How Can Industrial Parks Achieve Carbon Neutrality? Literature Review and Research Prospect Based on the CiteSpace Knowledge Map
Abstract
:1. Introduction
2. Methodology
2.1. Methods
2.2. Data Sources
2.3. Framework of This Study
3. Results
3.1. Descriptive Statistical Analysis
3.2. Network Analysis
3.2.1. National Cooperation Network
3.2.2. Institutional Cooperation Network
3.2.3. Co-Authorship Network
3.3. Research Hotspots
3.3.1. Keyword Co-Occurrence Network Analysis
3.3.2. Keyword Clustering
- Research on energy management in industrial parks.
- 2.
- Research on industrial symbiosis (IS) in industrial parks.
- 3.
- Research on economics and development of industrial parks.
- 4.
- Research on evaluations of carbon emissions in industrial parks.
3.4. Research Topic Evolution Analysis
3.4.1. Timeline View of Co-Citation Analysis
- Phase I (2007–2011): Initial exploration of energy management and carbon neutralization concepts in industrial parks. Research on carbon emissions reduction in industrial parks was only in its infancy during this period, with only three articles having high centrality and the rest with relatively low citation frequency. The issues of global climate change and environmental pollution had not received sufficient attention during this period, and theories and ideas on environmental performance at the industrial park level had yet to be established. The main findings of this period were all produced in 2011. Tom Maes et al. [50] explored the literature on industrial symbiosis and eco-industrial parks, starting with the Flanders’ poor control of greenhouse gas emissions from industrial parks. They argued that energy management in industrial parks can be integrated into the overall development process as well as the direction of the park. Maximizing efficiency is an extremely promising local optimization problem and enhancing the flexibility and stability of energy management in industrial parks requires further research. Mirko Z. Stijepovic et al. [51] presented a systematic approach to targeting the potential of waste heat recovery and designed the best reuse scenario at a plant in an industrial area. The method first considered the distances between the individual plants and determined the available waste heat’s mass and the feasibility of reuse. An objective optimization problem was solved to establish the maximum possible waste heat recovery for the industrial area. Then, a design optimization problem was solved for a concrete waste heat recovery scheme considering economic objectives. C. Block et al. [52] made a park-wide inventory for 2007 of the CO2 emissions due to energy consumption (electricity and fossil fuel) and waste incineration, as well as an inventory of the existing renewable electricity and heat generation of the Herdersbrug IP. Flanders’ carbon emissions were less than the carbon dioxide emissions avoided from renewable energy generation and therefore met the local government’s criteria for carbon neutralization. However, they did not consider the carbon dioxide emissions from fossil fuels used for heating. Overall, the articles in this period presented the concept of carbon neutralization in industrial estates and made initial explorations of carbon reduction from the perspective of energy management and waste heat recovery.
- Phase II (2012–2016), a period of theoretical and methodological development of carbon emissions reduction in industrial parks. This period was a boom period for carbon reduction research in industrial parks. Many studies began to employ models to quantify the carbon footprint and greenhouse gas emission potential within industrial parks and to reach certain conclusions. In addition, several gaps in the research were identified, such as spatial planning of industrial parks, the integration of emission reduction projects within parks, and social and business perspectives. Huijuan Dong et al. [41] argued that industrial parks were the main areas of greenhouse gas emissions. Therefore, it was essential to quantify the carbon footprint of industrial parks to suggest appropriate policies for reducing emissions. They applied a hybrid LCA model and obtained specific carbon footprint data for industrial parks, concluding that the chemical industry and specialized machinery manufacturing sector were the two sectors with the most prominent life-cycle carbon footprint. Marianne Boix et al. [16] retrieved articles in the form of reviews on “industrial symbiosis” (or “eco-industrial park”, or “inter plant integration”) and “optimization”, then detailed several EIP network types. They suggested that the problems with previous research were the need for multi-objective optimization studies, more flexibility in considering EIPs from a business perspective, and the need to explore the objective social factor. Yang Guo et al. [53] developed a vintage stock model to quantify the GHG mitigation potential and cost-effectiveness of Chinese eco-industrial parks by targeting energy infrastructure with five key measures. The results showed that two actions (conversion of coal-fired boilers to natural gas-fired boilers and replacement of coal-fired units with natural gas-fire-combined cycle units) had significant potential for GHG reductions (42–46%) compared to the baseline scenario. In most cases, significant economic benefits could also be achieved through GHG emission reductions. Industrial parks in Korea are also one of the country’s primary sources of CO2 emissions. To assess the performance of commercial eco-industrial park projects in mitigating climate change, Yong Un Ban et al. [54] analyzed the direct CO2 emission reductions from 41 eco-industrial park projects implemented in Korea between 2005 and 2012. The results showed that after the start of the eco-industrial park projects, CO2 emissions from the industrial sector in Korea decreased by 0.48% in 2004. Most of the projects were effectively implemented through networks that shared and exchanged energy and resources. Spatial development planning is therefore needed to establish relationships between nodes in the network effectively. Their study also found that the performance and limitations of eco-industrial park projects vary depending on the amount of fuel and waste reduction, the byproducts and waste recovered, and the location of the eco-industrial park. Therefore, eco-industrial park projects should integrate with other projects that reduce CO2 emissions from other sources, as eco-industrial park projects alone do not reduce CO2 emissions. Furthermore, local governments should cooperate in implementing city and regional projects to achieve environmentally and economically sustainable development. Catharine A. Kastner et al. [55] reviewed the quantitative tools and methods developed to identify and cultivate symbiotic industrial exchanges in existing industrial parks to minimize overall energy and material consumption. They highlighted the introduction of new topics such as infrastructure transformation, network analysis, company motivation, and confidentiality.
- Phase III (2017–2020) In-depth exploration of the industrial symbiosis approach and the initial proposal of a zero-carbon industrial park. The economic analysis of carbon reduction in industrial parks is gradually increasing, and energy management methods are becoming more abundant. Research on zero-carbon parks began to emerge at this stage. In addition, the study of industrial symbiosis extends from within industrial parks to the industrial symbiosis between parks and cities. Yang Guo et al. [48,49], the critical authors of this phase, were described in the preceding section, and their summary and assessment of carbon emissions in China’s national industrial parks, as well as that of the development of energy infrastructure within China’s national industrial parks, is of great relevance to future research. Jing-Chun Feng et al. [56] conducted a scenario analysis of the Traditional Chinese Medicine Industrial Park in Zhongshan City, Guangdong Province, China, to achieve zero carbon emissions. The results showed that all three scenarios could achieve zero carbon emissions. The economic assessment found that purchasing carbon offsets is the least cost-effective under current market conditions. Sensitivity analysis showed that the carbon price and the rate of reduction in the cost of solar energy significantly impacted the cost-effectiveness of carbon emission reductions. At the same time, with the current 90% reduction in the price of solar energy, the large-scale application of renewable energy, which generates more carbon offsets, could reap more economic and carbon reduction benefits. Xu Zhu et al. [57] proposed a regional integrated energy systems (RIES) energy management strategy based on energy stepped utilization to minimize the daily cost further and fully use the power. Finally, the simulation analysis showed that their proposed RIES energy management approach allowed for more flexible scheduling of gas turbine combinations and equipment output and could provide a more economical scheduling solution. Zhe Liu et al. [58] argued that there is currently more research required on achieving comprehensive development of industrial symbiosis with the aim of greenhouse gas emission reduction. They analyzed the challenges of lack of indicators, survey methods, and regional differences, and they detailed the opportunities for mitigating greenhouse gas emissions through the comprehensive development of industrial symbiosis. M.A. Butturi et al. [32] highlighted four main ways of achieving energy strategies and demonstrated possible solutions to increase renewable energy uptake at an industrial level. In addition, research gaps were identified, revealing that energy symbiosis networks between industrial and urban areas that integrate renewable energy systems remained to be adequately studied.
3.4.2. Burst Detection
4. Challenges and Prospects for the Zero Carbon Industrial Parks
- 1
- The carbon neutralization objective for IPs has not been established. There have been many studies focusing on how to reduce carbon emissions in industrial parks through measures such as integrated management solutions, but few case studies have started with the goal of achieving carbon neutralization in industrial parks as a construction and operational objective [84]. Apart from that, research on industrial parks has remained focused on planning EIPs, calculating and monitoring carbon emissions from established EIP resources [85], consolidating and repositioning energy infrastructure, and industrial symbiosis projects [86]. The transition from EIP to zero-carbon industrial park (ZCIP) or the methods and practices of how to build a ZCIP have received scant mention. It is vital to clarify the goal of carbon reduction in industrial parks. A ZCIP must have carbon neutralization as its primary vision [87]. Therefore, its construction goal and operational management throughout its life cycle can be coordinated to achieve zero carbon emissions by working together, significantly increasing the efficiency of carbon emissions reduction [88]. Within such a macro goal, energy management, production logistics, economic efficiency, and human-centered concepts need to be integrated into the system framework of a zero-carbon park [89]. Carbon neutralization is the essential feature that distinguishes a ZCIP from a traditional industrial park. It is also the principal basis for developing strategies in a park’s construction process. The ZCIP system’s design should be based on this vision to build a management and operation system and a human-centered intelligent service platform, and carbon emission and absorption are one of the evaluation criteria of the ZCIP system.
- 2
- Absence of integrated exploration of carbon absorption and emissions. The current study focused on measuring the sources of carbon emissions in industrial parks, with direct and indirect emissions. Electricity consumption and renewable energy offsets were all taken into account [90]. There are some challenges in measuring the carbon emissions side of the industry, such as the comprehensive inclusion of Scope 1, 2, and 3, for which data are not readily available. Whether upstream and downstream carbon emissions need to be included in the carbon accounting criteria needs further exploration [91]. Carbon emissions from transport and renewable energy-powered street lighting in parks also need to be discussed. Beyond this, little research has been conducted on carbon sequestration [92]. The achievement of carbon neutralization relies on carbon sequestration measures such as bioenergy with carbon capture and storage (BECCS) and carbon capture, utilization, and sequestration (CCUS), in addition to renewable energy offsets [93]. The critical role of vegetation planting for carbon sequestration in industrial estates has rarely been mentioned, but carbon sequestration is an essential part of achieving carbon neutrality. There are two main paths to achieving carbon neutrality in a ZCIP: controlling carbon emissions and increasing carbon sequestration, establishing a carbon trading market, and strengthening intelligent control [94], primarily utilizing renewable energy sources such as solar, wind, biomass fuels, nuclear, and other primary energy sources. Meanwhile, the development and large-scale application of hydrogen energy storage are being strengthened [95]. From an energy use point of view, energy saving and emissions reduction are mainly from the energy, production, transportation, building, and living aspects of parks [96]. We must optimize industrial production patterns, develop low-carbon and carbon-negative technologies, and promote zero-carbon transport and living. In addition, an integrated energy system must be established, combined with an intelligent grid, to form an all-in-one energy plan with multiple energy sources complementing each other. Furthermore, at the carbon sequestration end, the development of ecological carbon sinks, such as vegetation planting and pocket parks, as well as industrial carbon capture and sequestration capture technologies must be implemented. In addition, establishing a carbon trading market to optimize the allocation of carbon emission rights can further promote the upgrading of enterprises.
- 3
- Lack of a systematic review of social and environmental factor integration. The zero-carbon upgrade of many traditional parks is a significant aspect in constructing zero-carbon parks. Currently, the infrastructure of traditional parks, such as power systems, network systems, service systems, and data centers, is aging and lacks connectivity. The embedding of intelligent technologies urgently requires infrastructural upgrade and transformation, with a high demand for innovative design of physical systems and information systems [97]. Traditional Park design is based on fragmented and functional construction, with each sector relatively isolated and difficult to interoperate information with. The lack of system design thinking can lead to difficulties in obtaining sustainable benefits and smooth iterative system updates [98], and there is particular neglect of social and ecological factors surrounding the park, thus lacking the resilience to develop in the ever-changing economic and social environments. In addition, the concepts of carbon pricing, carbon trading markets, and carbon taxes are rarely mentioned [99]. An industrial park is a socioeconomic and ecological system formed by the interaction of multiple stakeholders, including the park, government, enterprises, and the public [100]. For industrial parks, their environmental management demands the participation of multiple parties. When considering environmental issues in industrial parks, researchers often base their research on the park, the government, or the enterprises, lacking the perspective of multiple subjects [101]. Public facilities and services, social consumption levels, tax policies, openness, regional industrial structure, and technological innovation capacity all have a significant impact on the output efficiency of industrial parks [93]. In the social dimension, the direct guiding role of national policies and the combined role of strategies with other dimensions need to be taken into account [102]. The design of a ZCIP system needs to consider the interests and needs of decisionmakers, managers, technical staff [103], resident enterprises, and residential users, and establish a decision model for the zero carbon park system [104]. Rationalize the weighting of different stakeholders’ decisions under the carbon neutralization target to motivate people to respond to the park’s policies and become a potent force for improving a park’s operational efficiency in the social dimension [105]. Ecologically, it is appropriate to exploit the strengths of local natural resources to promote the carbon neutralization level of IPs [106]. On the one hand, making good use of local natural resources such as wind, solar, and hydropower can solve most of the park’s energy supply needs, while other energy needs can be supplemented by utilizing intelligent grids or the presence of power generation, can achieve zero-carbon energy in IPs [107]. On the other hand, ecological carbon sinks can create small eco-climatic zones in IPs, designed and distributed in accordance with the carbon emissions of the buildings, creating gardening in the park and attracting households to participate in the maintenance and operation of the ecological carbon sink facilities.
- 4
- Insufficient uptake of emerging technologies and theories. The digital transformation of society has permeated all aspects of industrial production. Industrial parks integrate various resources inside and outside the parks, but little research has yet addressed the flexible use of emerging technologies in industrial parks. The application of emerging technologies such as 5G, IoT, digital twin, artificial intelligence, and cloud computing has not been studied in depth in the current articles on carbon reduction in industrial estates [108]. The traditional IP mainly relies on human resources management, which wastes many human resources. Handling these problems is a passive response, failing to provide intelligent and proactive services and lacking user experience design [109]. The various monitoring and management systems in parks fail to integrate and control the data collected and present it visually to park personnel [110], resulting in low operational efficiency. Data from various departments within the traditional IP lack effective sharing and interoperability [111]. A park’s real-time monitoring data needs to be processed and optimized by applying intelligent algorithms for data mining and analysis and filtering out critical information. To better achieve the goal of carbon neutrality, a park’s smart governance must be an innovative transformation of the entire park system for real-time carbon monitoring and management [112]. Digital empowerment is the key to building a zero-carbon park. While technology development for renewable energy and smart power systems plays a key role [113], the full integration of digitalization can drive the growth of zero-carbon park technology even more strongly. Firstly, zero carbon parks can be digitally managed to improve operational efficiency. Secondly, digitalization can also drive technological innovation in both directions, promoting the development, promotion, and commercialization of zero-carbon, carbon-reducing, and carbon-negative technologies. Thirdly, digitization helps to build a carbon monitoring system to achieve a real-time panoramic picture of a park’s carbon emissions [114]. In addition, digitalization is also a strong support for the operation of the carbon accounting system, which involves social entities from central to local, government to enterprise, and other cross-sectoral levels. The source of data, calculation methods, calculation scope, and other complex factors require digital monitoring to ensure accuracy.
5. A Systematic Design Framework to Construct Zero-Carbon Industrial Parks
- 1
- One objective: carbon neutralization
- 2
- Two sides: carbon emission and carbon absorption
- 3
- Three dimensions: social, technical, and ecological dimensions
- 4
- The carbon-neutral smart services platform
6. Conclusions
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Acknowledgments
Conflicts of Interest
References
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Data Source | Input Variables |
---|---|
Web of Science | (TS = (“industrial park *” OR “eco-industrial park *”)) AND TS = (“carbon emission *” OR “carbon dioxide emission *” OR “greenhouse gas * emission *” OR “GHG emission *” OR “greenhouse gas * mitigation” OR “CO2 emission *” OR “carbon discharge” OR “carbon footprint *” OR “carbon absor *” OR “carbon fixation” OR “carbon sink” OR “carbon neutral *” OR “zero carbon”) |
Limiters | “Article or Review Article”, “English” |
Number | Journal | TP | Percentage | IF |
---|---|---|---|---|
1 | Journal of Cleaner Production | 23 | 20.18% | 11.072 |
2 | Energy | 8 | 7.02% | 8.857 |
3 | Applied Energy | 7 | 6.14% | 11.446 |
4 | Energy Policy | 6 | 5.26% | 7.576 |
5 | Resources, Conservation and Recycling | 6 | 5.26% | 13.716 |
6 | Journal of Industrial Ecology | 5 | 4.39% | 7.202 |
7 | Environmental Science & Technology | 4 | 3.51% | 11.357 |
8 | Renewable & Sustainable Energy Reviews | 4 | 3.51% | 16.799 |
9 | International Journal of Energy Research | 3 | 2.63% | 4.672 |
10 | Sustainability | 3 | 2.63% | 3.889 |
Number | Frequency | Centrality | Keyword |
---|---|---|---|
1 | 20 | 0.29 | China |
2 | 16 | 0.39 | energy |
3 | 12 | 0.3 | system |
4 | 10 | 0.08 | management |
5 | 9 | 0.07 | design |
6 | 9 | 0.12 | city |
7 | 9 | 0.03 | life cycle assessment |
8 | 9 | 0.21 | symbiosis |
9 | 8 | 0.03 | performance |
10 | 8 | 0.03 | industrial symbiosis |
11 | 7 | 0.07 | consumption |
12 | 6 | 0.09 | model |
13 | 6 | 0.01 | mitigation |
14 | 6 | 0.05 | ecology |
15 | 5 | 0.18 | energy efficiency |
16 | 5 | 0.01 | industrial ecology |
17 | 5 | 0.02 | efficiency |
18 | 5 | 0.06 | climate change |
19 | 4 | 0.04 | integrated energy system |
20 | 4 | 0.01 | optimal design |
Cluster ID | Cluster Label | Keyword |
---|---|---|
0 | low carbon | low carbon; climate change; hybrid lca; structural decomposition |
1 | industrial ecology | industrial ecology; eco-industrial development; environmental co-benefits |
2 | strategy | strategy; small and medium enterprises; carbon metabolism; embodied carbon emissions; des/cchp |
3 | combined heat and power | combined heat and power; CO2 footprint; uncertainty analysis; eco-efficiency; energy efficiency |
4 | industrial layout adjustment | industrial layout adjustment; industrial land reallocation; industrial land development cost |
5 | system integration | system integration; bioeconomy; urban ecology; bioenergy; cchp; industrial energy symbiosis |
6 | carbon neutral | carbon neutral; multi-level modelling and optimization; carbon negative; carbon capture |
7 | techno-economic analysis | techno-economic analysis; pv; wind; grid-connected systems; industrial symbiosis |
8 | optimization | optimization; eco-industrial development strategies; carbon capture and storage (ccs); system; ghg management |
9 | energy infrastructure | energy infrastructure; infrastructure stock; industrial park infrastructure; economic assessment |
10 | renewable energy | renewable energy; energy consumption; solar pv; wind power; zero carbon emission |
Centrality | First Author | Year | Article | Journal | Cluster |
---|---|---|---|---|---|
0.16 | Guo Y | 2018 | The Role of Industrial Parks in Mitigating Greenhouse Gas Emissions from China | ENVIRON SCI TECHNOL | 6 |
0.04 | Maes T | 2011 | Energy Management on Industrial Parks in Flanders | RENEW SUST ENERG REV | 4 |
0.09 | Dong HJ | 2013 | Carbon Footprint Evaluation at Industrial Park Level: A Hybrid Life Cycle Assessment Approach | ENERG POLICY | 2 |
0.05 | Guo Y | 2018 | Exploring Greenhouse Gas-Mitigation Strategies in Chinese Eco-Industrial Parks by Targeting Energy Infrastructure Stocks | J IND ECOL | 2 |
0.08 | Boix M | 2015 | Investigation of Ions Hydration Using Molecular Modeling | J CLEAN PROD | 1 |
0.05 | Dong HJ | 2014 | Achieving Carbon Emission Reduction Through Industrial & Urban Symbiosis: A Case of Kawasaki | ENERGY | 1 |
0.01 | Guo Y | 2016 | Greenhouse Gas Mitigation in Chinese Eco-Industrial Parks by Targeting Energy Infrastructure: A Vintage Stock Model | ENVIRON SCI TECHNOL | 14 |
0.09 | Feng JC | 2018 | Case Study of an Industrial Park toward Zero Carbon Emission | APPL ENERG | 9 |
0.09 | Butturi MA | 2019 | Renewable Energy in Eco-Industrial Parks and Urban-Industrial Symbiosis: A Literature Review and a Conceptual Synthesis | APPL ENERG | 3 |
0.01 | Liu W | 2014 | Greenhouse Gas Emissions in China’s Eco-Industrial Parks: A Case Study of the Beijing Economic Technological Development Area | J CLEAN PROD | 2 |
Keywords | Strength | Begin | End | 2001–2022 |
---|---|---|---|---|
emission reduction | 1.89 | 2013 | 2013 | ▂▂▂▂▂▂▂▂▂▂▂▂▃▂▂▂▂▂▂▂▂▂ |
carbon dioxide | 2.64 | 2014 | 2017 | ▂▂▂▂▂▂▂▂▂▂▂▂▂▃▃▃▃▂▂▂▂▂ |
sustainability | 2.39 | 2015 | 2020 | ▂▂▂▂▂▂▂▂▂▂▂▂▂▂▃▃▃▃▃▃▂▂ |
system | 3.16 | 2016 | 2017 | ▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▃▃▂▂▂▂▂ |
design | 2.93 | 2016 | 2017 | ▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▃▃▂▂▂▂▂ |
ghg emission | 1.87 | 2016 | 2018 | ▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▃▃▃▂▂▂▂ |
sensitivity analysis | 2.33 | 2017 | 2020 | ▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▃▃▃▃▂▂ |
life cycle assessment | 2.1 | 2017 | 2020 | ▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▃▃▃▃▂▂ |
performance | 2.03 | 2017 | 2020 | ▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▃▃▃▃▂▂ |
mitigation | 2.42 | 2018 | 2019 | ▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▃▃▂▂▂ |
management | 2.33 | 2018 | 2022 | ▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▃▃▃▃▃ |
energy efficiency | 2.28 | 2018 | 2019 | ▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▃▃▂▂▂ |
optimal design | 2.98 | 2019 | 2020 | ▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▃▃▂▂ |
circular economy | 2.63 | 2019 | 2022 | ▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▃▃▃▃ |
renewable energy | 2.25 | 2019 | 2022 | ▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▃▃▃▃ |
model | 1.87 | 2019 | 2022 | ▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▃▃▃▃ |
energy | 2.14 | 2020 | 2020 | ▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▃▂▂ |
economic development | 2.48 | 2021 | 2022 | ▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▃▃ |
integrated energy system | 2.31 | 2021 | 2022 | ▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▃▃ |
carbon peak | 1.98 | 2021 | 2022 | ▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▂▃▃ |
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Yan, X.; Wang, L.; Fang, M.; Hu, J. How Can Industrial Parks Achieve Carbon Neutrality? Literature Review and Research Prospect Based on the CiteSpace Knowledge Map. Sustainability 2023, 15, 372. https://doi.org/10.3390/su15010372
Yan X, Wang L, Fang M, Hu J. How Can Industrial Parks Achieve Carbon Neutrality? Literature Review and Research Prospect Based on the CiteSpace Knowledge Map. Sustainability. 2023; 15(1):372. https://doi.org/10.3390/su15010372
Chicago/Turabian StyleYan, Xingyun, Lingyu Wang, Mingzhu Fang, and Jie Hu. 2023. "How Can Industrial Parks Achieve Carbon Neutrality? Literature Review and Research Prospect Based on the CiteSpace Knowledge Map" Sustainability 15, no. 1: 372. https://doi.org/10.3390/su15010372
APA StyleYan, X., Wang, L., Fang, M., & Hu, J. (2023). How Can Industrial Parks Achieve Carbon Neutrality? Literature Review and Research Prospect Based on the CiteSpace Knowledge Map. Sustainability, 15(1), 372. https://doi.org/10.3390/su15010372