Next Article in Journal
Managing Rural Decline in the 21st Century: Spatial Insights from European Shrinking Regions
Next Article in Special Issue
The Temporal Paradox of Mandatory Sustainability Disclosure: Evidence from Saudi Arabia’s 2021 Tadawul ESG Guidelines on Reporting Quality
Previous Article in Journal
Unveiling the Role of Corporate Governance in Shaping Environmental, Social, and Governance Performance and Firm Outcomes
Previous Article in Special Issue
Digital Finance, Internal and External Governance, and Corporate Environmental Information Disclosure
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Carbon Information Disclosure Quality in China’s Petroleum and Petrochemical Enterprises: An LLM Approach

College of Economics and Management, Nanjing Forestry University, No. 159 Longpan Road, Xuanwu District, Nanjing 210037, China
*
Author to whom correspondence should be addressed.
Sustainability 2026, 18(10), 5089; https://doi.org/10.3390/su18105089
Submission received: 2 April 2026 / Revised: 14 May 2026 / Accepted: 15 May 2026 / Published: 18 May 2026

Abstract

Global climate governance and corporate low-carbon transition have made carbon information disclosure important for assessing firms’ environmental governance and climate-risk responses. This study develops an industry-specific carbon information disclosure quality (CIDQ) framework for Chinese A-share listed petroleum and petrochemical firms, using 45 firm-year observations from 15 firms during 2022–2024. The framework includes 7 primary, 15 secondary, and 33 tertiary indicators. Disclosure texts were scored by the DeepSeek-V3.2 large language model (LLM) under predefined rule-based criteria, with temperature set to 0. Reliability was assessed against manual scoring of 15 reports, yielding an intraclass correlation coefficient (ICC) of 0.974. The full-sample mean score is 34.02, accounting for only 51.55% of the theoretical maximum of 66, indicating that the overall disclosure level remains relatively low. The annual mean score increased from 29.07 in 2022 to 37.60 in 2024, representing a cumulative rise of 8.53 points, or 29.34%. Substantial inter-firm differences are also observed: Sinopec recorded the highest three-year average score of 52.67, whereas Yunnan Yunwei recorded the lowest at 10.67. This study may provide a methodological reference for structured CIDQ evaluation and disclosure improvement in high-emission industries.

1. Introduction

Global climate governance has accelerated in recent years, increasing the importance of carbon information disclosure. The Emissions Gap Report 2024 issued by the United Nations Environment Programme (UNEP), which assesses the gap between current policy trajectories and the emission levels required to achieve the goals of the Paris Agreement while tracking global emissions trends, nationally determined contributions (NDCs), and sectoral mitigation potential, reports that global greenhouse gas emissions reached a record high of 57.1 GtCO2e in 2023. For firms in high-emission industries, information on carbon emissions, emission reduction targets, governance mechanisms, and climate-related risks is no longer merely a supplementary statement of environmental responsibility; rather, it has become an important basis for external stakeholders to assess firms’ environmental governance capacity, responses to climate-related risks, and progress toward a low-carbon transition. Accordingly, carbon information disclosure has gradually evolved from a predominantly voluntary corporate practice into an important information activity with implications for corporate governance, regulatory oversight, and market pricing [1,2,3,4].
As research in this field has expanded, scholarly attention has gradually shifted from whether firms disclose carbon-related information to the quality of such disclosure. Compared with merely examining whether firms disclose carbon-related information, carbon information disclosure quality (CIDQ) places greater emphasis on whether the disclosed content is complete, reliable, comparable, and useful for decision-making, thereby better reflecting firms’ actual level of climate governance and low-carbon transition capacity. However, the existing literature has yet to establish a unified framework for defining CIDQ, constructing indicator systems, and setting scoring rules, and substantial differences remain across studies in terms of evaluation dimensions and measurement outcomes [1,5,6]. This suggests that the assessment of CIDQ should not rely on the simple application of generic frameworks, but instead requires targeted adjustments that take into account the emission characteristics, transition pathways, and disclosure priorities of specific industries.
The petroleum and petrochemical industry provides an important context for research on CIDQ. This industry is characterized by high emission intensity, complex production processes, long industrial chains, and a large share of value-chain-related emissions, and therefore faces considerable pressure from climate governance and strong constraints associated with the low-carbon transition. Compared with firms in other industries, carbon information disclosure in this sector involves not only direct emissions and energy use, but also more industry-specific issues, such as Scope 3 emissions (according to the Greenhouse Gas Protocol, Scope 3 emissions refer to other indirect emissions occurring across the value chain, including both upstream and downstream emissions; see World Resources Institute (WRI) and World Business Council for Sustainable Development (WBCSD), Corporate Value Chain (Scope 3) Accounting and Reporting Standard, 2011) [7], supply chain carbon management, low-carbon technology development, responses to transition risks, and social impacts [8,9,10]. This indicates that the assessment of CIDQ in the petroleum and petrochemical industry cannot rely directly on generic evaluation frameworks, but instead requires a more targeted framework that incorporates industry-specific characteristics. Against this background, this study raises the following question: how can a CIDQ evaluation framework that captures industry characteristics be developed for China’s A-share petroleum and petrochemical industry, and how can such a framework be used to identify firms’ disclosure levels and inter-firm differences?
Recent sustainability disclosure initiatives in China have further increased the importance of standardized non-financial reporting. However, these developments do not eliminate the need for industry-specific evaluation tools. In sectors such as petroleum and petrochemicals, disclosure content is technically complex, strongly value-chain related, and closely linked to transition risk, making generic reporting guidance insufficient for fine-grained quality assessment. Accordingly, the specific gap addressed by this study is not simply the lack of a unified CIDQ framework in general, but the absence of an industry-specific, rule-based, and operationally transparent framework for evaluating carbon information disclosure quality in a high-emission sector with strong Scope 3 relevance and transition-related disclosure complexity.
Existing research on CIDQ still relies heavily on manual content analysis. Although manual coding enables researchers to identify disclosure content in light of textual context, its limitations in terms of time costs, consistency control, and repeated operations have become increasingly evident as sample sizes expand, disclosure texts become longer, and evaluation indicators grow more refined. Keyword-based text analysis is relatively efficient, but it has difficulty distinguishing substantive disclosure from symbolic statements and is less capable of capturing contextual semantics and differences in information quality. Traditional machine-learning methods offer greater flexibility in text classification and pattern recognition, but they typically depend on large-scale manually labeled samples and feature engineering. In recent years, the rapid development of large language models (LLMs) has provided a new technical pathway for structured disclosure evaluation. For tasks such as CIDQ evaluation, in which scoring criteria are relatively explicit and task boundaries are clearly defined, LLMs may be particularly suitable because they can identify and score disclosure content on the basis of predefined indicators and scoring rules, while also supporting contextual understanding and information integration across different sections of lengthy and structurally complex reports [11,12].
In this context, this study takes A-share listed companies in China’s petroleum and petrochemical industry from 2022 to 2024 as the research sample. In terms of research design, this study first constructs a CIDQ indicator system comprising 7 primary indicators, 15 secondary indicators, and 33 tertiary indicators by integrating the core dimensions of disclosure quality identified in the existing literature, the commonly adopted requirements of international climate and sustainability disclosure frameworks, and the disclosure characteristics of the petroleum and petrochemical industry. Second, based on clearly defined scoring rules for the tertiary indicators, this study employs an LLM to identify, interpret, and score carbon information disclosed in corporate social responsibility reports, ESG reports, and sustainability reports, thereby constructing a company-year-level AI-based carbon information disclosure quality index (AI-CIDQ). Finally, based on the scoring results, this study systematically analyzes the current state of CIDQ among Chinese petroleum and petrochemical enterprises in terms of overall distribution, annual changes, inter-firm differences, and performance across industry-specific disclosure dimensions, and further examines the reliability and consistency of the LLM-based scores through comparison with manual scoring. Accordingly, this study focuses on framework construction and measurement rather than on testing the determinants or causal effects of CIDQ, with the purpose of developing an industry-specific and operationally transparent framework for evaluating carbon information disclosure quality in China’s petroleum and petrochemical industry.
This study makes three main contributions. First, it situates the evaluation of carbon information disclosure quality (CIDQ) in the petroleum and petrochemical industry, a high-emission sector characterized by complex production processes, long value chains, and strong transition constraints, thereby extending CIDQ research to a context in which generic disclosure evaluation frameworks may be insufficient. Second, it develops an industry-oriented CIDQ indicator system comprising 7 primary indicators, 15 secondary indicators, and 33 tertiary indicators by integrating general disclosure quality dimensions with the commonly adopted requirements of international climate and sustainability disclosure frameworks and the industry-specific disclosure characteristics of petroleum and petrochemical firms. Third, it introduces an LLM-assisted, rule-based scoring approach into CIDQ evaluation and demonstrates, through comparison with manual scoring, that this method can provide relatively stable support for structured disclosure assessment under clearly specified evaluation rules and retained manual review.
The rest of this paper is organized as follows. Section 2 reviews the relevant literature. Section 3 describes the sample selection, the construction of the indicator system, the scoring rules, the LLM-based scoring method, and the reliability test. Section 4 presents the overall results, annual changes, and inter-firm differences in CIDQ. Section 5 discusses the findings and the applicability of the LLM-based approach. Section 6 concludes the paper.

2. Literature Review

2.1. Corporate Carbon Information Disclosure

As climate-related risks continue to intensify, corporate carbon information disclosure has become an increasingly important topic in research on environmental governance, capital markets, and corporate sustainability. Early studies generally suggest that the disclosure of carbon emissions, energy use, emission reduction targets, and related environmental management information helps enhance the transparency of environmental governance and enables investors, regulators, and other stakeholders to identify firms’ climate-related risks and transition pressures [13,14]. As climate issues have become increasingly embedded in international governance frameworks and capital market rules, carbon information disclosure has gradually evolved from a voluntary tool for corporate environmental communication into an important information mechanism with governance, regulatory, and market implications.
The existing literature has mainly focused on the determinants, influencing factors, and economic consequences of carbon information disclosure. With regard to disclosure incentives, firms often voluntarily disclose carbon emissions and related governance information in response to environmental concerns from investors, consumers, and the broader public, thereby improving corporate image, maintaining legitimacy, and enhancing social reputation [15]. In terms of influencing factors, firms’ environmental performance, governance structures, and external institutional pressures are widely regarded as important determinants of disclosure levels. For example, some studies find that firms with better environmental performance tend to disclose more detailed climate-related information [16], while board independence, board diversity, and other governance characteristics can also significantly affect the extent of greenhouse gas emissions disclosure [17]. Cross-country comparative studies further show that differences in regulatory systems, enforcement intensity, investor attention, and social norms lead to substantial divergence in firms’ carbon information disclosure practices [18]. This suggests that corporate carbon information disclosure is not merely an act of information release, but rather the result of the joint influence of internal governance conditions and the external institutional environment.
In addition to disclosure incentives, prior studies have also examined the governance effects and economic consequences of carbon information disclosure. A higher level of carbon information disclosure helps reduce external information asymmetry and strengthens the basis on which market participants assess firms’ environmental responsibility and transition capacity [19,20]. At the same time, disclosure itself may further encourage firms to improve carbon emissions management and environmental governance practices through reputational mechanisms, regulatory pressure, and capital market feedback [10]. In this sense, carbon information disclosure not only reflects firms’ existing environmental performance but may also influence their subsequent environmental governance practices through reputational mechanisms, regulatory pressure, and capital market feedback.
In the Chinese context, with the introduction of the “dual carbon” goals and the continued advancement of green finance, ESG governance, and environmental regulation, increasing attention has been paid to corporate carbon information disclosure. Existing studies show that public information channels such as social media can exert legitimacy pressure on firms, thereby encouraging them to disclose more carbon emissions information [21]. Climate-related disclosure has also, to some extent, promoted corporate emission reduction efforts and improvements in environmental governance [10]. Overall, the existing literature has provided substantial insights into the institutional background, driving factors, and governance consequences of corporate carbon information disclosure. However, significant differences remain across firms in terms of disclosure scope, depth, and standardization. Accordingly, how to systematically evaluate the quality of corporate carbon information disclosure has become an important extension of this line of research.
More recently, sustainability disclosure regulation and green finance developments in China have further increased the importance of carbon information disclosure. In 2024, China’s stock exchanges introduced new sustainability disclosure rules and subsequently issued implementation-oriented guidance, further strengthening expectations for more standardized non-financial reporting. (China’s stock exchanges issued sustainability reporting guidelines for listed companies in 2024. See Shanghai Stock Exchange, Guidelines No. 14 of Shanghai Stock Exchange for Self-Regulation of Listed Companies—Sustainability Report (Trial), issued on 12 April 2024 and effective from 1 May 2024; Shenzhen Stock Exchange, Guidelines No. 17 of Shenzhen Stock Exchange for Self-Regulation of Listed Companies—Sustainability Report (Trial), 2024. For subsequent implementation-oriented guidance, see Shanghai Stock Exchange, Sustainability Reporting Guidance, 2025.) At the same time, the continued advancement of green finance and the growing policy relevance of carbon-related markets have increased the importance of climate-related disclosure for listed firms, especially in high-emission sectors.
These developments suggest that the Chinese market context after 2024 is not only characterized by stronger disclosure expectations, but also by a growing need for more fine-grained evaluation tools. In the petroleum and petrochemical industry, where carbon-related disclosure is closely linked to Scope 3 emissions, value-chain management, and transition-related governance issues, generic reporting guidance alone is insufficient for assessing disclosure quality in a detailed and industry-sensitive manner.

2.2. Evaluation of CIDQ

As corporate sustainability reporting and climate-related disclosure continue to expand, the focus of research on carbon information disclosure has gradually shifted from whether firms disclose such information to the quality of that disclosure. Compared with merely examining whether firms provide carbon-related information, CIDQ places greater emphasis on the completeness, reliability, comparability, and decision relevance of disclosed content, and therefore better reflects firms’ climate governance capacity, information transparency, and progress in the low-carbon transition. In response to this issue, existing studies have explored CIDQ from multiple perspectives, including evaluation dimensions, indicator systems, and measurement methods.
In terms of evaluation content, the existing literature generally defines CIDQ as the level of information disclosed by firms with respect to carbon emissions data, emission reduction targets, governance mechanisms, risk identification, strategic arrangements, and performance outcomes, while placing particular emphasis on completeness, reliability, comparability, and relevance [2]. Patten (2002) was among the first to apply content analysis to code corporate environmental information and construct an environmental disclosure index, thereby providing a foundational approach for subsequent research on the evaluation of environmental and carbon information disclosure [22]. Since then, related studies have gradually extended the object of evaluation from general environmental information to carbon information disclosure and progressively developed multidimensional indicator frameworks to identify differences across firms in both the quantity and quality of disclosure [23].
In terms of specific methods, the existing literature mainly adopts manual content analysis, keyword-based text analysis, and machine-learning-based text analysis, while some recent studies have also explored hybrid approaches that combine rule-based screening, semantic extraction, and model-assisted classification. Manual content analysis remains important for interpretive judgment, but it is time-consuming and requires careful reliability assessment to ensure coding consistency [24]. Keyword-based and text-mining approaches can improve processing efficiency, but they may have difficulty capturing contextual meaning, disclosure depth, and dispersed climate-related information in lengthy reports [25]. Machine-learning-based approaches can support classification tasks, but their performance often depends on the selection of textual analysis tools, labeled samples, and task-specific model design [26,27]. Although these approaches differ in technical form, they share a common challenge in CIDQ research: how to conduct structured and context-sensitive quality evaluation under transparent scoring rules.
In addition to measurement methods, prior studies have also examined the conditions shaping CIDQ. For example, corporate governance characteristics are widely regarded as important factors influencing firms’ disclosure behavior [28]. Carbon assurance can enhance the credibility of disclosed information and, to some extent, improve disclosure quality [29]. In the context of developing countries, disclosure quality is also significantly affected by factors such as firm size, profitability, and industry characteristics [30,31].
Overall, although recent studies have substantially advanced ESG disclosure research and the application of AI-based textual analysis, the existing literature still provides limited guidance on how to construct an industry-specific, rule-based, and operationally transparent framework for evaluating carbon information disclosure quality in high-emission sectors. This gap is particularly evident in the petroleum and petrochemical industry, where disclosure content is technically complex, strongly value-chain related, and closely linked to transition risk and industry-specific governance issues. Therefore, how to improve the efficiency, consistency, and replicability of CIDQ evaluation while preserving the transparency of evaluation rules remains an important methodological issue.

2.3. Methods for Disclosure Evaluation

Recent studies have further expanded the literature on ESG and sustainability disclosure as well as AI-assisted textual analysis. Emerging studies in accounting, finance, and sustainability research have begun to examine the use of AI and large language models (LLMs) for ESG-related tasks such as textual classification, topic identification, readability assessment, alignment analysis, and structured disclosure evaluation [32,33]. These studies suggest that AI-based methods may improve the efficiency and depth of disclosure analysis, while also raising important questions regarding interpretability, transparency, and research design.
As the volume of corporate sustainability reports and environmental disclosure continues to expand, researchers have increasingly attempted to improve the efficiency of disclosure research through automated text analysis techniques. Early studies mainly quantified textual information in corporate reports through word-frequency statistics, keyword matching, and dictionary-based methods, and on this basis identified firms’ disclosure topics, risk expressions, and management characteristics [34,35]. However, these methods are generally more suitable for detecting specific terms or textual patterns, while their ability to support information judgment in complex contexts, cross-paragraph integration, and rule-based scoring tasks remains relatively limited [36,37].
Subsequently, machine learning methods were gradually introduced into research on corporate disclosure. Machine learning can extract structured information from large volumes of corporate report texts, thereby significantly improving research efficiency [38]. Textual features have also been used to identify firms’ climate governance capacity, risk exposure, and information transmission characteristics [39,40,41]. In addition, topic modeling, sentiment analysis, and related machine-learning-based approaches have been widely applied in financial text and corporate disclosure research to examine disclosure topics, semantic tendencies, firm characteristics, and their economic consequences [42,43,44,45,46,47,48]. Overall, these methods have advanced disclosure research from manual coding toward automated text processing. However, their core tasks have still been concentrated primarily on topic identification, text classification, and semantic measurement, rather than on conducting multi-level structured scoring of disclosure content according to explicit rules.
In this context, LLMs provide a new approach to evaluating corporate disclosure. Unlike keyword-based methods, which mainly rely on term matching, and traditional machine learning methods, which typically depend on training samples and feature engineering, LLMs may be particularly suitable for rule-based disclosure evaluation tasks that require contextual understanding, cross-section information integration, and structured scoring under predefined criteria [11,12]. However, this does not imply that LLMs are free from methodological risks. In particular, LLM outputs may contain plausible but unsupported interpretations or hallucinated inferences when processing lengthy and technically complex reports. For this reason, their use in disclosure evaluation should be combined with explicit scoring rules, textual-evidence requirements, and manual verification procedures.
In the context of CIDQ evaluation, the research objects are usually sustainability reports or ESG reports that are lengthy and structurally complex, while the evaluation task requires the model to determine, on the basis of multi-level indicators, whether certain information is disclosed, to what extent it is disclosed, and whether it satisfies the corresponding scoring criteria. Such tasks require not only keyword identification but also contextual understanding, substantive judgment of disclosure content, and the mapping of information dispersed across different sections into a unified evaluation framework. Compared with earlier methods, LLMs are more likely to improve the automation and consistency of the evaluation process while preserving the transparency of evaluation rules.
Overall, the existing literature provides important insights into corporate carbon disclosure, CIDQ evaluation, and AI-assisted textual analysis, but these streams remain only partially integrated. Studies on carbon disclosure have mainly examined incentives, influencing factors, and economic consequences; studies on CIDQ have proposed multiple dimensions and measurement approaches, yet without establishing a unified or industry-sensitive evaluation structure; and studies on automated text analysis have improved processing efficiency, but have focused mainly on classification and semantic extraction rather than structured, rule-based quality assessment.
As a result, the literature still provides limited guidance on how to construct an industry-specific, rule-based, and operationally transparent framework for evaluating carbon information disclosure quality in a high-emission sector such as petroleum and petrochemicals. Accordingly, the research problem addressed by this study is how to develop and validate such a framework in a way that is methodologically transparent and practically applicable.

3. Research Design and Methodology

3.1. Sample and Data

This study takes A-share listed companies in China’s petroleum and petrochemical industry as the research sample. According to the Guidelines for Industry Classification of Listed Companies (2012 Revision) (China Securities Regulatory Commission (CSRC), Guidelines for the Industry Classification of Listed Companies (2012 Revision), issued on 26 October 2012 and effective from the date of issuance) issued by the China Securities Regulatory Commission, no separate industry category is established for the petroleum and petrochemical industry. Instead, the sector is mainly classified into two categories: B07 Extraction of Petroleum and Natural Gas and C25 Processing of Petroleum, Coking, and Nuclear Fuel. The sample scope of this study is defined accordingly. This classification standard is retained because it provides a clear and consistent basis for identifying the relevant A-share listed firms and is consistent with the industry coding used in listed-company datasets.
To ensure sample comparability and data completeness, two additional screening criteria were applied. First, firms that were subject to *ST or ST special treatment throughout the entire sample period were excluded. Second, firms must have continuously disclosed corporate social responsibility reports, ESG reports, or sustainability reports for three consecutive years from 2022 to 2024. After screening, a final sample of 15 firms was obtained. The study covers three fiscal years from 2022 to 2024, yielding a total of 45 firm-year observations. The sample firms and their basic information are presented in Table 1.
The final sample should be understood as the full set of A-share listed petroleum and petrochemical firms that met the study’s disclosure-based inclusion criteria during 2022–2024, rather than as an arbitrary subset. Although the sample size is limited, it reflects the set of observable eligible firms within this industry context that provided the necessary consecutive disclosure texts for structured evaluation. The disclosure texts used in this study are collected mainly from ESG reports, sustainability reports, and social responsibility reports publicly available on CNINFO (Juchao Information Network, an information disclosure website for Chinese listed companies) and the official websites of the sample firms.

3.2. Indicator System and Scoring Rules

Existing research has not yet established a unified framework for defining and evaluating corporate CIDQ, and substantial differences remain across studies in terms of indicator selection, evaluation priorities, and scoring methods [1]. Based on the preceding literature review and in light of the characteristics of the petroleum and petrochemical industry, this study develops an indicator system for evaluating corporate CIDQ.
The main reference bases used for constructing the indicator system are summarized in Table 2.
In designing the indicator system, this study draws primarily on the GHG Protocol, the recommendations of the Task Force on Climate-related Financial Disclosures (TCFD), and IFRS S2 Climate-related Disclosures, while also incorporating discussions in the existing literature on disclosure quality dimensions. (TCFD: Available online: https://www.fsb.org/2017/06/recommendations-of-the-task-force-on-climate-related-financial-disclosures-2 (accessed on 1 April 2026). The TCFD provides a climate-related disclosure framework covering governance, strategy, risk management, and metrics and targets. This study draws on this framework in designing related indicators. IFRS S2: Available online: https://www.ifrs.org/issued-standards/ifrs-sustainability-standards-navigator/ifrs-s2-climate-related-disclosures (accessed on 1 April 2026). IFRS S2, issued by the ISSB, sets out climate-related disclosure requirements across governance, strategy, risk management, and metrics and targets. The relevant indicators in this study are developed with reference to its core requirements. GHG Protocol: Available online: https://ghgprotocol.org/standards (accessed on 1 April 2026). Developed by WRI and WBCSD, the GHG Protocol provides a widely used framework for greenhouse gas accounting and reporting. This study draws on this standard in setting emission boundaries, accounting scope, and related indicators.) On this basis, seven first-level dimensions are identified: understandability, reliability, comparability, relevance, completeness, timeliness, and industry specificity.
Ultimately, this study constructs an evaluation system comprising 7 primary indicators, 15 secondary indicators, and 33 tertiary indicators. The primary indicators reflect the core dimensions of CIDQ, the secondary indicators specify the main components of each dimension, and the tertiary indicators correspond to disclosure items that can be directly identified and assessed. In this way, the indicator system is designed to balance theoretical rigor, industry applicability, and operational feasibility. The full indicator system is reported in Table 3.
This study adopts a content-analysis-based scoring method and applies a three-level scoring scheme to each tertiary indicator [24]. Specifically, a score of 0 is assigned when the relevant information is not disclosed; a score of 1 is assigned when the firm provides only qualitative descriptions without verifiable quantitative information; a score of 2 is assigned when the disclosure provides quantitative data, measurable targets, or sufficiently specific and verifiable information that satisfies the indicator-specific criterion. In the aggregation process, all tertiary indicators are assigned equal weight [49,50], and the resulting scores are summed to construct AI-CIDQ. Under the current indicator system, the theoretical maximum score of AI-CIDQ is 66.
All 33 tertiary indicators were assigned equal weight because the present study aimed to establish a transparent and replicable rule-based evaluation framework, and no widely accepted industry-specific weighting benchmark is currently available for CIDQ. In the present framework, dimensions such as Relevance, Timeliness, and Completeness are treated as conceptually distinct components of disclosure quality rather than as empirical effect variables requiring differential weights on the basis of observed statistical dominance.
Although PCA-based weighting is a possible alternative, it was not adopted in this study for three reasons. First, PCA-derived weights mainly reflect the covariance structure of the data rather than the theoretical importance of individual indicators. Second, PCA is more suitable when indicators are sufficiently correlated and may be less appropriate when conceptually important indicators are weakly correlated or represent distinct dimensions. Third, prior studies have noted that weighting and aggregation choices in composite indicators may affect interpretability, indicator importance, and ranking robustness [51,52,53]. Therefore, at the initial stage of framework construction, equal weighting is more consistent with the objectives of transparency, interpretability, and replicability adopted in this study. Alternative weighting schemes, including PCA-based or AHP-based approaches, may be explored in future extensions of the framework.
The indicator system is designed as an operational evaluation framework composed of conceptually distinct dimensions of disclosure quality, rather than as a reflective psychometric scale measuring a single latent construct. Therefore, CFA and internal-consistency statistics such as Cronbach’s alpha were not applied in the present study.
In addition to the general 0–1–2 scoring logic, the present study operationalized the rubric through indicator-specific decision rules. For each tertiary indicator, a score of 0 was assigned when no relevant disclosure was identified; a score of 1 was assigned when the firm provided qualitative or general descriptive information without verifiable quantitative support; and a score of 2 was assigned when the disclosure included quantitative data, measurable targets, or other verifiable evidence directly relevant to the indicator. To improve consistency and reproducibility, a detailed operational scoring guide for all 33 tertiary indicators is provided in Appendix B. The appendix reports the indicator descriptions, the 0–1–2 scoring criteria, and brief boundary notes that clarify how each criterion was applied.
In addition, several tertiary indicators with relatively broad conceptual scope were further operationalized to improve scoring transparency. Specifically, “Risk Disclosure” refers to the disclosure of climate-related transition risks, regulatory risks, market risks, or physical risks associated with carbon management, rather than general statements of environmental commitment. “Full Value Chain Coverage” refers to whether the report extends beyond direct operational emissions to cover major upstream and downstream carbon-related activities, such as purchased materials, transportation, product use, or logistics arrangements. “Just Transition” refers to disclosures concerning the social implications of low-carbon transition, including employee reskilling, workforce adjustment, community impact, or stakeholder communication in transition processes.

3.3. LLM-Based Evaluation Process

To improve the efficiency of text processing and maintain consistency in scoring standards, this study employed an LLM to assist in the evaluation of corporate carbon disclosure content. Because ESG reports, social responsibility reports, and sustainability reports are often lengthy, contain substantial professional terminology, and differ across firms in terms of expression, information distribution, and disclosure scope, a fully manual item-by-item assessment would be costly and difficult to standardize consistently. Considering the model’s Chinese-language capability and accessibility, this study uses the DeepSeek-V3.2 LLM. (In this study, the DeepSeek-V3.2 model, accessed through the DeepSeek–chat interface, was used only as an auxiliary tool for rule-based scoring of corporate disclosure texts under predefined criteria. It was not used to draft, revise, or polish the manuscript. All research design, indicator construction, result interpretation, and manuscript writing were completed by the authors.) Prior studies have also shown the potential of LLMs in sustainability reporting and structured disclosure evaluation [11,12]. The temperature parameter was set to 0 in order to reduce output randomness and improve consistency in rule-based scoring tasks. This setting was intended to enhance result stability in practice, but it should not be interpreted as guaranteeing complete determinism across repeated runs.
To improve methodological transparency, the scoring prompts were designed indicator by indicator on the basis of the predefined indicator description and the corresponding 0–1–2 scoring rule. Each prompt asked the model to determine whether the relevant information was disclosed, whether the disclosure was qualitative only or also supported by verifiable quantitative information, and to return the score together with a brief rationale, textual evidence, and an evidence-location field. Because the reports were often lengthy and structurally complex, the full reports were first converted into machine-readable text while preserving the original section order and major headings as far as possible. For each tertiary indicator, the evaluation was conducted at the full-document level rather than on isolated text fragments, so that the model could identify relevant information dispersed across different sections of the same report. The present study did not employ an external retrieval-augmented generation module or a separate grounding system; instead, contextual consistency was maintained by combining the full report text with indicator-specific prompts that instructed the model to locate, interpret, and score disclosure content according to predefined rules. A representative prompt used in the evaluation process is provided in Appendix A.
The evaluation process consists of three steps. First, the ESG reports, social responsibility reports, and sustainability reports of the sample firms were collected and organized, and the full reports were converted into machine-readable text. Second, based on the predefined indicator system, indicator descriptions, and scoring rules, scoring prompts were constructed separately for each tertiary indicator and entered into the LLM together with the full report text. The model then identified information relevant to the current indicator across the entire document and returned the corresponding score, scoring rationale, textual evidence, and evidence-location information. Third, the model outputs were aggregated and reviewed. Under the equal-weight assumption, the scores of all tertiary indicators were then summed to construct a company-year AI-CIDQ score.
Figure 1 shows the automated LLM-based scoring process for CIDQ. It presents the main steps of the evaluation procedure, including text input, rule-based prompt design, model scoring, structured output generation, and score aggregation.
Table 4 reports the AI-CIDQ scores of the sample firms from 2022 to 2024. It presents the firm-level scoring results and provides the basis for the subsequent analysis of annual trends and inter-firm differences.
After model scoring, manual review was conducted only for cases involving ambiguous semantics, negative statements, or insufficient evidence. This review was applied as a targeted verification procedure rather than as a full manual recoding of all reports or a blinded multi-coder coding exercise. The purpose was to examine whether the score returned by the model was adequately supported by the identified textual evidence under the predefined scoring rules, and to correct possible misjudgments where necessary.

3.4. Reliability and Consistency Test

To examine the reliability and consistency of the LLM-based scores, this study randomly selected 15 reports from the 45 sample reports and conducted manual scoring independently of the LLM-based scores using the unified tertiary-indicator system and the 0–1–2 scoring rules. The reliability assessment concerns the consistency between LLM-based scores and manually assigned benchmark scores, rather than interrater reliability among multiple independent human coders.
The main evaluation process involved 45 firm-year reports and 33 tertiary indicators, resulting in 1485 indicator-level LLM scoring tasks. In the reliability test, the 15 sampled reports were manually scored at the tertiary-indicator level, yielding 495 paired observations. These figures indicate the operational scale of the computational and annotation process in the present study. It should be noted that Table 5 reports only the total-score comparison for the 15 sampled reports, whereas the consistency statistics in Table 6 are based on the 495 paired tertiary-indicator observations. On this basis, this study uses the Pearson correlation coefficient, the Spearman rank correlation coefficient, the paired-samples t-test, the intraclass correlation coefficient (ICC) [54], and the mean absolute error (MAE) [55] to assess the consistency between the LLM-based scores and the manual scores. The analysis is then further extended to the seven primary indicators in order to examine the stability of the LLM’s scoring performance across different dimensions. The detailed results are reported in Table 5, Table 6 and Table 7.
From the comparison of total scores, the LLM-based scores show a high degree of consistency with the manual scores. As shown in Table 5, with the exception of two sampled reports—Yunnan Yunwei (2022) and Yunnan Coal & Energy (2024)—the LLM-based score is 1 point lower than the manual score for all other sampled reports, with no substantial deviation observed. For example, the scores for Sinopec (2022) are 47 and 48, respectively; those for PetroChina (2023) are 53 and 54, respectively; and those for Sinopec Shanghai Petrochemical (2023) are 51 and 52, respectively.
Table 6 further reports the consistency test results based on 495 paired observations at the tertiary-indicator level. The Pearson and Spearman correlation coefficients are both 0.975 and are statistically significant at the 1% level, indicating that the LLM-based scores and the manual scores are highly consistent in terms of both score variation and sample ranking. The paired-samples t-test yields t = −3.007 (p = 0.003), suggesting that the LLM-based scores are marginally lower than the manual scores overall. The ICC of 0.974 indicates a high degree of absolute agreement between the two scoring approaches. The MAE of 0.0384 further suggests that the average absolute deviation between the LLM-based scores and the manual scores is small at the tertiary-indicator level.
Table 7 shows that the results at the primary-indicator level are broadly consistent with those at the total-score level. Across all seven dimensions—understandability, reliability, comparability, relevance, completeness, timeliness, and industry specificity—the Pearson correlation coefficients and Spearman rank correlation coefficients range from 0.976 to 1.000 and are all statistically significant at the 1% level. This indicates that the LLM-based scores remain highly consistent with the manual scores across all dimensions, demonstrating overall stability in scoring performance.
Overall, the differences between the LLM-based scores and the manual scores are small, and the degree of consistency between them is high. At the same time, the paired-samples t-test indicates that the LLM-based scores are, on average, slightly lower than the manual scores. These results suggest that the scoring procedure developed in this study has good reliability and can maintain a high level of agreement with manual scoring under the predefined evaluation criteria, while also exhibiting a modest downward scoring tendency that should be taken into account in interpretation.
Although all seven primary-indicator dimensions show high consistency with manual scoring, the “Industry Specificity” dimension yields the lowest agreement coefficients among them. This does not indicate weak performance in an absolute sense, since its Pearson and Spearman correlations remain above 0.97, but it may suggest that industry-specific disclosure items are comparatively more difficult to evaluate consistently. This is likely because such disclosures often involve technically complex and dispersed information, including Scope 3 emissions, supply chain carbon management, low-carbon technology, and transition-related social arrangements.

4. Results

This section reports measurement-oriented descriptive evidence on CIDQ under the proposed evaluation framework. Because the present study is designed as a framework-construction and measurement study rather than as a hypothesis-testing study, the results focus on the distribution, annual changes, firm-level heterogeneity, and dimension-level characteristics of the constructed CIDQ index.

4.1. Overall Analysis

Table 8 reports the descriptive statistics of the AI-CIDQ scores for the full sample. The statistics reported in Table 8 are intended to characterize the observed distribution of CIDQ in the study sample, including its central tendency, dispersion, and shape, rather than to provide inferential estimates of population parameters.
The mean score is 34.02, the median is 35.00, the standard deviation is 14.98, the minimum is 7.00, and the maximum is 56.00. The 25th and 75th percentiles are 24.00 and 48.00, respectively. Given that the theoretical maximum of the index is 66, the sample mean accounts for only 51.55% of the upper limit. This result indicates that the overall level of CIDQ in the petroleum and petrochemical industry remains relatively limited. At the same time, the score range is wide, and the interquartile range reaches 24 points, indicating substantial differences in disclosure quality across firms.

4.2. Annual Analysis

To examine changes in CIDQ during the study period, this study reports annual descriptive statistics of the AI-CIDQ scores in Table 9. These statistics are intended to characterize temporal variation within the observed sample under the proposed evaluation framework. Accordingly, the year-to-year changes are interpreted as measurement-oriented descriptive evidence of how the constructed index evolved over time, rather than as the outcome of formal repeated-measures hypothesis testing.
The annual statistics show that the CIDQ of the sample firms exhibited a continuous upward trend from 2022 to 2024. The mean score increased from 29.07 in 2022 to 35.40 in 2023 and further to 37.60 in 2024, representing a cumulative increase of 8.53 points, or 29.34%, over the three-year period. The median also rose from 29.00 to 41.00, indicating that the improvement in disclosure quality was not driven solely by a small number of high-scoring firms, but reflected an overall improvement across the sample. In terms of dispersion, the differences in scores across firms showed some degree of convergence. The standard deviation declined from 16.30 in 2022 to 13.72 in 2024, while the minimum score increased from 7.00 to 11.00, suggesting that firms with relatively low levels of disclosure also improved. The maximum score rose from 51.00 to 56.00, indicating that higher-scoring firms continued to improve on the basis of their already relatively strong performance. Overall, during the study period, the disclosure quality of the sample firms was characterized by an overall upward trend, narrowing disparities, and persistent heterogeneity.
Figure 2 illustrates the annual trend in mean CIDQ scores. The largest increase occurred from 2022 to 2023, suggesting that this was the period of fastest improvement among the sample firms. From 2023 to 2024, the mean score continued to rise, but at a slower pace.
Figure 3 provides further evidence of this trend. The boxplots show an upward shift in the score distribution over the three years, although the differences across firms did not disappear. Overall, the CIDQ of China’s A-share petroleum and petrochemical firms improved continuously from 2022 to 2024. However, by 2024, the mean score had reached only 56.97% of the theoretical maximum, indicating that the industry as a whole remained in a transitional stage from basic disclosure toward higher-quality disclosure.
The upward trend in annual mean scores may reflect several overlapping factors. These include the continued strengthening of climate-related regulatory expectations in China, firms’ accumulated experience in carbon-related reporting, and the gradual standardization of ESG and sustainability disclosure practices. Taken together, these factors may have contributed to the steady improvement in CIDQ observed during the sample period.

4.3. Firm-Level Heterogeneity in CIDQ

To further examine firm-level differences in CIDQ, this study reports the annual AI-CIDQ scores of the 15 sample firms for 2022–2024, together with their three-year average scores, in Table 10. The firm-level comparison is intended to describe cross-firm variation in the constructed CIDQ index within the observed sample. The descriptive labels used in this subsection are based on observed score levels and rankings, rather than on statistically validated clusters derived from formal group-comparison tests.
At the firm level, the results indicate noticeable heterogeneity in CIDQ. Sinopec, PetroChina, Sinopec Shanghai Petrochemical, Meijin Energy, and CNOOC rank at the top, with three-year average scores of 52.67, 52.33, 51.33, 48.00, and 47.67, respectively. Relative to the full-sample mean of 34.02, these five firms score 18.65, 18.31, 17.31, 13.98, and 13.65 points higher, respectively, indicating that these higher-scoring firms performed above the sample average in descriptive terms. Among them, the score ranges of PetroChina, Sinopec Shanghai Petrochemical, Meijin Energy, and CNOOC over the three years are only 2, 1, 2, and 3 points, respectively, suggesting that their disclosure performance is not only relatively strong but also comparatively stable.
Table 10 reports the detailed firm-level scores and three-year averages.
By contrast, Yunnan Yunwei, Blue Flame Holdings, and Yunnan Coal & Energy record three-year average scores of only 10.67, 14.00, and 19.33, respectively, which are 23.35, 20.02, and 14.69 points below the sample mean. Yunnan Yunwei records scores of 11, 10, and 11 over the three years, with a maximum fluctuation of only 1 point, indicating that it remained at a relatively low disclosure level throughout the sample period, with little sign of improvement. Blue Flame Holdings increases from 7 to 24, representing a cumulative increase of 17 points, but its 2024 score still reaches only 63.83% of the 2024 sample mean of 37.60. Yunnan Coal & Energy records scores of 17, 26, and 15, respectively; with its 2024 score 11 points lower than that of 2023, indicating relatively large fluctuations. These results suggest that some low-scoring firms still have a weak foundation for carbon information disclosure, and that their improvement lacks continuity.
The middle tier also shows considerable variation. Shenyang Chemical, North Huajin, Shanxi Coking, Guanghui Energy, and Kailuan Energy Chemical record three-year average scores of 37.00, 34.33, 33.00, 32.33, and 32.33, respectively, which are close to or slightly below the sample mean. Among them, Kailuan Energy Chemical increases from 18 to 44, representing a cumulative increase of 26 points. Yueyang Xingchang increased from 9 to 39, with a cumulative increase of 30 points over the three years, representing the largest increase in the full sample. These results indicate that some medium- and low-scoring firms began to strengthen carbon information disclosure markedly during the study period, but had not yet developed a stable pattern of high-quality disclosure.
In terms of inter-firm gaps, the top-ranked Sinopec records a three-year average score of 52.67, whereas the bottom-ranked Yunnan Yunwei records only 10.67, producing a difference of 42.00 points; the former is approximately 4.94 times the latter. Looking only at 2024, the highest score is 56 and the lowest is 11, producing a difference of 45 points; the former is approximately 5.09 times the latter. Overall, the results reveal substantial firm-level heterogeneity in CIDQ among China’s petroleum and petrochemical enterprises. Higher-quality disclosure is concentrated among a relatively small number of higher-scoring firms, whereas medium- and low-scoring firms, despite some improvement, differ considerably in both the extent and stability of that improvement. A balanced and broadly consistent disclosure pattern has not yet emerged within the industry. The persistently high scores of higher-scoring firms such as China Petroleum & Chemical Corporation and PetroChina Company Limited may reflect their relatively stronger governance foundations, more mature data collection and management systems, and greater experience in continuous environmental and climate-related disclosure. By contrast, firms with relatively low scores may still face constraints in disclosure capability, internal reporting infrastructure, and the continuity of carbon-related information management, which may limit both the level and stability of their disclosure performance.

5. Discussion

Taken together, the results show that the carbon information disclosure quality of China’s A-share petroleum and petrochemical firms improved from 2022 to 2024, but the overall disclosure level remained limited and firm-level differences persisted. This pattern suggests that the industry is still moving from basic carbon-related disclosure toward more complete, comparable, and verifiable disclosure. In the petroleum and petrochemical industry, carbon-related reporting often involves technically complex emissions accounting, value-chain-related information, transition-risk disclosure, and industry-specific governance arrangements. These features increase the difficulty of producing high-quality disclosure, especially for firms with weaker internal data systems or less experience in sustainability reporting.
The improvement observed during the sample period may be related to several overlapping factors, including stronger climate-related disclosure expectations in China, firms’ accumulated experience in ESG and sustainability reporting, and the gradual standardization of non-financial reporting practices. At the same time, the persistent differences across firms suggest that disclosure quality is not determined only by report length or the amount of disclosed information. Rather, it may also depend on firms’ governance foundations, internal data collection and management capacity, and the continuity of carbon-related disclosure practices. Higher-scoring firms such as China Petroleum & Chemical Corporation and PetroChina Company Limited may be better able to organize carbon-related data and maintain consistent reporting practices, whereas firms with relatively low scores may still face constraints in data availability, internal reporting infrastructure, and cross-departmental coordination. These findings are broadly consistent with prior studies showing that carbon disclosure is influenced by firms’ environmental performance, governance structures, external institutional pressures, and stakeholder expectations, and that climate-related disclosure may be associated with improvements in environmental governance and disclosure practices over time [10,16,17,18,19,20,21]. The present study adds industry-specific evidence by showing that, in a high-emission sector with technically complex and value-chain-related disclosure requirements, firm-level differences in disclosure quality may remain substantial even as reporting practices become more common.
The results can also be interpreted in light of legitimacy theory and stakeholder theory. From a legitimacy perspective, the improvement in CIDQ may reflect firms’ efforts to maintain social and regulatory acceptance as climate governance and sustainability disclosure expectations become stronger. From a stakeholder perspective, carbon disclosure provides a channel through which firms communicate information on emissions, reduction actions, climate-related risks, and transition progress to investors, regulators, communities, and other stakeholders. The persistence of firm-level differences suggests that firms differ not only in their willingness to disclose, but also in their capacity to provide disclosure that is specific, consistent, and supported by verifiable information [15,21].
Viewed against existing climate-disclosure frameworks, the weaker areas identified in this study are closely related to the core dimensions emphasized by TCFD and IFRS S2, including governance, strategy, risk management, and metrics and targets. The proposed framework should therefore be understood not as a substitute for these broader frameworks, but as an industry-specific operationalization of their key disclosure expectations. In the Chinese context, where sustainability reporting requirements have recently become more standardized, such a framework may provide a more detailed diagnostic tool for high-emission industries. More specifically, regulators and standard setters may use indicator-level results to identify disclosure items that require more targeted guidance, such as emission boundaries, Scope 3 emissions, calculation methods, transition-risk disclosure, value-chain coverage, and just transition arrangements. The framework may also help translate broad sustainability reporting requirements into more concrete industry checklists, for example by encouraging firms to disclose calculation bases, historical comparability, quantitative targets, and evidence for emission-reduction measures. For stock exchanges and industry associations, the framework may provide a reference for reviewing whether high-emission firms disclose not only general commitments but also verifiable data, implementation details, and value-chain-related information. For firms, the results suggest that improving CIDQ requires not only increasing the amount of report content, but also strengthening the completeness, comparability, and verifiability of disclosed information.
Methodologically, the reliability test suggests that LLM-assisted scoring can provide relatively stable support for structured CIDQ evaluation when explicit scoring rules, structured output requirements, textual evidence, and manual review are retained. At the same time, the LLM should be understood as an assistive tool rather than as an autonomous evaluator. This boundary is important because LLM outputs may contain unsupported interpretations or hallucinated inferences when processing lengthy and technically complex ESG reports. The current validation also focuses on consistency with manual benchmark scores and should not be interpreted as proving superiority over keyword retrieval, conventional text-classification methods, or other LLMs. Future applications of the framework should therefore continue to combine automated scoring with evidence-location requirements and researcher verification.
Overall, the findings provide measurement-oriented and industry-specific evidence on the current state of CIDQ in China’s petroleum and petrochemical industry. They show that disclosure quality improved during the sample period, but that the industry still faces challenges in moving from basic disclosure toward more complete, comparable, and verifiable disclosure. The findings should therefore be read as industry-specific and temporally comparative evidence rather than as causal or broadly generalizable conclusions.

6. Conclusions

This study developed an industry-specific framework for evaluating carbon information disclosure quality in China’s petroleum and petrochemical industry and applied an LLM-assisted scoring procedure to 45 firm-year observations from 2022 to 2024. The results show that CIDQ improved during the sample period, but the overall disclosure level remained relatively limited and substantial differences persisted across firms. These findings indicate that the industry has made progress in carbon-related reporting, while still facing challenges in providing complete, comparable, and verifiable disclosure, particularly for technically complex and value-chain-related items.
The study contributes to CIDQ research in two main respects. First, it develops a structured 7/15/33 evaluation framework that combines general disclosure-quality dimensions with the characteristics of the petroleum and petrochemical industry, including Scope 3 emissions, value-chain coverage, supply chain carbon management, low-carbon technology development, logistics emission optimization, and just transition. Second, it demonstrates that LLM-assisted scoring can support rule-based disclosure evaluation when explicit scoring criteria, structured output requirements, textual evidence, and manual review are retained. In this sense, the study provides a methodological reference for structured CIDQ evaluation in high-emission industries.
The study also has practical implications. For regulators and standard setters, the framework may serve as a diagnostic tool for identifying weak areas in carbon disclosure among petroleum and petrochemical firms, especially in value-chain-related and transition-related disclosure areas. It may also provide a reference for developing more detailed industry-specific disclosure guidance within the broader movement toward standardized sustainability reporting. For firms, the findings point to the need to improve internal carbon-data management and to provide more specific, consistent, and evidence-supported disclosure, rather than merely increasing the length or generality of report content.
Several limitations should be noted. First, the sample is limited to 15 A-share listed petroleum and petrochemical firms in China. Although the sample represents the firms that met the study’s disclosure-based inclusion criteria during 2022–2024, the external validity of the findings still requires further examination. Therefore, the observed annual changes and firm-level differences should be interpreted as measurement results within the defined sample, rather than as population-level or causal evidence for the entire petroleum and petrochemical industry. Future research may apply the framework to larger samples, longer time periods, other high-emission industries, or different country contexts to examine its broader applicability. Second, the construction of the index involves researcher-defined indicator selection, scoring boundaries, and equal-weight aggregation. Although these choices were made to preserve transparency, interpretability, and replicability, alternative weighting schemes or different indicator groupings may affect aggregate scores and firm rankings. Future research may therefore conduct sensitivity analyses and compare equal weighting with expert-based, PCA-based, AHP-based, or other weighting approaches where broader data and different research objectives are available. Third, the validation of the scoring results can be further strengthened. The present study compares LLM-based scores with manual benchmark scores, but it does not use a multi-coder human validation design or repeated-run stability tests under identical prompts. It also does not provide systematic comparisons with keyword retrieval, conventional text-classification methods, or other LLMs. In addition, LLM-assisted scoring may be affected by prompt sensitivity, model-version changes, context loss in long reports, hallucinated or unsupported interpretations, and a slight downward scoring tendency relative to manual scores. For this reason, the LLM-based procedure should be used as an assistive tool under explicit rules and evidence verification, rather than as a replacement for expert judgment. Future research may extend the validation design by involving multiple independent coders, testing model stability under different settings, comparing alternative automated methods, and examining the sensitivity of aggregated CIDQ scores to different weighting schemes. Finally, because this study is designed as a framework-construction and measurement study, the findings should be interpreted as measurement-oriented and industry-specific evidence rather than as causal conclusions about the determinants or consequences of CIDQ.

Author Contributions

M.Y. was responsible for data preparation and design, formal analysis, original draft writing, and manuscript preparation. M.Z. and M.Y. contributed to conceptualization, study design, manuscript drafting, and project supervision. All authors participated in the conceptualization and writing of this paper. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the National Social Science Fund of China, grant number 25BJY104, and the Philosophy and Social Science Research in Universities of Jiangsu Province, grant number 2023SJYB0152.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

The original contributions presented in this study are included in the article. Further inquiries can be directed to the corresponding author(s).

Acknowledgments

The DeepSeek-V3.2 model, accessed through the DeepSeek–chat interface, was used as an auxiliary research tool in the indicator-level scoring of corporate ESG, social responsibility, and sustainability reports under predefined scoring rules. The model was not used to generate the manuscript text, and all interpretation, writing, and revision of the manuscript were completed by the authors.

Conflicts of Interest

The authors declare no conflicts of interest.

Appendix A. Representative Prompt Structure Used for Indicator-Level Scoring

This appendix presents a representative prompt structure used in the indicator-level scoring process. The prompt was designed on the basis of the predefined indicator description, the corresponding 0–1–2 scoring rule, and the requirement that the model return a structured result. In the actual evaluation process, the full machine-readable report text was entered together with the indicator-specific prompt.
Table A1. Representative prompt structure used for indicator-level scoring.
Table A1. Representative prompt structure used for indicator-level scoring.
ComponentContent
Role/TaskPlease act as an expert in evaluating carbon information disclosure quality and assess the corporate report strictly according to the predefined criteria.
Evaluation Indicator{Level 1 Indicator}–{Level 2 Indicator}–{Level 3 Indicator}
Indicator
Description
{Indicator description}
Special NoteFor selected indicators, additional decision rules were included in the prompt in order to improve scoring consistency.
Example 1Explanation of Professional Terminology: Terms such as “Scope 1 emissions”, “direct emissions”, and “direct greenhouse gas emissions” were treated as equivalent expressions. Similar equivalence rules were applied to Scope 2 emissions, Scope 3 emissions, and carbon footprint terminology.
Example 2Emission Increases or Violation Incidents: Negative statements such as “no violations occurred” or “no environmental penalties were imposed” were treated as a form of relevant disclosure under this indicator.
Scoring Rule (0){Rule for 0}
Scoring Rule (1){Rule for 1}
Scoring Rule (2){Rule for 2}
Corporate Report Text{Full machine-readable report text inserted here in the actual evaluation process}
Table A2. Instructions and required output fields for indicator-level scoring.
Table A2. Instructions and required output fields for indicator-level scoring.
ComponentContent
Instruction 1The score must be supported by direct textual evidence from the report.
Instruction 2The model should pay attention to equivalent terminology and negative expressions where relevant.
Instruction 3A score of 0 should be assigned if no relevant information is disclosed.
Instruction 4A score of 1 should be assigned if the disclosure is only qualitative or general and lacks verifiable quantitative support.
Instruction 5A score of 2 should be assigned if the disclosure includes quantitative data, measurable targets, or other verifiable evidence directly relevant to the indicator.
Instruction 6The evidence must be quoted from the report text.
Output Field 1“score”: 0, 1, or 2
Output Field 2“reason”: brief explanation of why the disclosure meets the scoring rule
Output Field 3“evidence”: direct quotation or extracted textual evidence from the report
Output Field 4“evidence_location”: location of the evidence in the report
In the actual implementation, the prompt was generated separately for each tertiary indicator. The report text was converted into machine-readable text and entered together with the indicator-specific prompt so that the model could identify relevant information across different sections of the same report.

Appendix B. Operational Scoring Guide for the 33 Tertiary Indicators

This appendix provides the operational scoring guide for all 33 tertiary indicators. For each indicator, the tables report the indicator content, the 0–1–2 scoring criteria, and a brief boundary note to improve scoring transparency and reproducibility. The guide was developed strictly on the basis of the predefined evaluation framework used in this study.
Table A3. Operational scoring guide for tertiary indicators under A. Understandability.
Table A3. Operational scoring guide for tertiary indicators under A. Understandability.
CodeTertiary IndicatorIndicator
Description
Score 0Score 1Score 2Boundary/
Operational Note
A11Combination of Data and ChartsWhether carbon information is presented in multiple forms such as data tables and charts so as to improve readability.Only textual description is provided, with no data or charts.Data are provided, but charts are absent or very limited in form.Data are presented together with multiple charts or visual forms in a clear and intuitive way.Pure narrative disclosure was not sufficient. Quantitative data without visual presentation was coded as 1 rather than 2.
A12Explanation of Professional TerminologyWhether the firm explains carbon-related professional terms such as Scope 1, Scope 2, and Scope 3 emissions.Professional terms are used without explanation, or no carbon-related terms are mentioned.Some major terms are explained, including equivalent expressions.All professional terms used in the report, including equivalent expressions, are explained clearly and in detail.Partial explanation of key terms was coded as 1; comprehensive and explicit explanation across terms was coded as 2.
A21Index/Table of ContentsWhether the report provides an index or table of contents to help locate carbon-related information.No index or table of contents is provided.A simple index or contents list is provided, but it is not detailed enough.A detailed index or table of contents is provided, enabling rapid location of carbon-related information.A general report contents page was coded as 1 unless it clearly facilitated location of relevant carbon information.
Table A4. Operational scoring guide for tertiary indicators under B. Reliability.
Table A4. Operational scoring guide for tertiary indicators under B. Reliability.
CodeTertiary
Indicator
Indicator
Description
Score 0Score 1Score 2Boundary/
Operational Note
B11Disclosure of Calculation MethodsWhether the firm discloses carbon accounting methods and explains data sources.No accounting method is disclosed.A basic accounting framework is mentioned.Specific accounting methods and data sources are disclosed in detail.Mere mention of a framework or standard was coded as 1; method plus data-source detail was coded as 2.
B12Third-Party VerificationWhether carbon information is independently verified or assured by a third party.No third-party verification is disclosed.Third-party verification is mentioned only partially or without specifying scope.Independent third-party assurance is fully disclosed, including the verifier and verification scope.A general statement that some information was verified was coded as 1; named verifier plus scope was coded as 2.
B21Emission Increases or Violation IncidentsWhether the firm discloses negative information such as excessive emissions, penalties, or environmental incidents.No relevant information on violations, pollution, penalties, or related matters is mentioned at all.Negative information is only mentioned briefly or indirectly, including statements such as “no violations occurred”.Specific incidents are disclosed in detail together with corrective or improvement measures.Negative statements such as “no violations” were treated as relevant disclosure and coded as 1 rather than 0.
B22Risk DisclosureWhether the firm discloses carbon-related risks, such as policy risk or climate risk, with reference to TCFD-type logic.No relevant risk is disclosed.Some risks are disclosed, but not comprehensively.Multiple types of risk and corresponding response strategies are disclosed comprehensively.General environmental uncertainty language was not sufficient; identifiable carbon- or climate-related risk content was required.
Table A5. Operational scoring guide for tertiary indicators under C. Comparability.
Table A5. Operational scoring guide for tertiary indicators under C. Comparability.
CodeTertiary
Indicator
Indicator
Description
Score 0Score 1Score 2Boundary/
Operational Note
C11Cross-Period ConsistencyWhether consistent accounting methods and base years are used to support intertemporal comparison.Methods change frequently without explanation, or no consistency is discussed.Methods are broadly consistent with only minor adjustment, or consistency is mentioned without detail.Methods are fully consistent, or changes are reasonably explained, and comparative data are provided.A simple claim of consistency without showing comparable data was coded as 1.
C12Alignment with Industry StandardsWhether the disclosure is aligned with international or industry standards such as IPCC- or SASB-type frameworks.No standard is adopted.Some standards are partially adopted.The disclosure is fully aligned with relevant international or industry standards.Partial reference to standards was coded as 1; systematic alignment was coded as 2.
C21Stability of Report FormatWhether the report format is stable and facilitates comparison across periods or firms.The format is disorganized and lacks a stable structure.The format is basically stable, with some adjustments.The format is fully stable and clearly facilitates comparison.Minor layout changes did not prevent a score of 1 if the basic structure remained comparable.
C22Data StandardizationWhether carbon data are disclosed using standardized units such as tCO2e.Non-standard units are used.Standardized units are used only for part of the data.Standardized units are used consistently throughout the disclosure.Partial standardization was coded as 1; complete and consistent standardization was coded as 2.
Table A6. Operational scoring guide for tertiary indicators under D. Relevance.
Table A6. Operational scoring guide for tertiary indicators under D. Relevance.
CodeTertiary
Indicator
Indicator
Description
Score 0Score 1Score 2Boundary/
Operational Note
D11Emission Reduction StrategyWhether the firm discloses a long-term emission-reduction strategy, such as a carbon neutrality pathway.No emission-reduction strategy is disclosed.A strategy is mentioned, but it is not specific.A detailed long-term strategy and implementation pathway are disclosed.Broad strategic rhetoric without pathway detail was coded as 1.
D12Emission Reduction TargetsWhether the firm sets quantified emission-reduction targets, such as absolute or intensity-based targets.No quantified target is disclosed.A target is mentioned, but it is vague or not measurable.Clear quantified targets and timetable are disclosed.A target without measurable quantity or time frame was coded as 1 rather than 2.
D13Climate-Related GovernanceWhether the report describes board- or management-level responsibility for carbon governance.No governance mechanism is disclosed.Governance responsibility is mentioned only briefly, without board-level specificity.Board-level climate governance structure and specific responsibilities are clearly disclosed.Mention of management attention alone was coded as 1 unless concrete board-level oversight was specified.
D21Emission Reduction MeasuresWhether specific emission-reduction measures are disclosed, such as energy efficiency improvement or process optimization.No specific measures are disclosed.Some measures are disclosed, but not systematically.Various types of emission-reduction measures are disclosed systematically.Isolated examples were coded as 1; a broader and more organized set of actions was coded as 2.
D22Operation of Emission Reduction FacilitiesWhether the report describes the operation of emission-reduction facilities such as CCUS or renewable-energy equipment.No operating condition of emission-reduction facilities is disclosed.Operation is mentioned only briefly.Operating data and effectiveness are disclosed in detail.Mentioning that facilities existed was coded as 1; operational performance information was required for 2.
D23Carbon Trading and OffsettingWhether the firm participates in carbon trading or uses offset projects.No carbon-market participation is disclosed.Participation is disclosed, but insufficiently.Trading data and strategy are disclosed adequately and in detail.Mere participation without transaction or strategy detail was coded as 1.
D31Scope 1 EmissionsWhether the firm discloses direct greenhouse gas emissions data.Scope 1 emissions are not disclosed.A total amount is disclosed, or Scope 1 is mentioned only qualitatively.Emissions from specific sources are disclosed in detail with quantitative values.General or aggregate mention was coded as 1; source-level quantified disclosure was coded as 2.
D32Scope 2 EmissionsWhether the firm discloses indirect emissions from purchased electricity or heat.Scope 2 emissions are not disclosed.Total Scope 2 data are disclosed, or Scope 2 is only described qualitatively.Scope 2 emissions are disclosed in detail with quantitative values and explanation of electricity source.Quantified totals without contextual detail were coded as 1; fuller explanation and quantified disclosure was coded as 2.
D33Scope 3 EmissionsWhether the firm discloses value-chain indirect emissions such as supply chain or product-use emissions.Scope 3 emissions are not disclosed.Only part of Scope 3 emissions is disclosed.All major Scope 3 categories are disclosed comprehensively.Partial disclosure of selected categories was coded as 1.
D34Product Carbon FootprintWhether the firm discloses carbon-footprint data for major products.No product carbon footprint is disclosed.Carbon footprint is disclosed only for some products, or related actions are mentioned without complete data.Complete carbon-footprint disclosure is provided for major products.Action-oriented statements such as carrying out product carbon-footprint accounting were coded as 1 if full footprint disclosure was absent.
D35Carbon Intensity IndicatorsWhether the firm discloses carbon-intensity indicators, such as emissions per unit of output or revenue.No intensity indicator is disclosed.Basic intensity indicators are disclosed, or the concept is mentioned without sufficient detail.Multi-dimensional and standardized intensity indicators are disclosed.A single simple intensity metric was usually coded as 1; broader standardized intensity disclosure was coded as 2.
Table A7. Operational scoring guide for tertiary indicators under E. Completeness.
Table A7. Operational scoring guide for tertiary indicators under E. Completeness.
CodeTertiary
Indicator
Indicator
Description
Score 0Score 1Score 2Boundary/
Operational Note
E11Full Value Chain CoverageWhether carbon information covers the whole value chain, including upstream and downstream stages.Only own operations, or less, are covered.Part of the value chain is covered, such as upstream and own operations, but downstream use is missing.The full value chain is covered, including upstream, own operations, and downstream use stages.Coverage beyond direct operations but without downstream use-stage disclosure was coded as 1.
E12All Emission SourcesWhether all major emission sources are disclosed.Major emission sources are omitted.Main sources are covered, but not all major sources.All major emission sources are covered.Coverage of only the most visible sources was coded as 1 if material sources were still missing.
E21Data by Department/RegionWhether carbon data are disclosed by department, region, or business unit.Only company-level aggregate data are disclosed, or no such breakdown is mentioned.Some departmental or regional breakdown is mentioned, but concrete data are incomplete.Complete carbon data are disclosed by department, region, or business segment.A conceptual mention of segment disclosure without actual segmented data was coded as 1.
E22Historical Data ComparisonWhether the report provides historical data for trend analysis.No historical comparison is provided.Historical comparison is mentioned, but no concrete data are given.Comparative data for two years or more are provided.Trend language without actual comparative figures was coded as 1 rather than 2.
Table A8. Operational scoring guide for tertiary indicators under F. Timeliness.
Table A8. Operational scoring guide for tertiary indicators under F. Timeliness.
CodeTertiary
Indicator
Indicator
Description
Score 0Score 1Score 2Boundary/
Operational Note
F11Timeliness of Report DisclosureWhether carbon information is disclosed within a reasonable period after the end of the fiscal year.Disclosure is delayed by more than six months.Disclosure is delayed by about three to six months.Disclosure is timely or only slightly delayed.This indicator was judged against the timing of release rather than content richness.
F12Regular UpdatesWhether carbon information is updated regularly, for example on an annual basis.Disclosure is irregular.Disclosure is basically regular, but with interruption.Disclosure is updated strictly and regularly.Regular annual updating without interruption was required for 2.
Table A9. Operational scoring guide for tertiary indicators under G. Industry Specificity.
Table A9. Operational scoring guide for tertiary indicators under G. Industry Specificity.
CodeTertiary
Indicator
Indicator
Description
Score 0Score 1Score 2Boundary/
Operational Note
G11Low-Carbon Technology R&DWhether the firm discloses R&D investment in low-carbon technologies such as hydrogen, biofuels, or CCUS.No relevant R&D is disclosed.Basic R&D information is disclosed, but without specific content.Specific R&D inputs, achievements, and applications are disclosed in detail.A generic statement that low-carbon R&D existed was coded as 1.
G21Supplier Carbon ManagementWhether the firm discloses carbon-management requirements or cooperation for suppliers.No supplier carbon-management measure is disclosed.Basic supplier-management requirements or concepts are mentioned.Systematic supplier carbon-management requirements and measures are disclosed, with concrete data.Mention of a green supply chain idea alone was coded as 1 unless concrete management content was provided.
G22Logistics Emission OptimizationWhether the firm discloses logistics-related emission-reduction measures such as transport optimization.No logistics emission-reduction measure is disclosed.Logistics emission-reduction measures are mentioned, but not in detail.Detailed disclosure of logistics optimization outcomes or logistics-emission data is provided.Simple mention of logistics optimization was coded as 1; quantified effect or performance detail was coded as 2.
G31Community CommunicationWhether the firm discloses communication with communities regarding carbon-related projects and impacts.No community communication is disclosed.Basic communication is mentioned, but without record or mechanism.Systematic communication with feedback mechanisms is disclosed.General statements on community communication without a clear communication mechanism were coded as 1.
G32Just TransitionWhether the firm discloses a just-transition plan concerning the social impacts of energy transition on employees and communities.No social-transition impact is considered.Just transition is mentioned only briefly.A detailed just-transition plan is disclosed.General statements on employees or society were coded as 1 only when linked to transition-related impacts.

References

  1. Borghei, Z. Carbon Disclosure: A Systematic Literature Review. Account. Financ. 2021, 61, 5255–5280. [Google Scholar] [CrossRef]
  2. Hahn, R.; Kühnen, M. Determinants of Sustainability Reporting: A Review of Results, Trends, Theory, and Opportunities in an Expanding Field of Research. J. Clean. Prod. 2013, 59, 5–21. [Google Scholar] [CrossRef]
  3. Mateo-Márquez, A.J.; González-González, J.M.; Zamora-Ramírez, C. Countries’ Regulatory Context and Voluntary Carbon Disclosures. Sustain. Account. Manag. Policy J. 2020, 11, 383–408. [Google Scholar] [CrossRef]
  4. Bazhair, A.H.; Khatib, S.F.A.; Al Amosh, H. Taking Stock of Carbon Disclosure Research While Looking to the Future: A Systematic Literature Review. Sustainability 2022, 14, 13475. [Google Scholar] [CrossRef]
  5. Pitrakkos, P.; Maroun, W. Evaluating the Quality of Carbon Disclosures. Sustain. Account. Manag. Policy J. 2020, 11, 553–589. [Google Scholar] [CrossRef]
  6. Liu, Y.S.; Zhou, X.; Yang, J.H.; Hoepner, A.G.F.; Kakabadse, N. Carbon Emissions, Carbon Disclosure and Organizational Performance. Int. Rev. Financ. Anal. 2023, 90, 102846. [Google Scholar] [CrossRef]
  7. Guidelines for Industry Classification of Listed Companies (2012 Revision). CSRC Announcement No. 31 [2012]; China Securities Regulatory Commission: Beijing, China, 2012.
  8. Cormier, D.; Beauchamp, C. Market Incidence of Carbon Information Disclosure in the Oil and Gas Industry: The Mediating Role of Financial Analysts and Governance. J. Financ. Report. Account. 2021, 19, 901–920. [Google Scholar] [CrossRef]
  9. Zhao, J.J.; Wang, X.; Yang, D.C. Climate Change Risk Disclosure and Accounting Choice: Evidence from U.S. Oil and Gas Companies. Int. J. Bus. Econ. 2023, 8, 89–106. [Google Scholar] [CrossRef]
  10. Zhang, S. Climate Change Disclosure and Carbon Performance of Chinese Listed Companies: Exploring the Moderating Effects of Climate Governance and Corporate Environmental Governance. Front. Clim. 2024, 6, 1469899. [Google Scholar] [CrossRef]
  11. Mousavian Anaraki, S.A.; Croce, D.; Basili, R. Large Language Models for Sustainability Reporting: A Systematic Review and Research Agenda. Sustain. Futures 2025, 10, 101494. [Google Scholar] [CrossRef]
  12. Wu, Y.; Hu, P.; Wang, D.D. The AI Annotator: Large Language Models’ Potential in Scoring Sustainability Reports. Systems 2025, 13, 899. [Google Scholar] [CrossRef]
  13. Kolk, A.; Pinkse, J. Business Responses to Climate Change: Identifying Emergent Strategies. Calif. Manag. Rev. 2005, 47, 6–20. [Google Scholar] [CrossRef]
  14. Kolk, A.; Levy, D.; Pinkse, J. Corporate Responses in an Emerging Climate Regime: The Institutionalization and Commensuration of Carbon Disclosure. Eur. Account. Rev. 2008, 17, 719–745. [Google Scholar] [CrossRef]
  15. Stanny, E. Voluntary Disclosures of Emissions by U.S. Firms. Bus. Strategy Environ. 2013, 22, 145–158. [Google Scholar] [CrossRef]
  16. Giannarakis, G.; Zafeiriou, E.; Sariannidis, N. The Impact of Carbon Performance on Climate Change Disclosure. Bus. Strategy Environ. 2017, 26, 1078–1094. [Google Scholar] [CrossRef]
  17. Liao, L.; Luo, L.; Tang, Q. Gender Diversity, Board Independence, Environmental Committee and Greenhouse Gas Disclosure. Br. Account. Rev. 2015, 47, 409–424. [Google Scholar] [CrossRef]
  18. Luo, L.; Tang, Q.; Lan, Y.-C. Comparison of Propensity for Carbon Disclosure between Developing and Developed Countries: A Resource Constraint Perspective. Account. Res. J. 2013, 26, 6–34. [Google Scholar] [CrossRef]
  19. Xu, W.; Sun, Z.; Ni, H. Transparency Pays: How Carbon Emission Disclosure Lowers Cost of Capital. Econ. Anal. Policy 2024, 83, 165–177. [Google Scholar] [CrossRef]
  20. Steindl, T.; Habermann, F.; Küster, S. Carbon Disclosures and Information Asymmetry: Empirical Evidence on the Importance of Text in Understanding Numerical Emission Allowance Disclosures. J. Ind. Ecol. 2024, 28, 1883–1899. [Google Scholar] [CrossRef]
  21. Shao, J.; He, Z. How Does Social Media Drive Corporate Carbon Disclosure? Evidence from China. Front. Ecol. Evol. 2022, 10, 971077. [Google Scholar] [CrossRef]
  22. Patten, D.M. The Relation between Environmental Performance and Environmental Disclosure: A Research Note. Account. Organ. Soc. 2002, 27, 763–773. [Google Scholar] [CrossRef]
  23. Clarkson, P.M.; Li, Y.; Richardson, G.D.; Vasvari, F.P. Revisiting the Relation between Environmental Performance and Environmental Disclosure: An Empirical Analysis. Account. Organ. Soc. 2008, 33, 303–327. [Google Scholar] [CrossRef]
  24. Lombard, M.; Snyder-Duch, J.; Bracken, C.C. Content Analysis in Mass Communication: Assessment and Reporting of Intercoder Reliability. Hum. Commun. Res. 2002, 28, 587–604. [Google Scholar] [CrossRef]
  25. Maibaum, F.; Kriebel, J.; Foege, J.N. Selecting Textual Analysis Tools to Classify Sustainability Information in Corporate Reporting. Decis. Support Syst. 2024, 183, 114269. [Google Scholar] [CrossRef]
  26. Li, Q.; Peng, H.; Li, J.; Xia, C.; Yang, R.; Sun, L.; Yu, P.S.; He, L. A Survey on Text Classification: From Traditional to Deep Learning. ACM Trans. Intell. Syst. Technol. 2022, 13, 31. [Google Scholar] [CrossRef]
  27. Palanivinayagam, A.; El-Bayeh, C.Z.; Damaševičius, R. Twenty Years of Machine-Learning-Based Text Classification: A Systematic Review. Algorithms 2023, 16, 236. [Google Scholar] [CrossRef]
  28. Giannarakis, G.; Andronikidis, A.; Sariannidis, N. Determinants of Environmental Disclosure: Investigating New and Conventional Corporate Governance Characteristics. Ann. Oper. Res. 2020, 294, 87–105. [Google Scholar] [CrossRef]
  29. Luo, L.; Tang, Q.; Fan, H.; Ayers, J. Corporate Carbon Assurance and the Quality of Carbon Disclosure. Account. Financ. 2023, 63, 657–690. [Google Scholar] [CrossRef]
  30. Kalu, J.U.; Aliagha, G.U.; Buang, A. A Review of Economic Factors Influencing Voluntary Carbon Disclosure in the Property Sector of Developing Economies. IOP Conf. Ser. Earth Environ. Sci. 2016, 30, 012010. [Google Scholar] [CrossRef]
  31. Faisal, F.; Andiningtyas, E.D.; Achmad, T.; Haryanto, H.; Meiranto, W. The Content and Determinants of Greenhouse Gas Emission Disclosure: Evidence from Indonesian Companies. Corp. Soc. Responsib. Environ. Manag. 2018, 25, 1397–1406. [Google Scholar] [CrossRef]
  32. Du, K.; Mao, R.; Xing, F.; Mengaldo, G.; Cambria, E. Language Models for Environmental, Social, and Governance Analysis: A Review. Inf. Process. Manag. 2026, 63, 104596. [Google Scholar] [CrossRef]
  33. Zou, Y.; Shi, M.; Chen, Z.; Deng, Z.; Lei, Z.; Zeng, Z.; Yang, S.; Tong, H.; Xiao, L.; Zhou, W. ESGReveal: An LLM-Based Approach for Extracting Structured Data from ESG Reports. J. Clean. Prod. 2025, 489, 144572. [Google Scholar] [CrossRef]
  34. Li, F. The Information Content of Forward-Looking Statements in Corporate Filings—A Naïve Bayesian Machine Learning Approach. J. Account. Res. 2010, 48, 1049–1102. [Google Scholar] [CrossRef]
  35. Loughran, T.; McDonald, B. Textual Analysis in Accounting and Finance: A Survey. J. Account. Res. 2016, 54, 1187–1230. [Google Scholar] [CrossRef]
  36. Kotsantonis, S.; Serafeim, G. Four Things No One Will Tell You About ESG Data. J. Appl. Corp. Finance 2019, 31, 50–58. [Google Scholar] [CrossRef]
  37. Berg, F.; Kölbel, J.F.; Rigobon, R. Aggregate Confusion: The Divergence of ESG Ratings. Rev. Financ. 2022, 26, 1315–1344. [Google Scholar] [CrossRef]
  38. Mashrur, A.; Luo, W.; Zaidi, N.A.; Robles-Kelly, A. Machine Learning for Financial Risk Management: A Survey. IEEE Access 2020, 8, 203203–203223. [Google Scholar] [CrossRef]
  39. Dilling, P.F.A.; Harris, P.; Caykoylu, S. The Impact of Corporate Characteristics on Climate Governance Disclosure. Sustainability 2024, 16, 1962. [Google Scholar] [CrossRef]
  40. Bingler, J.A.; Kraus, M.; Leippold, M.; Webersinke, N. Cheap Talk and Cherry-Picking: What ClimateBert Has to Say on Corporate Climate Risk Disclosures. Financ. Res. Lett. 2022, 47, 102776. [Google Scholar] [CrossRef]
  41. Gentzkow, M.; Kelly, B.; Taddy, M. Text as Data. J. Econ. Lit. 2019, 57, 535–574. [Google Scholar] [CrossRef]
  42. Blei, D.M. Probabilistic Topic Models. Commun. ACM 2012, 55, 77–84. [Google Scholar] [CrossRef]
  43. Devlin, J.; Chang, M.-W.; Lee, K.; Toutanova, K. BERT: Pre-training of Deep Bidirectional Transformers for Language Understanding. In Proceedings of the 2019 Conference of the North American Chapter of the Association for Computational Linguistics: Human Language Technologies (NAACL-HLT); Association for Computational Linguistics: Minneapolis, MN, USA, 2019; pp. 4171–4186. [Google Scholar] [CrossRef]
  44. Hassan, T.A.; Hollander, S.; van Lent, L.; Tahoun, A. Firm-Level Political Risk: Measurement and Effects. Q. J. Econ. 2019, 134, 2135–2202. [Google Scholar] [CrossRef]
  45. Loughran, T.; McDonald, B. When Is a Liability Not a Liability? Textual Analysis, Dictionaries, and 10-Ks. J. Financ. 2011, 66, 35–65. [Google Scholar] [CrossRef]
  46. Kelly, B.T.; Pruitt, S.; Su, Y. Characteristics Are Covariances: A Unified Model of Risk and Return. J. Financ. Econ. 2019, 134, 501–524. [Google Scholar] [CrossRef]
  47. Grimmer, J.; Stewart, B.M. Text as Data: The Promise and Pitfalls of Automatic Content Analysis Methods for Political Texts. Polit. Anal. 2013, 21, 267–297. [Google Scholar] [CrossRef]
  48. Huang, A.H.; Lehavy, R.; Zang, A.Y.; Zheng, R. Analyst Information Discovery and Interpretation Roles: A Topic Modeling Approach. Manag. Sci. 2018, 64, 2833–2855. [Google Scholar] [CrossRef]
  49. Papoutsi, A.; Sodhi, M.S. A Sustainability Disclosure Index Using Corporate Sustainability Reports. J. Sustain. Res. 2020, 2, e200020. [Google Scholar] [CrossRef]
  50. OECD. Joint Research Centre-European Commission. Handbook on Constructing Composite Indicators: Methodology and User Guide; OECD Publishing: Paris, France, 2008. [Google Scholar] [CrossRef]
  51. Greco, S.; Ishizaka, A.; Tasiou, M.; Torrisi, G. On the Methodological Framework of Composite Indices: A Review of the Issues of Weighting, Aggregation, and Robustness. Soc. Indic. Res. 2019, 141, 61–94. [Google Scholar] [CrossRef]
  52. Becker, W.; Saisana, M.; Paruolo, P.; Vandecasteele, I. Weights and Importance in Composite Indicators: Closing the Gap. Ecol. Indic. 2017, 80, 12–22. [Google Scholar] [CrossRef]
  53. Booysen, F. An Overview and Evaluation of Composite Indices of Development. Soc. Indic. Res. 2002, 59, 115–151. [Google Scholar] [CrossRef]
  54. Koo, T.K.; Li, M.Y. A Guideline of Selecting and Reporting Intraclass Correlation Coefficients for Reliability Research. J. Chiropr. Med. 2016, 15, 155–163. [Google Scholar] [CrossRef]
  55. Hyndman, R.J.; Koehler, A.B. Another Look at Measures of Forecast Accuracy. Int. J. Forecast. 2006, 22, 679–688. [Google Scholar] [CrossRef]
Figure 1. Framework of the LLM-based CIDQ evaluation model.
Figure 1. Framework of the LLM-based CIDQ evaluation model.
Sustainability 18 05089 g001
Figure 2. Annual trend of mean CIDQ scores (2022–2024).
Figure 2. Annual trend of mean CIDQ scores (2022–2024).
Sustainability 18 05089 g002
Figure 3. Boxplots of AI-CIDQ score distributions by year (2022–2024). (Note: The box represents the interquartile range (IQR, from the 25th to the 75th percentile). The horizontal line inside the box denotes the median. The whiskers extend to the minimum and maximum values within 1.5 times the IQR. Dots represent outliers.)
Figure 3. Boxplots of AI-CIDQ score distributions by year (2022–2024). (Note: The box represents the interquartile range (IQR, from the 25th to the 75th percentile). The horizontal line inside the box denotes the median. The whiskers extend to the minimum and maximum values within 1.5 times the IQR. Dots represent outliers.)
Sustainability 18 05089 g003
Table 1. List of sample firms.
Table 1. List of sample firms.
Company Name (English)Company Name
(Chinese)
Stock CodeIndustry CategoryCityCountry
North Huajin Chemical Industries Co., Ltd.北方华锦化学工业股份有限公司000059Petroleum Processing, Coking and Nuclear Fuel Processing IndustryPanjinChina
Shenyang Chemical Co., Ltd.沈阳化工股份有限公司000698Petroleum Processing, Coking and Nuclear Fuel Processing IndustryShenyangChina
Shanxi Meijin Energy Co., Ltd.山西美锦能源股份有限公司000723Petroleum Processing, Coking and Nuclear Fuel Processing IndustryTaiyuanChina
Yueyang Xingchang Petro-Chemical Co., Ltd.岳阳兴长石化股份有限公司000819Petroleum Processing, Coking and Nuclear Fuel Processing IndustryYueyangChina
Shanxi Blue Flame Holding Company Limited山西蓝焰控股股份有限公司000968Oil and Gas Extraction IndustryTaiyuanChina
China Petroleum & Chemical Corporation中国石油化工股份有限公司600028Oil and Gas Extraction IndustryBeijingChina
Guanghui Energy Co., Ltd.广汇能源股份有限公司600256Oil and Gas Extraction IndustryUrumqiChina
Sinopec Shanghai Petrochemical Company Limited中国石化上海石油化工股份有限公司600688Petroleum Processing, Coking and Nuclear Fuel Processing IndustryShanghaiChina
Yunnan Yunwei Co., Ltd.云南云维股份有限公司600725Petroleum Processing, Coking and Nuclear Fuel Processing IndustryKunmingChina
Shanxi Coking Co., Ltd.山西焦化股份有限公司600740Petroleum Processing, Coking and Nuclear Fuel Processing IndustryHongtong (Linfen)China
Geo-Jade Petroleum Corporation洲际油气股份有限公司600759Oil and Gas Extraction IndustryHaikouChina
Yunnan Coal & Energy Co., Ltd.云南煤业能源股份有限公司600792Petroleum Processing, Coking and Nuclear Fuel Processing IndustryAnning
(Kunming)
China
CNOOC Limited中国海洋石油有限公司600938Oil and Gas Extraction IndustryHong KongChina
Kailuan Energy Chemical Co., Ltd.开滦能源化工股份有限公司600997Petroleum Processing, Coking and Nuclear Fuel Processing IndustryTangshanChina
PetroChina Company Limited中国石油天然气股份有限公司601857Oil and Gas Extraction IndustryBeijingChina
Table 2. Basis and corresponding content for the CIDQ evaluation indicators.
Table 2. Basis and corresponding content for the CIDQ evaluation indicators.
Basis/Reference
Framework
Corresponding Indicator Content Role in the Evaluation Framework
The Greenhouse Gas Protocol: A Corporate Accounting and Reporting StandardGreenhouse gas emission boundaries, Scope 1 and Scope 2 emissions, accounting methods, and reporting boundaries (corresponding to D3 Data Disclosure)Provides a standardized basis for the accounting and reporting of direct emissions and indirect emissions associated with purchased energy, and clarifies the disclosure scope and norms for basic emissions information.
Corporate Value Chain (Scope 3) Accounting and Reporting StandardScope 3 emissions, supply chain carbon management, and value chain coverage (corresponding to D3 Data Disclosure and G2 Supply Chain Management)Provides a specific reference for the disclosure of indirect emissions across upstream and downstream value chains and related management information, and defines the scope and requirements for value-chain carbon disclosure.
TCFD recommendations and IFRS S2 Climate-related DisclosuresGovernance, strategy, risk management, and metrics and targets (corresponding to D1 Strategy and Targets and B2 Disclosure of Negative Information)Provides a systematic disclosure framework for corporate climate governance arrangements, strategic responses, risk identification, and performance targets, and standardizes the dimensions of climate-related management disclosure.
Characteristics of the petroleum and petrochemical industryLow-carbon technology development, logistics emission optimization, supply chain emission reduction, and just transition (corresponding to G1 Technological Innovation, G2 Supply Chain Management, and G3 Social Impact)Reflects the industry-specific characteristics of high emissions, long value chains, and strong transition pressure in the petroleum and petrochemical industry, enhances the industry applicability of the indicator system and its ability to capture differences in disclosure, and addresses the limitations of generic frameworks in industry adaptation.
Table 3. CIDQ evaluation indicator system.
Table 3. CIDQ evaluation indicator system.
Primary IndicatorsSecondary IndicatorsTertiary Indicators
A. UnderstandabilityA1. Diversity of ExpressionA11. Combination of Data and Charts
A12. Explanation of Professional Terminology
A2. Structural ClarityA21. Index/Table of Contents
B. ReliabilityB1. Data AccuracyB11. Disclosure of Calculation Methods
B12. Third-Party Verification
B2. Disclosure of Negative InformationB21. Emission Increases or Violation Incidents
B22. Risk Disclosure
C. ComparabilityC1. Consistency in Calculation MethodsC11. Cross-Period Consistency
C12. Alignment with Industry Standards
C2. Format StandardizationC21. Stability of Report Format
C22. Data Standardization
D. RelevanceD1. Strategy and TargetsD11. Emission Reduction Strategy
D12. Emission Reduction Targets
D13. Climate-Related Governance
D2. Actions and PerformanceD21. Emission Reduction Measures
D22. Operation of Emission Reduction Facilities
D23. Carbon Trading and Offsetting
D3. Data DisclosureD31. Scope 1 Emissions
D32. Scope 2 Emissions
D33. Scope 3 Emissions
D34. Product Carbon Footprint
D35. Carbon Intensity Indicators
E. CompletenessE1. Coverage ScopeE11. Full Value Chain Coverage
E12. All Emission Sources
E2. Level of DetailE21. Data by Department/Region
E22. Historical Data Comparison
F. TimelinessF1. Disclosure TimeF11. Timeliness of Report Disclosure
F12. Regular Updates
G. Industry SpecificityG1. Technological InnovationG11. Low-Carbon Technology R&D
G2. Supply Chain ManagementG21. Supplier Carbon Management
G22. Logistics Emission Optimization
G3. Social ImpactG31. Community Communication
G32. Just Transition
Table 4. AI-CIDQ scores of sample firms (2022–2024).
Table 4. AI-CIDQ scores of sample firms (2022–2024).
Company Name (English)Company AbbreviationCityCountry202220232024
North Huajin Chemical Industries Co., Ltd.North HuajinPanjinChina314032
Shenyang Chemical Co., Ltd.Shenyang ChemicalShenyangChina323841
Shanxi Meijin Energy Co., Ltd.Meijin EnergyTaiyuanChina484947
Yueyang Xingchang Petro-Chemical Co., Ltd.Yueyang XingchangYueyangChina92339
Shanxi Blue Flame Holding Company LimitedBlue Flame HoldingsTaiyuanChina71124
China Petroleum & Chemical CorporationSinopecBeijingChina475556
Guanghui Energy Co., Ltd.Guanghui EnergyUrumqiChina273733
Sinopec Shanghai Petrochemical Company LimitedSinopec Shanghai PetrochemicalShanghaiChina515152
Yunnan Yunwei Co., Ltd.Yunnan YunweiKunmingChina111011
Shanxi Coking Co., Ltd.Shanxi CokingHongtong (Linfen)China292941
Geo-Jade Petroleum CorporationGeo-Jade PetroleumHaikouChina122627
Yunnan Coal & Energy Co., Ltd.Yunnan Coal & EnergyAnning (Kunming)China172615
CNOOC LimitedCNOOCHong KongChina464849
Kailuan Energy Chemical Co., Ltd.Kailuan Energy ChemicalTangshanChina183544
PetroChina Company LimitedPetroChinaBeijingChina515353
Table 5. Comparison of Manual-CIDQ and AI-CIDQ scores for sampled reports.
Table 5. Comparison of Manual-CIDQ and AI-CIDQ scores for sampled reports.
Company Name (English)CityCountryYearAI-CIDQManual-CIDQ
China Petroleum & Chemical CorporationBeijingChina20224748
Sinopec Shanghai Petrochemical Company LimitedShanghaiChina20235152
CNOOC LimitedHong KongChina20244950
Shanxi Meijin Energy Co., Ltd.TaiyuanChina20224849
PetroChina Company LimitedBeijingChina20235354
North Huajin Chemical Industries Co., Ltd.PanjinChina20243233
Shenyang Chemical Co., Ltd.ShenyangChina20223233
Guanghui Energy Co., Ltd.UrumqiChina20233738
Shanxi Coking Co., Ltd.Hongtong (Linfen)China20244142
Kailuan Energy Chemical Co., Ltd.TangshanChina20221819
Yueyang Xingchang Petro-Chemical Co., Ltd.YueyangChina20232324
Shanxi Blue Flame Holding Company LimitedTaiyuanChina20242425
Yunnan Yunwei Co., Ltd.KunmingChina20221111
Geo-Jade Petroleum CorporationHaikouChina20232627
Yunnan Coal & Energy Co., Ltd.Anning (Kunming)China20241515
Table 6. Consistency test results based on 495 paired tertiary-indicator scores 1.
Table 6. Consistency test results based on 495 paired tertiary-indicator scores 1.
Test
Indicator
Test Method/TypeStatistical Valuep-ValueCriterionResult Explanation
Overall Score CorrelationPearson0.975p < 0.001r > 0.7 indicates high correlationLLM-based scores are highly correlated with manual scores at the tertiary-indicator level
Overall Score CorrelationSpearman0.975p < 0.001ρ > 0.7 indicates high correlationHigh consistency in ranking at the tertiary-indicator level
Systematic BiasPaired t-testt = −3.0070.003p < 0.05 indicates significant differenceLLM-based tertiary-indicator scores are slightly lower than manual scores overall
Overall ConsistencyICC (Single Measurement, Absolute Agreement)0.974p < 0.001ICC > 0.75 indicates good consistencyLLM-based scoring consistency is good
Mean Absolute ErrorMAE0.0384-Smaller MAE indicates higher consistencyThe average error between LLM-based and manual is approximately 0.0384
1 Note: The consistency statistics reported in Table 6 are based on 495 paired observations at the tertiary-indicator level (15 sampled reports × 33 indicators), rather than on the 15 total-score observations reported in Table 5.
Table 7. Consistency test results by primary indicator.
Table 7. Consistency test results by primary indicator.
Primary IndicatorPearsonSpearmanp-ValueCorrelation CriterionTest Result
A. Understandability0.9770.984<0.001YesPass
B. Reliability1.0001.000<0.001YesPass
C. Comparability0.9890.986<0.001YesPass
D. Relevance0.9980.992<0.001YesPass
E. Completeness0.9890.986<0.001YesPass
F. Timeliness1.0001.000<0.001YesPass
G. Industry Specificity0.9760.978<0.001YesPass
Table 8. Overall descriptive statistics of AI-CIDQ scores.
Table 8. Overall descriptive statistics of AI-CIDQ scores.
StatisticValue
Sample Size (N)45
Mean34.02
Median35.00
Standard Deviation14.98
Minimum7.00
Maximum56.00
25th Percentile (P25)24.00
75th Percentile (P75)48.00
Skewness−0.301
Kurtosis−1.161
Table 9. Annual descriptive statistics of AI-CIDQ scores (2022–2024).
Table 9. Annual descriptive statistics of AI-CIDQ scores (2022–2024).
YearSample Size (N)MeanMedianStandard DeviationMinimumMaximum
20221529.0729.0016.307.0051.00
20231535.4037.0014.4510.0055.00
20241537.6041.0013.7211.0056.00
Table 10. AI-CIDQ scores and three-year averages by firm.
Table 10. AI-CIDQ scores and three-year averages by firm.
Company Name (English)CityCountry2022 Score2023 Score2024 ScoreAverage Score
China Petroleum & Chemical CorporationBeijingChina47555652.67
PetroChina Company LimitedBeijingChina51535352.33
Sinopec Shanghai Petrochemical Company LimitedShanghaiChina51515251.33
Shanxi Meijin Energy Co., Ltd.TaiyuanChina48494748.00
CNOOC LimitedHong KongChina46484947.67
Shenyang Chemical Co., Ltd.ShenyangChina32384137.00
North Huajin Chemical Industries Co., Ltd.PanjinChina31403234.33
Shanxi Coking Co., Ltd.Hongtong (Linfen)China29294133.00
Guanghui Energy Co., Ltd.UrumqiChina27373332.33
Kailuan Energy Chemical Co., Ltd.TangshanChina18354432.33
Yueyang Xingchang Petro-Chemical Co., Ltd.YueyangChina9233923.67
Geo-Jade Petroleum CorporationHaikouChina12262721.67
Yunnan Coal & Energy Co., Ltd.Anning (Kunming)China17261519.33
Shanxi Blue Flame Holding Company LimitedTaiyuanChina7112414.00
Yunnan Yunwei Co., Ltd.KunmingChina11101110.67
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Yuan, M.; Zhong, M. Carbon Information Disclosure Quality in China’s Petroleum and Petrochemical Enterprises: An LLM Approach. Sustainability 2026, 18, 5089. https://doi.org/10.3390/su18105089

AMA Style

Yuan M, Zhong M. Carbon Information Disclosure Quality in China’s Petroleum and Petrochemical Enterprises: An LLM Approach. Sustainability. 2026; 18(10):5089. https://doi.org/10.3390/su18105089

Chicago/Turabian Style

Yuan, Mengyi, and Ma Zhong. 2026. "Carbon Information Disclosure Quality in China’s Petroleum and Petrochemical Enterprises: An LLM Approach" Sustainability 18, no. 10: 5089. https://doi.org/10.3390/su18105089

APA Style

Yuan, M., & Zhong, M. (2026). Carbon Information Disclosure Quality in China’s Petroleum and Petrochemical Enterprises: An LLM Approach. Sustainability, 18(10), 5089. https://doi.org/10.3390/su18105089

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop