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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Environ. Sci.</journal-id>
<journal-title>Frontiers in Environmental Science</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Environ. Sci.</abbrev-journal-title>
<issn pub-type="epub">2296-665X</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="publisher-id">1652558</article-id>
<article-id pub-id-type="doi">10.3389/fenvs.2025.1652558</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Environmental Science</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Impact of land resource misallocation on carbon emission efficiency: empirical evidence from 274 cities in China</article-title>
<alt-title alt-title-type="left-running-head">Wen et al.</alt-title>
<alt-title alt-title-type="right-running-head">
<ext-link ext-link-type="uri" xlink:href="https://doi.org/10.3389/fenvs.2025.1652558">10.3389/fenvs.2025.1652558</ext-link>
</alt-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname>Wen</surname>
<given-names>Zhongqi</given-names>
</name>
<uri xlink:href="https://loop.frontiersin.org/people/3109862/overview"/>
<role content-type="https://credit.niso.org/contributor-roles/conceptualization/"/>
<role content-type="https://credit.niso.org/contributor-roles/data-curation/"/>
<role content-type="https://credit.niso.org/contributor-roles/formal-analysis/"/>
<role content-type="https://credit.niso.org/contributor-roles/methodology/"/>
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<role content-type="https://credit.niso.org/contributor-roles/writing-original-draft/"/>
<role content-type="https://credit.niso.org/contributor-roles/Writing - review &#x26; editing/"/>
</contrib>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Lee</surname>
<given-names>Woon-Seek</given-names>
</name>
<xref ref-type="corresp" rid="c001">&#x2a;</xref>
<role content-type="https://credit.niso.org/contributor-roles/project-administration/"/>
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<contrib contrib-type="author">
<name>
<surname>Woo</surname>
<given-names>Sheen</given-names>
</name>
<role content-type="https://credit.niso.org/contributor-roles/investigation/"/>
<role content-type="https://credit.niso.org/contributor-roles/validation/"/>
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<role content-type="https://credit.niso.org/contributor-roles/Writing - review &#x26; editing/"/>
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<aff>
<institution>Graduate School of Management of Technology</institution>, <institution>Pukyong National University</institution>, <addr-line>Busan</addr-line>, <country>Republic of Korea</country>
</aff>
<author-notes>
<fn fn-type="edited-by">
<p>
<bold>Edited by:</bold> <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/2879584/overview">Chengqi Wang</ext-link>, University of Nottingham, United Kingdom</p>
</fn>
<fn fn-type="edited-by">
<p>
<bold>Reviewed by:</bold> <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/2208423/overview">Yazhu Wang</ext-link>, Chinese Academy of Sciences (CAS), China</p>
<p>
<ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/3117070/overview">Qingmin Zeng</ext-link>, China West Normal University, China</p>
</fn>
<corresp id="c001">&#x2a;Correspondence: Woon-Seek Lee, <email>iewslee@pknu.ac.kr</email>
</corresp>
</author-notes>
<pub-date pub-type="epub">
<day>13</day>
<month>08</month>
<year>2025</year>
</pub-date>
<pub-date pub-type="collection">
<year>2025</year>
</pub-date>
<volume>13</volume>
<elocation-id>1652558</elocation-id>
<history>
<date date-type="received">
<day>23</day>
<month>06</month>
<year>2025</year>
</date>
<date date-type="accepted">
<day>28</day>
<month>07</month>
<year>2025</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2025 Wen, Lee and Woo.</copyright-statement>
<copyright-year>2025</copyright-year>
<copyright-holder>Wen, Lee and Woo</copyright-holder>
<license xlink:href="http://creativecommons.org/licenses/by/4.0/">
<p>This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.</p>
</license>
</permissions>
<abstract>
<sec>
<title>Introduction</title>
<p>With the acceleration of urbanization and the implementation of the &#x201c;dual carbon&#x201d; goals, the impact of Land Resource Misallocation (LRM) on Urban Carbon Emission Efficiency (UCEE) has attracted increasing attention.</p>
</sec>
<sec>
<title>Methods</title>
<p>Based on panel data from 274 Chinese cities during the period 2010&#x2013;2022, we constructed a LRM index and employed a two-way fixed-effects model to empirically analyze the relationship between LRM and UCEE.</p>
</sec>
<sec>
<title>Results</title>
<p>The results revealed that LRM significantly hindered the improvement of carbon emissions efficiency in cities. The mechanism analysis indicates that this negative effect is primarily transmitted through the obstruction of Industrial Structure Upgrading (ISU) and Green Technological Innovation (GTI). Further, regional heterogeneity tests showed that the suppressive effect was more pronounced in the central and western regions, small- and medium-sized cities, and non-resource-based cities.</p>
</sec>
<sec>
<title>Discussion</title>
<p>In terms of policy implications, deepening market-oriented reforms of the land system, optimizing land use structures, reducing administrative intervention in land allocation, and simultaneously promoting industrial upgrading and GTI to enhance UCEE are recommended.</p>
</sec>
</abstract>
<kwd-group>
<kwd>land resource misallocation</kwd>
<kwd>urban carbon emission efficiency</kwd>
<kwd>industrial structure upgrading</kwd>
<kwd>green technological innovation</kwd>
<kwd>panel data analysis</kwd>
</kwd-group>
<custom-meta-wrap>
<custom-meta>
<meta-name>section-at-acceptance</meta-name>
<meta-value>Land Use Dynamics</meta-value>
</custom-meta>
</custom-meta-wrap>
</article-meta>
</front>
<body>
<sec id="s1">
<title>1 Introduction</title>
<p>Global warming poses an unprecedented challenge to sustainable development, and the urgency to reduce greenhouse gas (GHG) emissions never increased. Rapid urbanization and industrialization, especially in developing economies, significantly intensified energy consumption and carbon emissions (<xref ref-type="bibr" rid="B1">Abbasi et al., 2020</xref>). Although cities occupy only a small proportion of the Earth&#x2019;s surface, their energy use contributes approximately 70% of global CO<sub>2</sub> emissions (<xref ref-type="bibr" rid="B22">Luqman et al., 2023</xref>). Therefore, improving Urban Carbon Emission Efficiency (UCEE) (i.e., achieving greater economic and social output while reducing carbon emissions) has become a key strategy for addressing climate change and maintaining economic growth. Enhancing urban carbon emission efficiency is crucial not only for achieving global climate goals such as those outlined in the Paris Agreement but also for promoting sustainable urban development (<xref ref-type="bibr" rid="B11">Fan and Xu, 2025</xref>). This is particularly relevant for China, which, despite significant progress in deploying renewable energy in recent years, has also become one of the largest carbon emitters globally (<xref ref-type="bibr" rid="B29">Raihan and Bari, 2024</xref>; <xref ref-type="bibr" rid="B34">Wang et al., 2024</xref>). China pledged to reach peak carbon emissions by 2030 and achieve carbon neutrality by 2060 (<xref ref-type="bibr" rid="B41">Zhang et al., 2023</xref>; <xref ref-type="bibr" rid="B43">Zhang H. et al., 2024</xref>). Achieving this transformation requires a fundamental decoupling of economic growth from carbon emissions, which, in turn, requires significant improvements in carbon efficiency across all sectors of the urban economy. Carbon emission efficiency generally reflects the effectiveness with which an economy or city generates output or achieves development goals per unit of carbon emissions (<xref ref-type="bibr" rid="B4">Chen et al., 2025</xref>). Quantitatively, carbon emission efficiency is often expressed as the ratio of economic output (or other benefit indicators) to carbon emissions or inversely as the carbon intensity of economic activities (<xref ref-type="bibr" rid="B19">Li et al., 2024</xref>). A higher UCEE implies that a city produces more GDP, services, or social welfare per ton of CO<sub>2</sub> emitted, indicating a higher degree of sustainable, low-carbon development. Therefore, enhancing the urban carbon emission efficiency is critical for achieving emission reductions while sustaining socioeconomic progress (<xref ref-type="bibr" rid="B42">Zhang Y. et al., 2024</xref>).</p>
<p>Numerous studies explored the determinants of UCEE. Technological innovation and energy structure are frequently identified as key drivers. For instance, clean energy and advanced technologies can significantly enhance efficiency by reducing carbon emissions per unit of energy use or output (<xref ref-type="bibr" rid="B25">Miao et al., 2024</xref>). Similarly, industrial structure plays an important role: cities dominated by high-tech industries and services typically exhibit better carbon efficiency than those centered on heavy industry because of the lower emissions of the tertiary sector (<xref ref-type="bibr" rid="B5">Zhang H. et al., 2024</xref>). Robust environmental policies and regulations can also improve the UCEE by promoting energy conservation and emission control. Recent analyses of Chinese cities show that stricter environmental regulations and lower energy intensity (energy use per unit GDP) are significantly associated with higher carbon efficiency, emphasizing the importance of governance and green investment (<xref ref-type="bibr" rid="B5">Zhang H. et al., 2024</xref>). Summarily, existing literature suggests that technological, structural, and policy-related factors jointly contribute to improvements in UCEE.</p>
<p>However, one critical factor was overlooked in the discussion on urban carbon efficiency, namely, the role of urban land use and allocation. The spatial distribution of land across different uses and cities may also substantially affect carbon emissions (<xref ref-type="bibr" rid="B35">Wen et al., 2025</xref>). Urban form and land use patterns fundamentally shape energy demand and emissions. For example, unplanned urban sprawl often leads to increased vehicle use and higher <italic>per capita</italic> emissions, while compact, well-planned cities enable more efficient infrastructure and lower carbon footprints (<xref ref-type="bibr" rid="B1">Abbasi et al., 2020</xref>). Studies emphasize that optimizing urban spatial structures (e.g., promoting polycentric layouts and higher density) can enhance carbon efficiency by reducing travel distances and conserving land resources (<xref ref-type="bibr" rid="B11">Fan and Xu, 2025</xref>). These findings suggest that urban planning and land management are crucial for achieving emission reduction goals. Furthermore, in many emerging economies, land is not fully allocated through market forces, although it is heavily influenced by government policies and institutional arrangements (<xref ref-type="bibr" rid="B35">Wen et al., 2025</xref>). This often results in Land Resource Misallocation (LRM), in which the distribution of land across industrial, commercial, and residential uses deviates from economically efficient or environmentally optimal patterns. China is a typical case in which land ownership is shared between the state and collectives, giving governments the dominant authority over land allocation. Land use has become a critical policy instrument for stimulating economic growth. Under the &#x201c;land-for-development&#x201d; strategy, local governments tend to allocate large portions of urban land to industrial uses at artificially low prices to attract manufacturing investment and boost GDP (<xref ref-type="bibr" rid="B15">Han and Huang, 2022</xref>). While this approach has fueled rapid industrialization, it has also led to inefficient urban layouts such as oversized and underutilized industrial parks. This reflects an imbalance in land use and a misallocation of land resources away from potentially more efficient or higher-value applications (<xref ref-type="bibr" rid="B15">Han and Huang, 2022</xref>). For example, land misallocation results in higher emissions and lower efficiency. Using data from Chinese cities, <xref ref-type="bibr" rid="B15">Han and Huang (2022)</xref> found that land misallocation, especially overallocation to industrial land, significantly increases urban carbon emissions. Their analysis suggests that this effect operates through multiple channels: land misallocation hampers industrial upgrading, inhibits technological innovation, and undermines the benefits of economic agglomeration, thereby locking cities into inefficient, high-carbon development paths (<xref ref-type="bibr" rid="B15">Han and Huang, 2022</xref>). Similarly, <xref ref-type="bibr" rid="B44">Zhou et al. (2022)</xref> directly confirmed the adverse effects of land resource misallocation on urban carbon emission efficiency. They reported that cities with higher degrees of misallocation tend to have significantly lower carbon efficiency, implying that poor land allocation results in higher total emissions and lower economic output per unit of carbon (<xref ref-type="bibr" rid="B44">Zhou et al., 2022</xref>).</p>
<p>Although the academic community has gradually begun to explore the relationship between LRM and UCEE, this field is still in its infancy, with several important knowledge gaps yet to be addressed. For example, whether land misallocation is a significant determinant of urban carbon emission efficiency has not been fully examined or empirically validated in the existing literature (<xref ref-type="bibr" rid="B12">Gao and He, 2024</xref>). Furthermore, the underlying mechanisms through which land misallocation affects carbon efficiency are poorly understood. Much of the empirical literature focuses on either the direct impact of the industrial structure on emissions or treats the industrial structure as a mediating variable for other factors (<xref ref-type="bibr" rid="B12">Gao and He, 2024</xref>; <xref ref-type="bibr" rid="B6">Cheng Y. et al., 2025</xref>; <xref ref-type="bibr" rid="B40">Xue et al., 2025</xref>), neglecting its potential role as a transmission mechanism linking land misallocation and urban carbon efficiency. While some studies explored the relationship between land misallocation and green technological innovation (<xref ref-type="bibr" rid="B39">Xu et al., 2025</xref>), a lack of research still exists on the mediating pathway of &#x201c;Land Resource Misallocation&#x2013;Green Technological Innovation&#x2013;Urban Carbon Emission Efficiency,&#x201d; which overlooks the crucial role that green innovation may play in this linkage (<xref ref-type="bibr" rid="B27">Nan et al., 2022</xref>).</p>
<p>Therefore, we examined the impact of LRM on UCEE, identified whether misallocation is a key determinant, and uncovered its transmission mechanism. Using panel data from 274 prefecture-level cities in China between 2010 and 2022, we constructed a two-way fixed-effects model to empirically assess the relationship between LRM and carbon emission efficiency. The results show that land misallocation significantly inhibits improvements in carbon emissions efficiency, and robustness checks confirm the validity of the baseline findings. These empirical results contribute to the literature by addressing a previously overlooked dimension in environmental economics&#x2014;highlighting LRM as a significant factor influencing UCEE. The mechanism analysis reveals that LRM impedes carbon efficiency, primarily by suppressing Green Technological Innovation (GTI) and hindering Industrial Structure Upgrading (ISU). The identification of these two mediating variables confirms that ISU and GTI play pivotal roles in the transmission mechanism through which land misallocation affects UCEE. This finding not only enriches the theoretical framework of the mechanism but also addresses a significant gap in the existing literature. Heterogeneity analysis further showed that this inhibitory effect was more pronounced in the central and western regions, small- and medium-sized cities, and non-resource-based cities. We verified the robustness of our findings by replacing the core explanatory variable with the ratio of land transfer revenue to urban construction land area. Additionally, we address endogeneity concerns using the interaction term between the average urban terrain slope and the annual economic growth target of the city as an instrumental variable, and the conclusions remain robust. The use of this instrumental variable strengthens the validity of causal identification in assessing the effect of LRM on UCEE, thus contributing to the methodological literature by addressing endogeneity concerns that have been largely overlooked in prior studies. These findings confirm the rigorous identification of LRM as an important determinant of urban carbon emissions efficiency.</p>
<p>The remainder of this paper is organized as follows. <xref ref-type="sec" rid="s2">Section 2</xref> develops the theoretical framework and research hypotheses; <xref ref-type="sec" rid="s3">Section 3</xref> describes the data, variables, and empirical model; <xref ref-type="sec" rid="s4">Section 4</xref> presents and discusses the empirical results; <xref ref-type="sec" rid="s5">Section 5</xref> concludes with key findings, policy implications, and future research directions; and <xref ref-type="sec" rid="s6">Section 6</xref> provides a brief summary.</p>
</sec>
<sec id="s2">
<title>2 Theoretical framework and hypotheses</title>
<p>To illustrate the hypothesized relationships between LRM and UCEE, this study constructs a conceptual framework, as shown in <xref ref-type="fig" rid="F1">Figure 1</xref>. Specifically, <xref ref-type="statement" rid="H1">H1</xref> tests the direct effect of LRM on UCEE, while <xref ref-type="statement" rid="H2">H2</xref> and <xref ref-type="statement" rid="H3">H3</xref> explore the mediating roles of ISU and GTI, respectively.</p>
<fig id="F1" position="float">
<label>FIGURE 1</label>
<caption>
<p>Conceptual framework.</p>
</caption>
<graphic xlink:href="fenvs-13-1652558-g001.tif">
<alt-text content-type="machine-generated">Flowchart illustrating the relationship between land resource misallocation and urban carbon emission efficiency, labeled as H1. It shows two mechanism variables: industrial structure upgrading (H2) and green technological innovation (H3) affecting the process.</alt-text>
</graphic>
</fig>
<sec id="s2-1">
<title>2.1 Direct impact of land resource misallocation on urban carbon emission efficiency</title>
<p>LRM refers to the inefficient allocation of land across industrial sectors and functional uses, often stemming from government intervention deviating from market-oriented mechanisms (<xref ref-type="bibr" rid="B45">Zhou et al., 2023</xref>). In China, such distortions are reflected not only in the quantity or spatial distribution of land supply but also deeply embedded in land pricing structures and property rights systems (<xref ref-type="bibr" rid="B16">Huang et al., 2025</xref>). A prominent manifestation of this phenomenon is that local governments, driven by short-term fiscal revenue and economic growth targets, allocate land at artificially low prices to high-energy-consuming industries (<xref ref-type="bibr" rid="B2">An, 2024</xref>; <xref ref-type="bibr" rid="B3">Chen and Yuan, 2025</xref>), effectively reducing land use costs for carbon-intensive sectors (<xref ref-type="bibr" rid="B13">Gao et al., 2022</xref>). This practice distorts urban spatial development patterns, constrains the emergence of low-carbon industries, and undermines the competitiveness of green and innovative enterprises in the land market, thereby limiting their expansion and contribution to carbon reduction (<xref ref-type="bibr" rid="B17">Jiang et al., 2022</xref>; <xref ref-type="bibr" rid="B37">Wu et al., 2023</xref>). Such an institutional bias exacerbates the feedback loop between resource misallocation, industrial path dependence, and carbon lock-in, locking cities into a high-emission growth trajectory (<xref ref-type="bibr" rid="B6">Cheng Y. et al., 2025</xref>). Furthermore, existing literature suggests that the concentration of land allocation in low-productivity sectors also leads to structural inefficiencies, reflected in declines in total factor productivity (TFP). This misallocation reinforces traditional high-pollution industrial structures, further entrenching rigid emission patterns and reducing the overall carbon emission efficiency (<xref ref-type="bibr" rid="B12">Gao and He, 2024</xref>). For instance, <xref ref-type="bibr" rid="B44">Zhou et al. (2022)</xref>, based on panel data from Chinese cities, found that higher degrees of land misallocation were associated with poorer urban carbon performance. Summarily, we argue that LRM has become a significant structural barrier to improving the efficiency of urban carbon emissions. Hence, we propose the following hypotheses:</p>
<p>
<statement content-type="h1" id="H1">
<label>H1</label>
<p>LRM hinders improvements in UCEE.</p>
</statement>
</p>
</sec>
<sec id="s2-2">
<title>2.2 Mechanism of industrial structure upgrading</title>
<p>In the context of carbon neutrality, the optimization and upgrading of industrial structures are widely recognized as key pathways for improving the efficiency of urban carbon emissions. The core lies in transforming urban economies from traditional high-carbon, resource-intensive industries toward green, low-carbon, and high-value-added emerging sectors (<xref ref-type="bibr" rid="B44">Zhou et al., 2022</xref>), ultimately targeting the development of industries characterized by elevated value capture, advanced technological embeddedness, and eco-efficient production paradigms (<xref ref-type="bibr" rid="B30">Ran et al., 2023</xref>). This transformation not only helps reduce carbon intensity and improve energy structure but also enhances green productivity at the urban level through technological advancement (<xref ref-type="bibr" rid="B3">Chen and Yuan, 2025</xref>). However, as a typical institutional distortion, land&#x2013;resource misallocation may serve as a suppressive mechanism during this transition. The misallocation compresses the accessibility of land for high-tech industries and modern services, hampers spatial agglomeration and capital-deepening of green industries, and thus weakens the advancement of industrial upgrading (<xref ref-type="bibr" rid="B38">Xie et al., 2022</xref>; <xref ref-type="bibr" rid="B5">Cheng G. et al., 2025</xref>). Furthermore, resource dependence impedes the advancement and upgrading of industrial structure (<xref ref-type="bibr" rid="B33">Wang et al., 2019</xref>). The suboptimal allocation of land factors may reinforce existing high-carbon industrial structures through &#x201c;path dependence,&#x201d; resulting in a &#x201c;lock-in effect&#x201d; preventing the transition to more advanced industrial forms and undermines carbon efficiency (<xref ref-type="bibr" rid="B5">Cheng G. et al., 2025</xref>). Therefore, we argue that LRM may suppress improvements in UCEE by obstructing ISU. Accordingly, we propose the following hypothesis:</p>
<p>
<statement content-type="h2" id="H2">
<label>H2</label>
<p>LRM inhibits the improvement of UCEE by impeding ISU.</p>
</statement>
</p>
</sec>
<sec id="s2-3">
<title>2.3 Mediating mechanism of green technological innovation</title>
<p>Under the guidance of the &#x201c;dual carbon&#x201d; goals, GTI is widely regarded as a critical lever to enhance UCEE. Its essence lies in decoupling economic growth from carbon emissions by improving resource utilization efficiency and environmental performance through technological progress and institutional innovation (<xref ref-type="bibr" rid="B8">Deng et al., 2019</xref>; <xref ref-type="bibr" rid="B27">Nan et al., 2022</xref>). The Green Technological Innovation encompasses not only clean production, energy-saving technologies, and renewable energy, but also green transformation in institutions, management, and business models, forming the core of urban green development capacity that aligns with the long-term sustainability paradigm (<xref ref-type="bibr" rid="B18">Li and Liao, 2020</xref>). As land is an essential input for green innovation, its allocation directly influences the formation of the green technological capacity of a city. The existence of LRM may hinder the GTI, thereby weakening UCEE. An imbalanced allocation of industrial land increases the carbon intensity per unit of economic output and limits the potential for large-scale adoption of clean technologies (<xref ref-type="bibr" rid="B7">Chu et al., 2019</xref>). For example, when land is preferentially allocated to polluting and energy-intensive industries, green firms face higher land costs, weaker infrastructure support, and insufficient innovation network connections, ultimately suppressing investments in green R&#x26;D and the diffusion of sustainable technologies (<xref ref-type="bibr" rid="B10">Du and Li, 2021</xref>). Contrarily, green industries and service sectors depend on high-quality land and a supportive ecological environment; however, under a distorted land allocation regime, such sectors are often marginalized in urban space, weakening the capacity for sustainable development of the city (<xref ref-type="bibr" rid="B5">Cheng G. et al., 2025</xref>). Based on this logic, we propose the following hypothesis.</p>
<p>
<statement content-type="h3" id="H3">
<label>H3</label>
<p>LRM inhibits the improvement of UCEE by hindering the development of GTI.</p>
</statement>
</p>
</sec>
</sec>
<sec sec-type="methods" id="s3">
<title>3 Methodology</title>
<sec id="s3-1">
<title>3.1 Sample selection and data sources</title>
<p>We used panel data from 274 prefecture-level cities in China over a 13-year period from 2010 to 2022, comprising 3,562 observations, to investigate the relationship between LRM and carbon emissions efficiency, as well as its underlying mechanisms. Observations with missing values (city-year pairs) were excluded to ensure consistency in the alignment of all variables, and 3,004 valid observations were ultimately retained for the benchmark regression. All data were analyzed using the Stata software. To address heteroscedasticity, robust standard errors were used in all regressions. To mitigate the influence of outliers, all continuous variables are winsorized at the top and bottom 1%.</p>
<p>The data for each indicator were sourced as follows: LRM data were obtained from the <italic>China Urban Construction Statistical Yearbook</italic> and carbon emission efficiency data were derived from the CEADS database. Data on ISU, population density, human capital, financial development level, foreign direct investment, and per-capita fiscal expenditure were collected from statistical yearbooks, bulletins, and statistical bureaus at various government levels in China. GTI data are obtained from the CNRDS database. The environmental regulation intensity was compiled from government work reports published on official government websites.</p>
</sec>
<sec id="s3-2">
<title>3.2 Variable measurement</title>
<sec id="s3-2-1">
<title>3.2.1 Explanatory variable</title>
<p>LRM serves as the central explanatory variable within this empirical framework. Land resource allocation refers to the distribution of land across industries (<xref ref-type="bibr" rid="B5">Cheng G. et al., 2025</xref>). Under the vertically integrated governance system and current land policy framework of China, land is publicly owned and the government holds substantial discretion over its allocation. In pursuit of economic benefits, local governments tend to supply large quantities of industrial land, while restricting the provision of land for commercial and residential purposes, leading to the excessive expansion of industrial land. This phenomenon was defined here as the land resource misallocation (<xref ref-type="bibr" rid="B42">Zhang Y. et al., 2024</xref>). Accordingly, we measured LRM using the proportion of industrial land within the total urban construction land. This ratio reflects the extent to which land allocation is biased toward secondary industries, capturing the potential influence of government-led land resource distribution on carbon emission efficiency.</p>
<p>LRM was calculated using the following <xref ref-type="disp-formula" rid="e1">Equation 1</xref>:<disp-formula id="e1">
<mml:math id="m1">
<mml:mrow>
<mml:mi>L</mml:mi>
<mml:mi>R</mml:mi>
<mml:mi>M</mml:mi>
<mml:mo>&#x3d;</mml:mo>
<mml:mfrac>
<mml:mrow>
<mml:mi>I</mml:mi>
<mml:mi>n</mml:mi>
<mml:mi>d</mml:mi>
<mml:mi>u</mml:mi>
<mml:mi>s</mml:mi>
<mml:mi>t</mml:mi>
<mml:mi>r</mml:mi>
<mml:mi>i</mml:mi>
<mml:mi>a</mml:mi>
<mml:mi>l</mml:mi>
<mml:mtext>&#xa0;</mml:mtext>
<mml:mi>L</mml:mi>
<mml:mi>a</mml:mi>
<mml:mi>n</mml:mi>
<mml:mi>d</mml:mi>
<mml:mtext>&#xa0;</mml:mtext>
<mml:mi>A</mml:mi>
<mml:mi>r</mml:mi>
<mml:mi>e</mml:mi>
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</p>
</sec>
<sec id="s3-2-2">
<title>3.2.2 Dependent variable</title>
<p>The dependent variable is UCEE. We adopt a super-efficiency Slack-Based Measure (SBM) model incorporating undesirable outputs (CO<sub>2</sub> emissions) to measure UCEE. This method was first proposed by <xref ref-type="bibr" rid="B32">Tone (2001)</xref>, and we followed the approach of <xref ref-type="bibr" rid="B44">Zhou et al. (2022)</xref> by simultaneously considering both input and output indicators with indicator selection based on data availability. Compared with traditional models for measuring UCEE, the proposed model offers several advantages. First, it directly incorporates undesirable outputs (i.e., CO<sub>2</sub> emissions), thereby avoiding efficiency distortion caused by data transformation in conventional approaches. Second, it relaxes the upper bound of efficiency scores, allowing differentiation among highly efficient cities. Third, by adopting a non-radial optimization framework and a directional distance function, it accurately identifies the improvement potential of individual input and output factors. These features make the model a robust and suitable tool for assessing UCEE. The specific indicators used to calculate the UCEE were as follows:<list list-type="simple">
<list-item>
<p>(1) Input variables include the following factors.</p>
<list list-type="simple">
<list-item>
<p>i) Capital input, represented by the annual stock of fixed assets in the city (unit: ten thousand yuan).</p>
</list-item>
<list-item>
<p>ii) Labor input, measured by the number of employed persons in the city (unit: ten thousand persons)</p>
</list-item>
<list-item>
<p>iii) Energy input, represented by the total energy consumption in the city (unit: ten thousand tons of standard coal).</p>
</list-item>
</list>
</list-item>
<list-item>
<p>(2) Desirable output variable: Real GDP of the city (unit: ten thousand yuan).</p>
</list-item>
<list-item>
<p>(3) Undesirable output variable: Urban CO<sub>2</sub> emissions (unit: 10,000 tons), which are estimated based on the consumption of major energy types and their corresponding emission factors, including coal, oil, natural gas, and electricity.</p>
</list-item>
</list>
</p>
<p>The corresponding model is as follows:<disp-formula id="e2">
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<label>(2)</label>
</disp-formula>
</p>
<p>In <xref ref-type="disp-formula" rid="e2">Equation 2</xref> above, the variables &#x3b4;k<sup>-</sup>, &#x3b4;r<sup>&#x2b;</sup>, and &#x3b4;qb are referred to as <italic>slack variables</italic>. &#x3b4;k<sup>-</sup>, &#x3b4;r<sup>&#x2b;</sup>, and &#x3b4;qb represent the slack in the <italic>k</italic>-th type of capital input, the shortfall in the <italic>r</italic>-th desirable output, and the surplus in the <italic>q</italic>-th undesirable output, respectively. While &#x3c6; denotes the carbon emission efficiency score of the decision-making unit (DMU o). Correspondingly, xko, yro, and bqo denote the inputs of the <italic>k</italic>-th capital, <italic>r</italic>-th desirable output, and <italic>q</italic>-th undesirable output for decision-making unit <italic>o</italic> (DMU <italic>o</italic>). The objective of the model is to minimize input redundancies and excessive undesirable outputs while maintaining the current level of desirable outputs, thereby improving the carbon emission efficiency.</p>
<p>The computational methods for these slack variables are expressed in <xref ref-type="disp-formula" rid="e3">Equations 3</xref>&#x2013;<xref ref-type="disp-formula" rid="e5">5</xref>:<disp-formula id="e3">
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<label>(4)</label>
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<disp-formula id="e5">
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<mml:mi>&#x3b4;</mml:mi>
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</p>
<p>The weighted linear combinations in <xref ref-type="disp-formula" rid="e3">Equations 3</xref>&#x2013;<xref ref-type="disp-formula" rid="e5">5</xref> are defined as follows: &#x2211;<sub>i</sub>&#x3bb;<sub>i</sub>x<sub>k</sub>
<sub>i</sub> represents the minimum required input of factor k, based on a weighted combination of peer DMU. &#x2211;<sub>i</sub>&#x3bb;<sub>i</sub>y<sub>ri</sub> indicates the maximum achievable level of desirable output r, under current technology. &#x2211;<sub>i</sub>&#x3bb;<sub>i</sub>b<sub>qi</sub> denotes the lowest attainable level of undesirable output q, considering environmental constraints. Here, &#x3bb;<sub>i</sub> is the weight assigned to each DMU in constructing the reference (efficient) frontier.</p>
<p>Based on the super-efficiency SBM model, 3,562 observations of UCEE were calculated using <xref ref-type="disp-formula" rid="e2">Equation 2</xref>. The efficiency values range from 0.020 to 1.110, with a mean of 0.332, indicating an overall low level of carbon efficiency. This finding suggests that significant room for improvement exists in the synergy between carbon reduction and economic growth in Chinese cities. Although a few cities exhibited UCEE values approaching 1, indicating relatively balanced development, most cities fell into the low-efficiency range, reflecting their continued reliance on traditional high-emission, low-output development models.</p>
</sec>
<sec id="s3-2-3">
<title>3.2.3 Mechanism variables</title>
<p>We introduced two mechanism variables: ISU and GTI.</p>
<p>To measure the level of industrial structure upgrading, we follow the method by <xref ref-type="bibr" rid="B26">Murakami (2015)</xref>, employing a structural indicator widely used in related research, namely, the level of service-oriented industrial transformation, referred to in this study as ISU. Specifically, this indicator is measured as the ratio of the added value of the tertiary sector to that of the secondary sector. This reflects the shift in economic activity from traditional manufacturing to high-value-added and low-carbon modern services (<xref ref-type="bibr" rid="B45">Zhou et al., 2023</xref>). A higher ratio indicates a greater share of the service sector in the national economy, representing a higher level of industrial structural upgrade.</p>
<p>The second variable is GTI. Following the method of <xref ref-type="bibr" rid="B36">Wu et al. (2022)</xref>, we use the number of obtained green patents as a proxy. This metric is widely accepted in environmental economics. Prior to the regression analysis, we apply a log transformation to the count of green patents after adding one (<xref ref-type="bibr" rid="B21">Liu et al., 2021</xref>). This transformation helps smooth the skewness of distribution and enhances the comparability of green innovation levels across cities.</p>
</sec>
<sec id="s3-2-4">
<title>3.2.4 Control variables</title>
<p>UCEE is affected by several factors. Referring to existing literature (<xref ref-type="bibr" rid="B45">Zhou et al., 2023</xref>; <xref ref-type="bibr" rid="B2">An, 2024</xref>; <xref ref-type="bibr" rid="B31">Shao et al., 2024</xref>; <xref ref-type="bibr" rid="B16">Huang et al., 2025</xref>), we control for the following variables: (1) Population Density (PD), measured by the number of permanent residents per unit of land area (unit: persons/km<sup>2</sup>); (2) Financial Development (FD), calculated as the ratio of the sum of year-end loan and deposit balances of financial institutions to the GDP of the city in the same year; (3) Human Capital (HC), measured by the share of permanent residents holding an associate degree or higher (unit: %); (4) Foreign Direct Investment (FDI), measured as the share of actual utilized foreign direct investment in the annual GDP of the city (unit: %); (5) Per Capita Fiscal Expenditure (PCFE), based on the general public budget expenditure <italic>per capita</italic>, where population is defined as the number of permanent residents (unit: yuan/person); (6) Environmental Regulation Intensity (ERI), represented by the proportion of environment-related terms in the annual work report of the local government.</p>
</sec>
</sec>
<sec id="s3-3">
<title>3.3 Empirical model</title>
<p>Following the methodology of <xref ref-type="bibr" rid="B23">Ma et al. (2025)</xref>, we constructed a two-way fixed effects model in a benchmark regression to capture the inhibitory effect of LRM on carbon emissions efficiency across cities and over time, thereby testing <xref ref-type="statement" rid="H1">Hypothesis 1</xref>.</p>
<p>Baseline regression model:<disp-formula id="e6">
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<p>In the model, <italic>c, t, &#x3b1;</italic>
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</sec>
</sec>
<sec id="s4">
<title>4 Empirical results and analyses</title>
<sec id="s4-1">
<title>4.1 Descriptive statistics</title>
<p>To better understand the characteristics of the research sample and obtain an overview of the panel data, we conducted a descriptive statistical analysis of the main variables. The analysis was performed using the Stata software, and the results are presented in <xref ref-type="table" rid="T1">Table 1</xref>.</p>
<table-wrap id="T1" position="float">
<label>TABLE 1</label>
<caption>
<p>Descriptive statistics.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="left">Variables</th>
<th align="left">N</th>
<th align="left">Min</th>
<th align="left">Max</th>
<th align="left">Mean</th>
<th align="left">SD</th>
<th align="left">p25</th>
<th align="left">p50</th>
<th align="left">p75</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">UCEE</td>
<td align="left">3,004</td>
<td align="left">0.150</td>
<td align="left">0.834</td>
<td align="left">0.326</td>
<td align="left">0.115</td>
<td align="left">0.252</td>
<td align="left">0.302</td>
<td align="left">0.374</td>
</tr>
<tr>
<td align="left">LRM</td>
<td align="left">3,004</td>
<td align="left">2.091</td>
<td align="left">37.710</td>
<td align="left">18.640</td>
<td align="left">8.191</td>
<td align="left">12.270</td>
<td align="left">19.000</td>
<td align="left">24.330</td>
</tr>
<tr>
<td align="left">PD</td>
<td align="left">3,004</td>
<td align="left">23.220</td>
<td align="left">2,614.000</td>
<td align="left">471.700</td>
<td align="left">427.900</td>
<td align="left">191.400</td>
<td align="left">358.200</td>
<td align="left">620.500</td>
</tr>
<tr>
<td align="left">FD</td>
<td align="left">3,004</td>
<td align="left">0.987</td>
<td align="left">6.559</td>
<td align="left">2.459</td>
<td align="left">1.122</td>
<td align="left">1.670</td>
<td align="left">2.154</td>
<td align="left">2.906</td>
</tr>
<tr>
<td align="left">HC</td>
<td align="left">3,004</td>
<td align="left">0.113</td>
<td align="left">9.607</td>
<td align="left">1.863</td>
<td align="left">1.993</td>
<td align="left">0.642</td>
<td align="left">1.169</td>
<td align="left">2.093</td>
</tr>
<tr>
<td align="left">FDI</td>
<td align="left">3,004</td>
<td align="left">0.007</td>
<td align="left">7.677</td>
<td align="left">1.769</td>
<td align="left">1.730</td>
<td align="left">0.395</td>
<td align="left">1.277</td>
<td align="left">2.528</td>
</tr>
<tr>
<td align="left">PCFE</td>
<td align="left">3,004</td>
<td align="left">2,643.000</td>
<td align="left">21,706.000</td>
<td align="left">8,819.000</td>
<td align="left">3,849.000</td>
<td align="left">5,960.000</td>
<td align="left">8,292.000</td>
<td align="left">11,009.000</td>
</tr>
<tr>
<td align="left">ERI</td>
<td align="left">3,004</td>
<td align="left">0.479</td>
<td align="left">1.905</td>
<td align="left">0.949</td>
<td align="left">0.271</td>
<td align="left">0.759</td>
<td align="left">0.908</td>
<td align="left">1.086</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>Note: UCEE, urban carbon emission efficiency; LRM, land resource misallocation; PD, population density; FD, financial development; HC, human capital; FDI, foreign direct investment; PCFE, per capita fiscal expenditure; ERI, environmental regulation intensity.</p>
</fn>
</table-wrap-foot>
</table-wrap>
<p>The dependent variable, UCEE, has a mean value of 0.150, a median of 0.302, and a standard deviation of 0.115, indicating a certain degree of variation in carbon efficiency, which provides a sound foundation for further empirical investigation. The independent variable, LRM, shows a mean of 18.64 and a median of 19.00, suggesting that the overall level of the variable is concentrated around 19. Additionally, the descriptive statistics of the other variables indicated that all variables fell within a reasonable range, confirming the appropriateness of the sample selection in this study.</p>
</sec>
<sec id="s4-2">
<title>4.2 Correlation analysis</title>
<p>
<xref ref-type="table" rid="T2">Table 2</xref> presents the results of correlation analyses. At the preliminary level, LRM appeared to be negatively correlated with UCEE, although the relationship was not statistically significant, indicating the need for further investigation. Additionally, most <italic>p</italic>-values in the correlation test were &#x3c;0.01, suggesting that the variables exhibited strong correlations at the 1% significance level.</p>
<table-wrap id="T2" position="float">
<label>TABLE 2</label>
<caption>
<p>Correlation test.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="left">Variables</th>
<th align="left">UCEE</th>
<th align="left">LRM</th>
<th align="left">PD</th>
<th align="left">FD</th>
<th align="left">HC</th>
<th align="left">FDI</th>
<th align="left">PCFE</th>
<th align="left">ERI</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">UCEE</td>
<td align="left">1</td>
<td align="left"/>
<td align="left"/>
<td align="left"/>
<td align="left"/>
<td align="left"/>
<td align="left"/>
<td align="left"/>
</tr>
<tr>
<td align="left">LRM</td>
<td align="left">&#x2212;0.029</td>
<td align="left">1</td>
<td align="left"/>
<td align="left"/>
<td align="left"/>
<td align="left"/>
<td align="left"/>
<td align="left"/>
</tr>
<tr>
<td align="left">PD</td>
<td align="left">0.001</td>
<td align="left">0.194&#x2a;&#x2a;&#x2a;</td>
<td align="left">1</td>
<td align="left"/>
<td align="left"/>
<td align="left"/>
<td align="left"/>
<td align="left"/>
</tr>
<tr>
<td align="left">FD</td>
<td align="left">&#x2212;0.038&#x2a;&#x2a;</td>
<td align="left">&#x2212;0.072&#x2a;&#x2a;&#x2a;</td>
<td align="left">0.201&#x2a;&#x2a;&#x2a;</td>
<td align="left">1</td>
<td align="left"/>
<td align="left"/>
<td align="left"/>
<td align="left"/>
</tr>
<tr>
<td align="left">HC</td>
<td align="left">0.007</td>
<td align="left">0.003</td>
<td align="left">0.261&#x2a;&#x2a;&#x2a;</td>
<td align="left">0.589&#x2a;&#x2a;&#x2a;</td>
<td align="left">1</td>
<td align="left"/>
<td align="left"/>
<td align="left"/>
</tr>
<tr>
<td align="left">FDI</td>
<td align="left">0.030</td>
<td align="left">0.141&#x2a;&#x2a;&#x2a;</td>
<td align="left">0.295&#x2a;&#x2a;&#x2a;</td>
<td align="left">0.043&#x2a;&#x2a;</td>
<td align="left">0.260&#x2a;&#x2a;&#x2a;</td>
<td align="left">1</td>
<td align="left"/>
<td align="left"/>
</tr>
<tr>
<td align="left">PCFE</td>
<td align="left">0.002</td>
<td align="left">&#x2212;0.019</td>
<td align="left">0.063&#x2a;&#x2a;&#x2a;</td>
<td align="left">0.395&#x2a;&#x2a;&#x2a;</td>
<td align="left">0.275&#x2a;&#x2a;&#x2a;</td>
<td align="left">0.017</td>
<td align="left">1</td>
<td align="left"/>
</tr>
<tr>
<td align="left">ERI</td>
<td align="left">0.010</td>
<td align="left">&#x2212;0.071&#x2a;&#x2a;&#x2a;</td>
<td align="left">&#x2212;0.115&#x2a;&#x2a;&#x2a;</td>
<td align="left">0.060&#x2a;&#x2a;&#x2a;</td>
<td align="left">0.044&#x2a;&#x2a;</td>
<td align="left">&#x2212;0.097&#x2a;&#x2a;&#x2a;</td>
<td align="left">0.133&#x2a;&#x2a;&#x2a;</td>
<td align="left">1</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>Note: Pearson correlation coefficients are reported. &#x2a;&#x2a;&#x2a;p &#x3c; 0.01, &#x2a;&#x2a;p &#x3c; 0.05, &#x2a;p &#x3c; 0.1.</p>
</fn>
</table-wrap-foot>
</table-wrap>
</sec>
<sec id="s4-3">
<title>4.3 Multicollinearity test</title>
<p>Multicollinearity refers to a strong correlation among the explanatory variables in a regression analysis, which may result in unstable coefficient estimates and reduced statistical significance. The Variance Inflation Factor (VIF) test is commonly used to detect multicollinearity. Here, we applied the VIF test to examine the multicollinearity among the explanatory variables. As shown in <xref ref-type="table" rid="T3">Table 3</xref>, all the VIF values were below the critical threshold of 10, indicating that multicollinearity was not a concern. Therefore, multicollinearity does not threaten the validity of the empirical results.</p>
<table-wrap id="T3" position="float">
<label>TABLE 3</label>
<caption>
<p>VIF tes<bold>t</bold>.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="left">Variables</th>
<th align="left">VIF</th>
<th align="left">1/VIF</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">LRM</td>
<td align="left">1.060</td>
<td align="left">0.941</td>
</tr>
<tr>
<td align="left">PD</td>
<td align="left">1.200</td>
<td align="left">0.831</td>
</tr>
<tr>
<td align="left">FD</td>
<td align="left">1.740</td>
<td align="left">0.573</td>
</tr>
<tr>
<td align="left">HC</td>
<td align="left">1.700</td>
<td align="left">0.588</td>
</tr>
<tr>
<td align="left">FDI</td>
<td align="left">1.190</td>
<td align="left">0.844</td>
</tr>
<tr>
<td align="left">PCFE</td>
<td align="left">1.210</td>
<td align="left">0.829</td>
</tr>
<tr>
<td align="left">ERI</td>
<td align="left">1.040</td>
<td align="left">0.958</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s4-4">
<title>4.4 Baseline regression analysis</title>
<p>The baseline regression employed a two-way fixed effects model and adopted a stepwise regression approach. The results of <xref ref-type="disp-formula" rid="e6">Equation 6</xref> are presented in <xref ref-type="table" rid="T4">Table 4</xref>. In the first step, the control variables were excluded. The estimation results show that the coefficient of the variable LRM (&#x3b2;<sub>1</sub>) is negative and statistically significant at the 1% level. In the second step, after including the control variables, the coefficient of LRM (&#x3b2;<sub>1</sub>) remains significantly negative at the 1% level (coefficient &#x3d; -0.001, p &#x3c; 0.01). Therefore, <xref ref-type="statement" rid="H1">Hypothesis 1</xref> is supported, confirming that LRM significantly reduces UCEE.</p>
<table-wrap id="T4" position="float">
<label>TABLE 4</label>
<caption>
<p>Baseline regressio<bold>n</bold>.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th rowspan="2" align="left">Variables</th>
<th align="left">(1)</th>
<th align="left">(2)</th>
</tr>
<tr>
<th align="left">UCEE</th>
<th align="left">UCEE</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">LRM</td>
<td align="left">&#x2212;0.001&#x2a;&#x2a;&#x2a;</td>
<td align="left">&#x2212;0.001&#x2a;&#x2a;&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(-3.11)</td>
<td align="left">(-2.96)</td>
</tr>
<tr>
<td align="left">PD</td>
<td align="left"/>
<td align="left">0.000</td>
</tr>
<tr>
<td align="left"/>
<td align="left"/>
<td align="left">(1.53)</td>
</tr>
<tr>
<td align="left">FD</td>
<td align="left"/>
<td align="left">&#x2212;0.005</td>
</tr>
<tr>
<td align="left"/>
<td align="left"/>
<td align="left">(-1.45)</td>
</tr>
<tr>
<td align="left">HC</td>
<td align="left"/>
<td align="left">0.010&#x2a;&#x2a;&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left"/>
<td align="left">(2.77)</td>
</tr>
<tr>
<td align="left">FDI</td>
<td align="left"/>
<td align="left">&#x2212;0.001</td>
</tr>
<tr>
<td align="left"/>
<td align="left"/>
<td align="left">(-0.77)</td>
</tr>
<tr>
<td align="left">PCFE</td>
<td align="left"/>
<td align="left">&#x2212;0.000</td>
</tr>
<tr>
<td align="left"/>
<td align="left"/>
<td align="left">(-0.55)</td>
</tr>
<tr>
<td align="left">ERI</td>
<td align="left"/>
<td align="left">0.002</td>
</tr>
<tr>
<td align="left"/>
<td align="left"/>
<td align="left">(0.30)</td>
</tr>
<tr>
<td align="left">Constant</td>
<td align="left">0.347&#x2a;&#x2a;&#x2a;</td>
<td align="left">0.322&#x2a;&#x2a;&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(50.04)</td>
<td align="left">(11.71)</td>
</tr>
<tr>
<td align="left">Observations</td>
<td align="left">3,004</td>
<td align="left">3,004</td>
</tr>
<tr>
<td align="left">R-squared</td>
<td align="left">0.585</td>
<td align="left">0.587</td>
</tr>
<tr>
<td align="left">City FE</td>
<td align="left">YES</td>
<td align="left">YES</td>
</tr>
<tr>
<td align="left">Year FE</td>
<td align="left">YES</td>
<td align="left">YES</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>Note: &#x2a;&#x2a;&#x2a;p &#x3c; 0.01, &#x2a;&#x2a;p &#x3c; 0.05, &#x2a;p &#x3c; 0.1; robust t-statistics in parentheses.</p>
</fn>
</table-wrap-foot>
</table-wrap>
</sec>
<sec id="s4-5">
<title>4.5 Robustness and endogeneity tests</title>
<sec id="s4-5-1">
<title>4.5.1 Alternative measurement of independent variables</title>
<p>To ensure the robustness of the empirical findings, we replace the core independent variable with an alternative measure: the ratio of land concession revenue to urban construction land area. Land concession revenue data were compiled from the National Bureau of Statistics of China, the <italic>China Land and Resources Yearbook</italic>, and official disclosures from local governments. The results in Column (1) of <xref ref-type="table" rid="T5">Table 5</xref> show that the coefficient remains significantly negative at the 1% level. This confirmed the reliability of the core conclusions.</p>
<table-wrap id="T5" position="float">
<label>TABLE 5</label>
<caption>
<p>Robustness test<bold>s</bold>.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th rowspan="3" align="left">Variables</th>
<th align="left">Alternative independent variable</th>
<th align="left">Excluding the impact of COVID-19</th>
</tr>
<tr>
<th align="left">(1)</th>
<th align="left">(2)</th>
</tr>
<tr>
<th align="left">UCEE</th>
<th align="left">UCEE</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">LCR</td>
<td align="left">&#x2212;0.001&#x2a;&#x2a;&#x2a;</td>
<td align="left"/>
</tr>
<tr>
<td align="left"/>
<td align="left">(-3.64)</td>
<td align="left"/>
</tr>
<tr>
<td align="left">LRM</td>
<td align="left"/>
<td align="left">&#x2212;0.001&#x2a;&#x2a;&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left"/>
<td align="left">(-2.92)</td>
</tr>
<tr>
<td align="left">PD</td>
<td align="left">0.000&#x2a;</td>
<td align="left">0.000</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(1.67)</td>
<td align="left">(1.17)</td>
</tr>
<tr>
<td align="left">FD</td>
<td align="left">&#x2212;0.005</td>
<td align="left">&#x2212;0.005</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(-1.55)</td>
<td align="left">(-1.40)</td>
</tr>
<tr>
<td align="left">HC</td>
<td align="left">0.011&#x2a;&#x2a;&#x2a;</td>
<td align="left">0.008&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(2.86)</td>
<td align="left">(1.83)</td>
</tr>
<tr>
<td align="left">FDI</td>
<td align="left">&#x2212;0.001</td>
<td align="left">&#x2212;0.001</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(-0.55)</td>
<td align="left">(-0.56)</td>
</tr>
<tr>
<td align="left">PCFE</td>
<td align="left">&#x2212;0.000</td>
<td align="left">&#x2212;0.000</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(-0.50)</td>
<td align="left">(-0.19)</td>
</tr>
<tr>
<td align="left">ERI</td>
<td align="left">0.002</td>
<td align="left">0.002</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(0.28)</td>
<td align="left">(0.29)</td>
</tr>
<tr>
<td align="left">Constant</td>
<td align="left">0.299&#x2a;&#x2a;&#x2a;</td>
<td align="left">0.324&#x2a;&#x2a;&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(11.36)</td>
<td align="left">(10.27)</td>
</tr>
<tr>
<td align="left">Observations</td>
<td align="left">3,000</td>
<td align="left">2,597</td>
</tr>
<tr>
<td align="left">R-squared</td>
<td align="left">0.586</td>
<td align="left">0.606</td>
</tr>
<tr>
<td align="left">City FE</td>
<td align="left">YES</td>
<td align="left">YES</td>
</tr>
<tr>
<td align="left">Year FE</td>
<td align="left">YES</td>
<td align="left">YES</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>Note: &#x2a;&#x2a;&#x2a;p &#x3c; 0.01, &#x2a;&#x2a;p &#x3c; 0.05, &#x2a;p &#x3c; 0.1; robust t-statistics in parentheses. LCR, land concession revenue.</p>
</fn>
</table-wrap-foot>
</table-wrap>
</sec>
<sec id="s4-5-2">
<title>4.5.2 Robustness test: excluding the impact of COVID-19</title>
<p>To further verify robustness, we excluded observations from 2020 to 2021, which were significantly affected by the COVID-19 pandemic. The regression results reported in column (2) of <xref ref-type="table" rid="T5">Table 5</xref> indicate that the core findings remain stable and are not influenced by major external shocks, thereby reinforcing the robustness of the study.</p>
</sec>
<sec id="s4-5-3">
<title>4.5.3 Endogeneity test: Instrumental variable approach</title>
<p>To address potential endogeneity issues arising from omitted variables or measurement errors, we employed the two-stage least squares (2SLS) method with an instrumental variable (IV). We constructed IV as the interaction term between the average terrain slope of a city and its economic growth target for the corresponding year. The terrain slope data were sourced from the <italic>Gridded Dataset of Terrain Relief Degree in China</italic>, and the economic growth target was obtained from local government work reports. The theoretical rationale is as follows: terrain conditions affect the amount of developable land, while the economic growth target reflects the preference of the local government for land development intensity. Their interaction captures the pressure a city faces in achieving its economic goals under specific topographic constraints, which in turn affects its land allocation behavior. Therefore, this interaction term is theoretically correlated with land-resource misallocation. Simultaneously, it does not directly influence carbon emission efficiency but only affects it indirectly through the land allocation mechanism. Given that the main effects of both terrain slope and economic growth targets are controlled, the exogeneity assumption of the instrument is also satisfied. This variable was calculated by multiplying the average slope (in degrees) with the economic growth target of the by the city (in percentages) and scaling the product by a factor of 100.</p>
<p>
<xref ref-type="table" rid="T6">Table 6</xref> presents the estimation results. Column (1) reports the first-stage regression, in which the coefficient of the instrumental variable is 0.091 and is significantly positive at the 5% level (<italic>p</italic> &#x3c; 0.05), confirming its relevance in explaining LRM. In Column (2), after incorporating the instrumental variable, the second-stage regression results show that the coefficient of LRM remains negative (&#x2212;0.020) and significant at the 10% level (<italic>p</italic> &#x3c; 0.1), indicating that the core conclusion remains robust after accounting for endogeneity.</p>
<table-wrap id="T6" position="float">
<label>TABLE 6</label>
<caption>
<p>Endogeneity test: 2SL<bold>S</bold>.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th rowspan="3" align="left">Variables</th>
<th align="left">First stage</th>
<th align="left">Second stage</th>
</tr>
<tr>
<th align="left">(1)</th>
<th align="left">(2)</th>
</tr>
<tr>
<th align="left">LRM</th>
<th align="left">UCEE</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">IV</td>
<td align="left">0.091<sup>&#x2a;&#x2a;</sup>
</td>
<td align="left"/>
</tr>
<tr>
<td align="left"/>
<td align="left">(0.04)</td>
<td align="left"/>
</tr>
<tr>
<td align="left">LRM</td>
<td align="left"/>
<td align="left">&#x2212;0.020<sup>&#x2a;</sup>
</td>
</tr>
<tr>
<td align="left"/>
<td align="left"/>
<td align="left">(0.01)</td>
</tr>
<tr>
<td align="left">PD</td>
<td align="left">&#x2212;0.003<sup>&#x2a;&#x2a;</sup>
</td>
<td align="left">&#x2212;0.000</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(0.00)</td>
<td align="left">(0.00)</td>
</tr>
<tr>
<td align="left">FD</td>
<td align="left">0.413<sup>&#x2a;&#x2a;</sup>
</td>
<td align="left">0.002</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(0.17)</td>
<td align="left">(0.01)</td>
</tr>
<tr>
<td align="left">HC</td>
<td align="left">&#x2212;0.187</td>
<td align="left">0.006</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(0.17)</td>
<td align="left">(0.01)</td>
</tr>
<tr>
<td align="left">FDI</td>
<td align="left">&#x2212;0.206<sup>&#x2a;&#x2a;</sup>
</td>
<td align="left">&#x2212;0.005<sup>&#x2a;</sup>
</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(0.08)</td>
<td align="left">(0.00)</td>
</tr>
<tr>
<td align="left">PCFE</td>
<td align="left">0.000</td>
<td align="left">&#x2212;0.000</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(0.00)</td>
<td align="left">(0.00)</td>
</tr>
<tr>
<td align="left">ERI</td>
<td align="left">0.550</td>
<td align="left">0.013</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(0.36)</td>
<td align="left">(0.01)</td>
</tr>
<tr>
<td align="left">Observations</td>
<td align="left">2,987</td>
<td align="left">2,987</td>
</tr>
<tr>
<td align="left">R2</td>
<td align="left"/>
<td align="left">&#x2212;0.83</td>
</tr>
<tr>
<td align="left">F</td>
<td align="left">5.03</td>
<td align="left">1.54</td>
</tr>
<tr>
<td align="left">CD Wald F</td>
<td align="left">6.33</td>
<td align="left"/>
</tr>
<tr>
<td align="left">SW S stat.</td>
<td align="left">9.27</td>
<td align="left"/>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>Note: &#x2a;&#x2a;&#x2a;p &#x3c; 0.01, &#x2a;&#x2a;p &#x3c; 0.05, &#x2a;p &#x3c; 0.1; robust t-statistics in parentheses. IV: the interaction term between the average terrain slope of a city and its economic growth target for the corresponding year.</p>
</fn>
</table-wrap-foot>
</table-wrap>
</sec>
</sec>
<sec id="s4-6">
<title>4.6 Mechanism analysis</title>
<p>Given the potential over-identification issues associated with the traditional three-step approach to causal mechanism identification, we adopt a revised two-step empirical strategy inspired by <xref ref-type="bibr" rid="B45">Zhou et al. (2023)</xref> and <xref ref-type="bibr" rid="B28">Qing et al. (2024)</xref>. This approach was designed to empirically test the mechanism by which LRM affects UCEE. The first step involved empirically testing the effect of LRM on the two mediating variables of ISU and GTI. In the second step, rather than conducting an additional regression analysis, we rely on existing authoritative literature and logical inferences to verify the established correlations between the mediating variables and carbon emissions efficiency. This allowed us to infer the mediating role of ISU and GTI in the relationship between LRM and UCEE.</p>
<p>The corresponding models are presented in <xref ref-type="disp-formula" rid="e7">Equations 7</xref>, <xref ref-type="disp-formula" rid="e8">8</xref>:<disp-formula id="e7">
<mml:math id="m8">
<mml:mrow>
<mml:mi>I</mml:mi>
<mml:mi>S</mml:mi>
<mml:msub>
<mml:mi>U</mml:mi>
<mml:mrow>
<mml:mi>c</mml:mi>
<mml:mi>t</mml:mi>
</mml:mrow>
</mml:msub>
<mml:mo>&#x3d;</mml:mo>
<mml:msub>
<mml:mi>&#x3b1;</mml:mi>
<mml:mi>c</mml:mi>
</mml:msub>
<mml:mo>&#x2b;</mml:mo>
<mml:msub>
<mml:mi>&#x3b1;</mml:mi>
<mml:mi>t</mml:mi>
</mml:msub>
<mml:mo>&#x2b;</mml:mo>
<mml:msub>
<mml:mi>&#x3b1;</mml:mi>
<mml:mn>0</mml:mn>
</mml:msub>
<mml:mo>&#x2b;</mml:mo>
<mml:msub>
<mml:mi>&#x3b2;</mml:mi>
<mml:mn>1</mml:mn>
</mml:msub>
<mml:mi>L</mml:mi>
<mml:mi>R</mml:mi>
<mml:msub>
<mml:mi>M</mml:mi>
<mml:mrow>
<mml:mi>c</mml:mi>
<mml:mi>t</mml:mi>
</mml:mrow>
</mml:msub>
<mml:mo>&#x2b;</mml:mo>
<mml:mi>&#x3b3;</mml:mi>
<mml:msub>
<mml:mi>X</mml:mi>
<mml:mrow>
<mml:mi>c</mml:mi>
<mml:mi>t</mml:mi>
</mml:mrow>
</mml:msub>
<mml:mo>&#x2b;</mml:mo>
<mml:msub>
<mml:mi>&#x3b5;</mml:mi>
<mml:mrow>
<mml:mi>c</mml:mi>
<mml:mi>t</mml:mi>
</mml:mrow>
</mml:msub>
</mml:mrow>
</mml:math>
<label>(7)</label>
</disp-formula>
<disp-formula id="e8">
<mml:math id="m9">
<mml:mrow>
<mml:mi>G</mml:mi>
<mml:mi>T</mml:mi>
<mml:msub>
<mml:mi>I</mml:mi>
<mml:mrow>
<mml:mi>c</mml:mi>
<mml:mi>t</mml:mi>
</mml:mrow>
</mml:msub>
<mml:mo>&#x3d;</mml:mo>
<mml:msub>
<mml:mi>&#x3b1;</mml:mi>
<mml:mi>c</mml:mi>
</mml:msub>
<mml:mo>&#x2b;</mml:mo>
<mml:msub>
<mml:mi>&#x3b1;</mml:mi>
<mml:mi>t</mml:mi>
</mml:msub>
<mml:mo>&#x2b;</mml:mo>
<mml:msub>
<mml:mi>&#x3b1;</mml:mi>
<mml:mn>0</mml:mn>
</mml:msub>
<mml:mo>&#x2b;</mml:mo>
<mml:msub>
<mml:mi>&#x3b2;</mml:mi>
<mml:mn>1</mml:mn>
</mml:msub>
<mml:mi>L</mml:mi>
<mml:mi>R</mml:mi>
<mml:msub>
<mml:mi>M</mml:mi>
<mml:mrow>
<mml:mi>c</mml:mi>
<mml:mi>t</mml:mi>
</mml:mrow>
</mml:msub>
<mml:mo>&#x2b;</mml:mo>
<mml:mi>&#x3b3;</mml:mi>
<mml:msub>
<mml:mi>X</mml:mi>
<mml:mrow>
<mml:mi>c</mml:mi>
<mml:mi>t</mml:mi>
</mml:mrow>
</mml:msub>
<mml:mo>&#x2b;</mml:mo>
<mml:msub>
<mml:mi>&#x3b5;</mml:mi>
<mml:mrow>
<mml:mi>c</mml:mi>
<mml:mi>t</mml:mi>
</mml:mrow>
</mml:msub>
</mml:mrow>
</mml:math>
<label>(8)</label>
</disp-formula>
</p>
<p>
<xref ref-type="table" rid="T7">Table 7</xref> presents the results. Column (1) shows that the coefficient of LRM on ISU is negative and statistically significant at the 5% level (coefficient &#x3d; &#x2212;0.002, <italic>p</italic> &#x3c; 0.05), indicating that LRM inhibits ISU. Column (2) shows that the coefficient of LRM on GTI is also negative and significant at the 5% level (coefficient &#x3d; &#x2212;0.005, <italic>p</italic> &#x3c; 0.05), suggesting that LRM impedes the development of GTI.</p>
<table-wrap id="T7" position="float">
<label>TABLE 7</label>
<caption>
<p>Mechanism tes<bold>t</bold>.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th rowspan="2" align="left">Variables</th>
<th align="left">(1)</th>
<th align="left">(2)</th>
</tr>
<tr>
<th align="left">ISU</th>
<th align="left">GTI</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">LRM</td>
<td align="left">&#x2212;0.002&#x2a;&#x2a;</td>
<td align="left">&#x2212;0.005&#x2a;&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(-2.58)</td>
<td align="left">(-2.32)</td>
</tr>
<tr>
<td align="left">PD</td>
<td align="left">0.000</td>
<td align="left">0.000&#x2a;&#x2a;&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(0.29)</td>
<td align="left">(4.16)</td>
</tr>
<tr>
<td align="left">FD</td>
<td align="left">0.157&#x2a;&#x2a;&#x2a;</td>
<td align="left">&#x2212;0.090&#x2a;&#x2a;&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(9.29)</td>
<td align="left">(-5.23)</td>
</tr>
<tr>
<td align="left">HC</td>
<td align="left">0.036&#x2a;&#x2a;&#x2a;</td>
<td align="left">0.021</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(3.01)</td>
<td align="left">(1.34)</td>
</tr>
<tr>
<td align="left">FDI</td>
<td align="left">0.001</td>
<td align="left">0.026&#x2a;&#x2a;&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(0.11)</td>
<td align="left">(3.62)</td>
</tr>
<tr>
<td align="left">PCFE</td>
<td align="left">&#x2212;0.000</td>
<td align="left">0.000&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(-0.40)</td>
<td align="left">(1.65)</td>
</tr>
<tr>
<td align="left">ERI</td>
<td align="left">0.003</td>
<td align="left">&#x2212;0.086&#x2a;&#x2a;&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(0.19)</td>
<td align="left">(-2.75)</td>
</tr>
<tr>
<td align="left">Constant</td>
<td align="left">0.597&#x2a;&#x2a;&#x2a;</td>
<td align="left">4.603&#x2a;&#x2a;&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(8.24)</td>
<td align="left">(41.77)</td>
</tr>
<tr>
<td align="left">Observations</td>
<td align="left">3,004</td>
<td align="left">3,004</td>
</tr>
<tr>
<td align="left">R-squared</td>
<td align="left">0.885</td>
<td align="left">0.960</td>
</tr>
<tr>
<td align="left">City FE</td>
<td align="left">YES</td>
<td align="left">YES</td>
</tr>
<tr>
<td align="left">Year FE</td>
<td align="left">YES</td>
<td align="left">YES</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>Note: &#x2a;&#x2a;&#x2a;p &#x3c; 0.01, &#x2a;&#x2a;p &#x3c; 0.05, &#x2a;p &#x3c; 0.1; robust t-statistics in parentheses. ISU, industrial structure upgrading; GTI, green technological innovation.</p>
</fn>
</table-wrap-foot>
</table-wrap>
<p>Regarding the correlation between ISU, GTI, and UCEE, experts and scholars provided substantial evidence. Studies showed that the advancement and upgrading of industrial structures can, to a certain extent, suppress carbon emissions in neighboring regions and significantly improve urban carbon emission efficiency (<xref ref-type="bibr" rid="B9">Deng et al., 2023</xref>; <xref ref-type="bibr" rid="B6">Cheng Y. et al., 2025</xref>). <xref ref-type="bibr" rid="B24">Miao et al. (2017)</xref> and <xref ref-type="bibr" rid="B20">Liao et al. (2024)</xref> empirically validated the relationship between Green Technological Innovation and urban carbon emission efficiency. Their findings indicate that green innovation plays a key role in promoting low-carbon transformation and has a significantly positive impact on improving UCEE, a view widely acknowledged in academic circles.</p>
<p>Summarily, LRM impedes ISU, thereby suppressing improvements in UCEE; similarly, it hinders the advancement of GTI, which in turn limits the enhancement of UCEE. These two causal pathways are well substantiated, thus confirming <xref ref-type="statement" rid="H2 H3">hypotheses 2, 3</xref>.</p>
</sec>
<sec id="s4-7">
<title>4.7 Heterogeneity analysis</title>
<sec id="s4-7-1">
<title>4.7.1 Geographic heterogeneity of cities</title>
<p>To further examine the spatial differences in the impact of LRM on UCEE, we followed the approach of <xref ref-type="bibr" rid="B44">Zhou et al. (2022)</xref> and conducted regional regressions based on the eastern, central, and western regions of China. The regression results are presented in <xref ref-type="table" rid="T8">Table 8</xref>.</p>
<table-wrap id="T8" position="float">
<label>TABLE 8</label>
<caption>
<p>Heterogeneity by geographic locatio<bold>n</bold>.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th rowspan="2" align="left">Variables</th>
<th align="left">(1)</th>
<th align="left">(2)</th>
<th align="left">(3)</th>
</tr>
<tr>
<th align="left">Eastern</th>
<th align="left">Central</th>
<th align="left">Western</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">LRM</td>
<td align="left">0.000</td>
<td align="left">&#x2212;0.002<sup>&#x2a;&#x2a;</sup>
</td>
<td align="left">&#x2212;0.001<sup>&#x2a;</sup>
</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(0.04)</td>
<td align="left">(-2.58)</td>
<td align="left">(-1.95)</td>
</tr>
<tr>
<td align="left">PD</td>
<td align="left">0.000<sup>&#x2a;&#x2a;&#x2a;</sup>
</td>
<td align="left">&#x2212;0.000</td>
<td align="left">0.000</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(2.64)</td>
<td align="left">(-0.21)</td>
<td align="left">(0.51)</td>
</tr>
<tr>
<td align="left">FD</td>
<td align="left">0.004</td>
<td align="left">&#x2212;0.007</td>
<td align="left">&#x2212;0.021<sup>&#x2a;&#x2a;</sup>
</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(0.84)</td>
<td align="left">(-1.06)</td>
<td align="left">(-2.02)</td>
</tr>
<tr>
<td align="left">HC</td>
<td align="left">&#x2212;0.003</td>
<td align="left">0.009</td>
<td align="left">0.024<sup>&#x2a;&#x2a;&#x2a;</sup>
</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(-0.50)</td>
<td align="left">(1.61)</td>
<td align="left">(2.96)</td>
</tr>
<tr>
<td align="left">FDI</td>
<td align="left">0.002</td>
<td align="left">&#x2212;0.007<sup>&#x2a;&#x2a;</sup>
</td>
<td align="left">0.000</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(0.88)</td>
<td align="left">(-1.98)</td>
<td align="left">(0.10)</td>
</tr>
<tr>
<td align="left">PCFE</td>
<td align="left">&#x2212;0.000</td>
<td align="left">0.000</td>
<td align="left">&#x2212;0.000</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(-0.74)</td>
<td align="left">(0.61)</td>
<td align="left">(-0.97)</td>
</tr>
<tr>
<td align="left">ERI</td>
<td align="left">0.024<sup>&#x2a;&#x2a;</sup>
</td>
<td align="left">&#x2212;0.011</td>
<td align="left">0.000</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(2.02)</td>
<td align="left">(-1.05)</td>
<td align="left">(0.02)</td>
</tr>
<tr>
<td align="left">Constant</td>
<td align="left">0.241<sup>&#x2a;&#x2a;&#x2a;</sup>
</td>
<td align="left">0.388<sup>&#x2a;&#x2a;&#x2a;</sup>
</td>
<td align="left">0.350<sup>&#x2a;&#x2a;&#x2a;</sup>
</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(5.29)</td>
<td align="left">(8.79)</td>
<td align="left">(7.36)</td>
</tr>
<tr>
<td align="left">Observations</td>
<td align="left">1,116</td>
<td align="left">1,163</td>
<td align="left">725</td>
</tr>
<tr>
<td align="left">R-squared</td>
<td align="left">0.637</td>
<td align="left">0.537</td>
<td align="left">0.619</td>
</tr>
<tr>
<td align="left">City FE</td>
<td align="left">YES</td>
<td align="left">YES</td>
<td align="left">YES</td>
</tr>
<tr>
<td align="left">Year FE</td>
<td align="left">YES</td>
<td align="left">YES</td>
<td align="left">YES</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>Note: &#x2a;&#x2a;&#x2a;p &#x3c; 0.01, &#x2a;&#x2a;p &#x3c; 0.05, &#x2a;p &#x3c; 0.1; robust t-statistics in parentheses.</p>
</fn>
</table-wrap-foot>
</table-wrap>
<p>These findings indicate significant regional heterogeneity in the impact of LRM on carbon emission efficiency. Specifically, in the Central and Western regions, the coefficients of the land misallocation variables were negative and statistically significant at the 5% and 10% levels, respectively. This suggests that LRM significantly suppresses improvements in UCEE in these regions. Contrastingly, the coefficient in the eastern region is statistically insignificant, which may be attributed to the more developed institutional environment of the region and higher factor allocation efficiency, thus partially offsetting the negative effects of land misallocation.</p>
<p>This result aligns with that of the known regional differences in terms of administrative governance capacity, land market development, and industrial maturity. Cities in the central and western regions are more reliant on administratively driven land allocation and industrial expansion for their economic development, making them more vulnerable to inefficient land use. Such distortions in land allocation hinder ISU and weaken the green innovation ecosystem, ultimately exerting a negative impact on carbon emission efficiency.</p>
<p>Therefore, policies aimed at improving UCEE should fully consider the regional disparities. Particularly, greater emphasis should be placed on strengthening land market institutions and optimizing land use structures in Central and Western China to mitigate the environmental externalities resulting from resource misallocation.</p>
</sec>
<sec id="s4-7-2">
<title>4.7.2 Heterogeneity by city size</title>
<p>To further investigate whether the impact of LRM on UCEE varies by city population size, we conducted group regressions based on city size, following the classification criteria proposed by <xref ref-type="bibr" rid="B2">An (2024)</xref>. According to the <italic>Notice of the State Council on Adjusting the Standards for City Size Classification</italic> (Guo Fa (2014) No. 51), cities with a permanent urban population of one million or more are categorized as large cities, whereas those with fewer than one million residents are classified as small- and medium-sized cities. <xref ref-type="table" rid="T9">Table 9</xref> presents the estimation results for the two groups.</p>
<table-wrap id="T9" position="float">
<label>TABLE 9</label>
<caption>
<p>Heterogeneity by city siz<bold>e</bold>.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th rowspan="2" align="left">Variables</th>
<th align="left">(1)</th>
<th align="left">(2)</th>
</tr>
<tr>
<th align="left">Large cities</th>
<th align="left">Small and medium cities</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">LRM</td>
<td align="left">&#x2212;0.001</td>
<td align="left">&#x2212;0.001&#x2a;&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(-0.98)</td>
<td align="left">(-2.47)</td>
</tr>
<tr>
<td align="left">PD</td>
<td align="left">0.000</td>
<td align="left">0.000&#x2a;&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(0.94)</td>
<td align="left">(2.36)</td>
</tr>
<tr>
<td align="left">FD</td>
<td align="left">0.009</td>
<td align="left">&#x2212;0.010&#x2a;&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(1.45)</td>
<td align="left">(-2.41)</td>
</tr>
<tr>
<td align="left">HC</td>
<td align="left">&#x2212;0.003</td>
<td align="left">0.021&#x2a;&#x2a;&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(-0.53)</td>
<td align="left">(4.10)</td>
</tr>
<tr>
<td align="left">FDI</td>
<td align="left">0.003</td>
<td align="left">&#x2212;0.004&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(0.98)</td>
<td align="left">(-1.80)</td>
</tr>
<tr>
<td align="left">PCFE</td>
<td align="left">0.000</td>
<td align="left">&#x2212;0.000</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(0.05)</td>
<td align="left">(-0.92)</td>
</tr>
<tr>
<td align="left">ERI</td>
<td align="left">&#x2212;0.005</td>
<td align="left">0.006</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(-0.37)</td>
<td align="left">(0.76)</td>
</tr>
<tr>
<td align="left">Constant</td>
<td align="left">0.285&#x2a;&#x2a;&#x2a;</td>
<td align="left">0.314&#x2a;&#x2a;&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(4.24)</td>
<td align="left">(11.43)</td>
</tr>
<tr>
<td align="left">Observations</td>
<td align="left">846</td>
<td align="left">2,158</td>
</tr>
<tr>
<td align="left">R-squared</td>
<td align="left">0.504</td>
<td align="left">0.616</td>
</tr>
<tr>
<td align="left">City FE</td>
<td align="left">YES</td>
<td align="left">YES</td>
</tr>
<tr>
<td align="left">Year FE</td>
<td align="left">YES</td>
<td align="left">YES</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>Note: &#x2a;&#x2a;&#x2a;p &#x3c; 0.01, &#x2a;&#x2a;p &#x3c; 0.05, &#x2a;p &#x3c; 0.1; robust t-statistics in parentheses.</p>
</fn>
</table-wrap-foot>
</table-wrap>
<p>The results revealed significant heterogeneity based on city size. Specifically, in small and medium-sized cities, the coefficient of the Mismatch variable was significantly negative at the 5% level, indicating that LRM significantly suppressed improvements in carbon emission efficiency. Contrastingly, the effect is statistically insignificant in large cities, suggesting that the impact is weaker or negligible in these contexts.</p>
<p>This difference may stem from the disparities in governance capacity, industrial maturity, and institutional flexibility between large and small cities. Large cities generally possess more efficient land markets, better regulatory frameworks, and stronger technological infrastructures, enabling them to absorb or offset the distortions caused by land misallocation. Comparatively, small- and medium-sized cities are more constrained by administrative land allocation mechanisms and are more susceptible to the inefficiencies of distorted land use patterns, which in turn limits their ability to pursue low-carbon transformation.</p>
<p>These findings highlighted the need for different policy interventions. Large cities should focus on optimizing existing mechanisms to enhance carbon efficiency, whereas small- and medium-sized cities urgently need to address structural distortions in land allocation to unlock their potential to improve carbon emission performance.</p>
</sec>
<sec id="s4-7-3">
<title>4.7.3 Heterogeneity by resource endowment type</title>
<p>To examine whether the impact of LRM on UCEE differs between resource-based and non-resource-based cities, we followed the classification method of <xref ref-type="bibr" rid="B42">Zhang Y. et al. (2024)</xref>. Based on the <italic>National Plan for the Sustainable Development of Resource-Based Cities (2003&#x2013;2020)</italic>, the sample cities were divided into two subgroups, resource-based and non-resource-based cities, and separate regressions were conducted. According to official documents, resource-based cities refer to those that have long relied on the extraction and primary processing of natural resources such as coal, petroleum, and non-ferrous metals as their primary economic foundation. <xref ref-type="table" rid="T10">Table 10</xref> presents the regression results for both city types.</p>
<table-wrap id="T10" position="float">
<label>TABLE 10</label>
<caption>
<p>Heterogeneity by resource endowment typ<bold>e</bold>.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th rowspan="2" align="left">Variables</th>
<th align="left">(1)</th>
<th align="left">(2)</th>
</tr>
<tr>
<th align="left">Resource-based cities</th>
<th align="left">Non-resource-based cities</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">LRM</td>
<td align="left">&#x2212;0.001</td>
<td align="left">&#x2212;0.001&#x2a;&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(-1.43)</td>
<td align="left">(-2.38)</td>
</tr>
<tr>
<td align="left">PD</td>
<td align="left">0.000</td>
<td align="left">0.000&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(0.09)</td>
<td align="left">(1.86)</td>
</tr>
<tr>
<td align="left">FD</td>
<td align="left">&#x2212;0.001</td>
<td align="left">&#x2212;0.007&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(-0.14)</td>
<td align="left">(-1.68)</td>
</tr>
<tr>
<td align="left">HC</td>
<td align="left">0.003</td>
<td align="left">0.013&#x2a;&#x2a;&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(0.60)</td>
<td align="left">(2.66)</td>
</tr>
<tr>
<td align="left">FDI</td>
<td align="left">&#x2212;0.003</td>
<td align="left">&#x2212;0.001</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(-0.89)</td>
<td align="left">(-0.41)</td>
</tr>
<tr>
<td align="left">PCFE</td>
<td align="left">0.000</td>
<td align="left">&#x2212;0.000</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(1.45)</td>
<td align="left">(-1.39)</td>
</tr>
<tr>
<td align="left">ERI</td>
<td align="left">&#x2212;0.009</td>
<td align="left">0.009</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(-0.97)</td>
<td align="left">(0.99)</td>
</tr>
<tr>
<td align="left">Constant</td>
<td align="left">0.336&#x2a;&#x2a;&#x2a;</td>
<td align="left">0.305&#x2a;&#x2a;&#x2a;</td>
</tr>
<tr>
<td align="left"/>
<td align="left">(9.41)</td>
<td align="left">(7.57)</td>
</tr>
<tr>
<td align="left">Observations</td>
<td align="left">1,207</td>
<td align="left">1,797</td>
</tr>
<tr>
<td align="left">R-squared</td>
<td align="left">0.655</td>
<td align="left">0.532</td>
</tr>
<tr>
<td align="left">City FE</td>
<td align="left">YES</td>
<td align="left">YES</td>
</tr>
<tr>
<td align="left">Year FE</td>
<td align="left">YES</td>
<td align="left">YES</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>Note: &#x2a;&#x2a;&#x2a;p &#x3c; 0.01, &#x2a;&#x2a;p &#x3c; 0.05, &#x2a;p &#x3c; 0.1; robust t-statistics in parentheses.</p>
</fn>
</table-wrap-foot>
</table-wrap>
<p>The regression results reveal that the resource endowment type leads to significant heterogeneity in the effect of LRM on UCEE. Specifically, in non-resource-based cities, the coefficient of LRM variable was significantly negative at the 5% level (&#x2212;0.001, <italic>t</italic> &#x3d; &#x2212;2.38), indicating that LRM significantly hindered improvements in UCEE. Contrastingly, in resource-based cities, the coefficient is not statistically significant (&#x2212;0.001, <italic>t</italic> &#x3d; &#x2212;1.43), suggesting that in cities with strong resource dependence, LRM may not be a primary constraint on UCEE enhancement.</p>
<p>This discrepancy may be attributed to entrenched industrial structures and relatively rigid land-use policies in resource-based cities. In these cities, economic operations are often heavily influenced by state-led investment priorities and legacy infrastructure. Even if land allocation becomes more efficient, its effect may be offset by the dominance of resource-intensive, high-emissions industries. Comparatively, non-resource-based cities typically possess more diversified industrial structures and greater institutional flexibility, making them more responsive to land allocation distortions.</p>
<p>These findings emphasize the importance of designing differentiated policy frameworks. For non-resource-based cities, correcting LRM is the key to improving UCEE. However, for resource-based cities, more fundamental structural reforms, such as industrial transformation or the implementation of environmental compensation mechanisms, may be required to achieve sustainable low-carbon transition goals.</p>
</sec>
</sec>
</sec>
<sec sec-type="discussion" id="s5">
<title>5 Discussion</title>
<sec id="s5-1">
<title>5.1 Key findings</title>
<p>Based on panel data from Chinese cities, we constructed a two-way fixed effects model to systematically assess the impact of LRM on UCEE. Furthermore, it empirically examines two mediating mechanisms, ISU and GTI, through which misallocation exerts indirect effects. The main findings were as follows:</p>
<p>First, LRM significantly hinders the improvement of UCEE, confirming that such institutional distortions lead to higher carbon emissions per unit output. This finding is consistent with that of <xref ref-type="bibr" rid="B44">Zhou et al. (2022)</xref>, who showed that a higher degree of misallocation between industrial and commercial land is correlated with lower carbon efficiency. Similarly, <xref ref-type="bibr" rid="B6">Cheng Y. et al. (2025)</xref> quantitatively estimated that a 1% increase in the land misallocation index results in an average increase of 0.502% in urban carbon emissions. This implies that the oversupply of low-cost industrial land by the local governments aimed at rapid development promotes the expansion of energy-intensive industries, reduces energy efficiency, and substantially suppresses carbon emission efficiency (<xref ref-type="bibr" rid="B15">Han and Huang, 2022</xref>). Generally, the recent studies overwhelmingly confirms the significant negative effect of LRM on carbon efficiency. However, not all studies reached consistent conclusions. For instance, <xref ref-type="bibr" rid="B3">Chen and Yuan (2025)</xref> argued that the negative effect of land misallocation on carbon efficiency is significantly weakened in regions where land marketization reforms progressed. This finding suggests that in economically advanced regions with sound market mechanisms, the inhibitory effect of land misallocation is relatively weak. Therefore, differences in regional development stages and policy environments explain the variations in empirical results across studies.</p>
<p>Second, the mechanism analysis indicates that LRM reduces carbon emission efficiency by obstructing the transition of the industrial structure from high-carbon to low-carbon sectors, thereby inhibiting industrial upgrading. Numerous studies support the notion that barriers to industrial transformation are a critical transmission channel through which land misallocation affects carbon efficiency (<xref ref-type="bibr" rid="B44">Zhou et al., 2022</xref>; <xref ref-type="bibr" rid="B6">Cheng Y. et al., 2025</xref>). <xref ref-type="bibr" rid="B44">Zhou et al. (2022)</xref> explicitly stated that land misallocation delays industrial upgrading, increases the proportion of highly polluting and energy-intensive industries, and suppresses carbon efficiency improvements. <xref ref-type="bibr" rid="B6">Cheng Y. et al. (2025)</xref> further demonstrated through a mediation analysis that approximately 16.3% of the total effect of land misallocation is transmitted via changes in industrial structure. This provides additional evidence that land misallocation indirectly hinders the shift from high-carbon to low-carbon industries, thus lowering the CEs. However, <xref ref-type="bibr" rid="B6">Cheng Y. et al. (2025)</xref> also highlighted that industrial upgrading accounts for only a small part of the total effect, suggesting the existence of other influential mechanisms beyond the scope of structural transformation.</p>
<p>Third, our study shows that LRM suppresses GTI, further weakening UCEE. Several scholars argue that the distorted allocation of land factors restricts the concentration and input of green innovation, thereby indirectly reducing carbon efficiency (<xref ref-type="bibr" rid="B15">Han and Huang, 2022</xref>). <xref ref-type="bibr" rid="B15">Han and Huang (2022)</xref> provided empirical evidence that land misallocation significantly inhibits green innovation activities and weakens economic agglomeration, leading to increased emissions. <xref ref-type="bibr" rid="B39">Xu et al. (2025)</xref> find that land misallocation has a direct and significant negative impact on urban green innovation capacity, operating through structural, scale, and spatial agglomeration. Similarly, <xref ref-type="bibr" rid="B3">Chen and Yuan (2025)</xref> showed that misallocated land leads to insufficient investment in green R&#x26;D and delays in technological advancement, thus reducing the driving force for emission reduction. However, other studies offer different perspectives. <xref ref-type="bibr" rid="B45">Zhou et al. (2023)</xref>, through mechanism analysis, empirically identify economic agglomeration, industrial structure, and urbanization as joint mediators of the impact of land misallocation on energy efficiency, without highlighting green innovation as a channel. This may be due to the differences in the measurements of energy efficiency versus carbon efficiency. Overall, the majority of the literature supports the pathway of &#x201c;land misallocation &#x2192; inhibited green innovation &#x2192; reduced carbon efficiency,&#x201d; though a few studies show divergent conclusions due to differences in research focus or the selection of control variables. This highlights the importance of considering multiple research perspectives and carefully selecting appropriate covariates.</p>
<p>Fourth, regarding heterogeneity, existing studies generally agree that land resource misallocation affects urban carbon emission efficiency, and also emphasize its heterogeneous effects based on city location (<xref ref-type="bibr" rid="B2">An, 2024</xref>), population size (<xref ref-type="bibr" rid="B14">Gao et al., 2023</xref>), and resource endowment (<xref ref-type="bibr" rid="B44">Zhou et al., 2022</xref>), which are consistent with those of the heterogeneity dimensions examined here. Our findings show that the inhibitory effect of land misallocation on carbon efficiency is significant only in the central and western regions (<xref ref-type="bibr" rid="B2">An, 2024</xref>), small and medium-sized cities (<xref ref-type="bibr" rid="B14">Gao et al., 2023</xref>), and non-resource-based cities (<xref ref-type="bibr" rid="B44">Zhou et al., 2022</xref>), aligning with that of most scholarly conclusions. However, <xref ref-type="bibr" rid="B44">Zhou et al. (2022)</xref> report that the effect is also significant in resource-based cities, which they attribute to the lagged effects of land policies&#x2014;i.e., the land misallocation in the earlier period may affect current carbon efficiency. This does not contradict our findings as the lag effect may explain short-term inconsistencies in resource-based cities, whereas our analysis focused on the average effect over time.</p>
</sec>
<sec id="s5-2">
<title>5.2 Research contributions</title>
<p>This study contributes to the literature in both theoretical and methodological dimensions.</p>
<p>From a theoretical perspective, first, it supplements the institutional explanation of land-resource allocation from an environmental economics perspective. It explicitly highlights that land misallocation is not merely an issue of allocation efficiency but also one with far-reaching environmental consequences. Second, it constructs a dual-mechanism mediation framework of &#x201c;Land Resource Misallocation&#x2013;Industrial Structure Upgrading/Green Technological Innovation&#x2013;Urban Carbon Emission Efficiency,&#x201d; addressing the limitations of earlier studies regarding the identification of transmission pathways (<xref ref-type="bibr" rid="B12">Gao and He, 2024</xref>; <xref ref-type="bibr" rid="B6">Cheng Y. et al., 2025</xref>).</p>
<p>From a methodological perspective, by introducing the interaction between the average terrain slope and the annual economic growth target of a city as an instrumental variable, we enhance the credibility of causal inferences regarding LRM and enrich methodological applications in environmental economics to tackle endogeneity problems.</p>
</sec>
<sec id="s5-3">
<title>5.3 Policy recommendations</title>
<p>From a policy perspective, our findings offer the following recommendations for promoting green development and optimizing land systems in China.<list list-type="simple">
<list-item>
<p>(1) Accelerate market-oriented reforms in land resource allocation, and break away from the administratively driven logic of land supply&#x2014;especially by avoiding the preferential allocation of low-cost land to high-emission industries, to curb misallocation at its source.</p>
</list-item>
<list-item>
<p>(2) Strengthen land policy support for green enterprises, high-tech industries, and modern service sectors. The structure of land supply should be optimized to guide the upgrading of urban industrial layouts and facilitate low-carbon transformation.</p>
</list-item>
<list-item>
<p>(3) Use land allocation reform as a strategic entry point to promote a coordinated system of &#x201c;green technology&#x2013;institutional innovation&#x2013;carbon governance&#x201d;. Leverage the synergy between industrial and technological policies to enhance innovation chains and strengthen emission reduction pathways.</p>
</list-item>
<list-item>
<p>(4) Implement differentiated land and industrial policies across various types of cities, with particular attention paid to non-resource-based and small-to medium-sized cities where land misallocation has constrained green development. The adaptability and inclusiveness of land allocation systems should be improved to support low-carbon governance.</p>
</list-item>
</list>
</p>
</sec>
<sec id="s5-4">
<title>5.4 Research limitations and future research directions</title>
<p>This study has some limitations.</p>
<p>First, although a comprehensive panel dataset was constructed and a two-way fixed-effects model was employed to explore the linear impact of LRM on UCEE, the spatial dependence and regional spillover effects of land misallocation were not fully addressed. Future research could incorporate spatial econometric models or multiscale geographically weighted regression (MGWR) models and update the dataset with post-2023 observations to further investigate the spatial transmission mechanisms and nonlinear characteristics of the influence of land misallocation on carbon efficiency across cities.</p>
<p>Second, in terms of mechanism analysis, future studies may consider introducing structural equation modeling (SEM) to enhance causal inference in mediating effect analysis. Furthermore, as current measurement indicators rely largely on static city-level data, future work could integrate remote sensing imagery, enterprise-level carbon emission records, and natural language processing (NLP) techniques to depict land-use behavior, green innovation activity, and policy enforcement intensity more dynamically and precisely at the micro level.</p>
<p>Third, given the diverse development stages and functional roles of Chinese cities, subsequent research could incorporate heterogeneity in urbanization levels and examine the distinct characteristics of tourism-oriented cities. Such efforts would provide more scientific and theoretical support and empirical evidence for achieving coordinated regional emission reduction and the modernization of land resource governance capacity.</p>
</sec>
</sec>
<sec sec-type="conclusion" id="s6">
<title>6 Conclusion</title>
<p>Conclusively, we utilized panel data from 274 Chinese cities spanning the period from 2010 to 2022. A super-efficiency SBM model incorporating undesirable outputs was employed to measure UCEE, and empirical tests were conducted using panel regression models with both city and time fixed effects. The results confirmed that LRM significantly undermines the efficiency of urban carbon emissions. Distorted land-use patterns and entrenchment of carbon-intensive industrial structures hinder cities from decoupling carbon emissions from economic growth. These findings emphasize the critical urgency of advancing land market reforms and implementing integrated spatial planning to enhance UCEE and steer cities toward a green and low-carbon transformation. Furthermore, it is essential to further refine land governance strategies tailored to different types of cities and evaluate their long-term impacts on carbon emissions efficiency.</p>
</sec>
</body>
<back>
<sec sec-type="data-availability" id="s7">
<title>Data availability statement</title>
<p>The original contributions presented in the study are included in the article/supplementary material, further inquiries can be directed to the corresponding author.</p>
</sec>
<sec sec-type="author-contributions" id="s8">
<title>Author contributions</title>
<p>ZW: Conceptualization, Data curation, Formal Analysis, Methodology, Software, Writing &#x2013; original draft, Writing &#x2013; review and editing. W-SL: Project administration, Resources, Supervision, Writing &#x2013; original draft, Writing &#x2013; review and editing. SW: Investigation, Validation, Visualization, Writing &#x2013; review and editing.</p>
</sec>
<sec sec-type="funding-information" id="s9">
<title>Funding</title>
<p>The author(s) declare that financial support was received for the research and/or publication of this article. This research was funded by the Guangdong Planning Office of Philosophy and Social Science Foundation (Grant number: GD24XYJ32).</p>
</sec>
<sec sec-type="COI-statement" id="s10">
<title>Conflict of interest</title>
<p>The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.</p>
</sec>
<sec sec-type="ai-statement" id="s11">
<title>Generative AI statement</title>
<p>The author(s) declare that no Generative AI was used in the creation of this manuscript.</p>
</sec>
<sec sec-type="disclaimer" id="s12">
<title>Publisher&#x2019;s note</title>
<p>All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.</p>
</sec>
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