87 | 0.87 | 0.87 | 0.87 | 100 | 0.1 | rbf |
| Level | Legal | Market | Supervision | Total | |||
|---|---|---|---|---|---|---|---|
| Quantity | Proportion | Quantity | Proportion | Quantity | Proportion | Quantity | |
| Country | 26.0 | 47.3% | 22.0 | 40.0% | 7.0 | 12.7% | 55.0 |
| Province | 17.8 | 35.5% | 23.4 | 45.5% | 9.5 | 19.0% | 50.7 |
| City | 13.4 | 31.1% | 19.5 | 45.0% | 9.6 | 23.9% | 42.5 |
| County | 13.0 | 30.6% | 19.9 | 45.9% | 9.8 | 23.4% | 42.7 |
| Level | Precise | General | Vague | Total | |||
|---|---|---|---|---|---|---|---|
| Quantity | Proportion | Quantity | Proportion | Quantity | Proportion | Quantity | |
| Country | 19.0 | 6.9% | 38.0 | 13.8% | 218.0 | 79.3% | 275.0 |
| Province | 23.7 | 8.5% | 47.3 | 17.1% | 205.4 | 74.4% | 276.4 |
| City | 23.0 | 9.2% | 48.7 | 19.6% | 176.2 | 71.2% | 247.9 |
| County | 21.6 | 8.4% | 43.7 | 17.7% | 179.5 | 73.8% | 244.8 |
| Dimension | Sub-Dimension | Specific Indicator | Policy Instrument Intensity | Policy Target Intensity | Policy Intensity | |||
|---|---|---|---|---|---|---|---|---|
| Correlation Coefficient | p Value | Correlation Coefficient | p Value | Correlation Coefficient | p Value | |||
| Economic Level | Regional GDP | Regional GDP (CNY 100 million) 2023 | −0.28 | 0.20 | −0.30 | 0.17 | −0.33 | 0.13 |
| Per Capita Economic Indicators | Per Capita Regional GDP (CNY/person) 2023 | −0.51 | 0.01 | −0.48 | 0.02 | −0.49 | 0.02 | |
| Per Capita Disposable Income of All Residents (CNY) 2023 | −0.50 | 0.01 | −0.46 | 0.03 | −0.48 | 0.02 | ||
| Per Capita Consumption Expenditure of All Residents (CNY) 2023 | −0.49 | 0.02 | −0.45 | 0.03 | −0.47 | 0.02 | ||
| Industrial Structure | Value Added by Primary Industry (CNY 100 million) 2023 | 0.04 | 0.84 | −0.08 | 0.71 | −0.04 | 0.86 | |
| Value Added by Secondary Industry (CNY 100 million) 2023 | −0.18 | 0.42 | −0.19 | 0.39 | −0.22 | 0.30 | ||
| Value Added by Tertiary Industry (CNY 100 million) 2023 | −0.37 | 0.08 | −0.38 | 0.07 | −0.41 | 0.05 | ||
| Value Added by Industry (CNY 100 million) 2023 | −0.18 | 0.40 | −0.18 | 0.42 | −0.22 | 0.31 | ||
| Value Added by Construction (CNY 100 million) 2023 | −0.13 | 0.56 | −0.24 | 0.27 | −0.23 | 0.30 | ||
| Value Added by Agriculture, Forestry, Animal Husbandry, and Fishery (CNY 100 million) 2023 | 0.04 | 0.87 | −0.08 | 0.71 | −0.04 | 0.84 | ||
| Value Added by Wholesale and Retail Trade (CNY 100 million) 2023 | −0.25 | 0.25 | −0.26 | 0.24 | −0.30 | 0.16 | ||
| Value Added by Transport, Storage, and Postal Services (CNY 100 million) 2023 | −0.26 | 0.23 | −0.24 | 0.26 | −0.29 | 0.18 | ||
| Value Added by Accommodation and Catering Services (CNY 100 million) 2023 | −0.22 | 0.30 | −0.30 | 0.16 | −0.30 | 0.16 | ||
| Value Added by Financial Intermediation (CNY 100 million) 2023 | −0.45 | 0.03 | −0.46 | 0.03 | −0.48 | 0.02 | ||
| Value Added by Real Estate (CNY 100 million) 2023 | −0.28 | 0.20 | −0.32 | 0.13 | −0.34 | 0.11 | ||
| Value Added by Other Industries (CNY 100 million) 2023 | −0.42 | 0.05 | −0.43 | 0.04 | −0.45 | 0.03 | ||
| Population Size | Total Population | Year-End Resident Population (10,000 persons) 2023 | −0.09 | 0.68 | −0.18 | 0.41 | −0.17 | 0.44 |
| Urbanization and Density | Urbanization Rate (%) 2023 | −0.30 | 0.16 | −0.25 | 0.25 | −0.27 | 0.21 | |
| Urban Population Density (persons/km2) 2019 | 0.10 | 0.66 | −0.06 | 0.77 | −0.04 | 0.86 | ||
| Environment and Ecology | Carbon Emissions | Total Greenhouse Gas Emissions (10,000 tons CO2 equivalent) 2021 | −0.04 | 0.87 | 0.18 | 0.41 | 0.09 | 0.70 |
| Per Capita Greenhouse Gas Emissions (tons CO2 equivalent/person) 2021 | 0.07 | 0.74 | 0.39 | 0.06 | 0.28 | 0.20 | ||
| Greenhouse Gas Emissions per Unit GDP (tons CO2 equivalent/10,000 yuan) 2021 | 0.13 | 0.55 | 0.39 | 0.07 | 0.29 | 0.17 | ||
| Greening and Ecology | Urban Green Space Area (10,000 hectares) 2023 | −0.16 | 0.45 | −0.12 | 0.57 | −0.18 | 0.42 | |
| Forest Coverage Rate (%) 2023 | 0.20 | 0.37 | −0.22 | 0.31 | 0.00 | 1.00 | ||
| Forest Area (10,000 hectares) 2023 | 0.11 | 0.63 | 0.08 | 0.72 | 0.12 | 0.60 | ||
| Forestry Land Area (10,000 hectares) 2023 | 0.11 | 0.62 | 0.17 | 0.44 | 0.17 | 0.43 | ||
| Energy Consumption and Production | Energy Consumption | Electricity Consumption (100 million kWh) 2023 | −0.17 | 0.45 | −0.07 | 0.75 | −0.14 | 0.51 |
| Coal Consumption (10,000 tons) 2019 | 0.11 | 0.62 | 0.31 | 0.15 | 0.24 | 0.27 | ||
| Kerosene Consumption (10,000 tons) 2019 | −0.51 | 0.01 | −0.54 | 0.01 | −0.53 | 0.01 | ||
| Gasoline Consumption (10,000 tons) 2019 | −0.19 | 0.39 | −0.20 | 0.36 | −0.20 | 0.36 | ||
| Natural Gas Consumption (100 million cubic meters) 2019 | −0.23 | 0.30 | −0.28 | 0.19 | −0.29 | 0.17 | ||
| Energy Production | Investment in Energy Industry (100 million yuan) 2017 | −0.03 | 0.89 | 0.05 | 0.81 | −0.02 | 0.94 | |
| Electricity Generation (100 million kWh) 2021 | −0.10 | 0.64 | 0.04 | 0.87 | −0.04 | 0.86 | ||
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Zhen, M.; Li, H.; Wang, Y. Quantitative Comparison of China’s Multi-Level Carbon Peaking Policies Based on Natural Language Processing. Sustainability 2026, 18, 296. https://doi.org/10.3390/su18010296
Zhen M, Li H, Wang Y. Quantitative Comparison of China’s Multi-Level Carbon Peaking Policies Based on Natural Language Processing. Sustainability. 2026; 18(1):296. https://doi.org/10.3390/su18010296
Chicago/Turabian StyleZhen, Mengmeng, Huimin Li, and Yufei Wang. 2026. "Quantitative Comparison of China’s Multi-Level Carbon Peaking Policies Based on Natural Language Processing" Sustainability 18, no. 1: 296. https://doi.org/10.3390/su18010296
APA StyleZhen, M., Li, H., & Wang, Y. (2026). Quantitative Comparison of China’s Multi-Level Carbon Peaking Policies Based on Natural Language Processing. Sustainability, 18(1), 296. https://doi.org/10.3390/su18010296

