Business Cycles and Pollution Emission Intensity —Mechanism Analysis and Policy Response
LI Jianjun, FENG Kexin, DENG Guichuan, PENG Yuchao
School of Finance, Central University of Finance and Economics; International School of Business and Finance, Sun Yat-Sen University; Advanced Institute of Finance, Sun Yat-Sen University
Summary:
In the face of environmental issues and limited resources, how to coordinate the relationship between development and emission reduction, while alleviating business cycle fluctuations and encouraging enterprises to take the initiative in emission reduction, is of great significance for achieving a “win-win” situation between the economy and environment. To answer this question, it is necessary to first clarify the relationship between business cycles and corporate emission reduction behavior and environmental performance. Thus, this paper focuses on pollution emission intensity, aiming to explore the dynamic processes, internal mechanisms, and policy responses of different corporate reduction behaviors in different business cycles in China, to facilitate green and high-quality enterprise development. Based on the pollution data of Chinese industrial enterprises from 1998 to 2013, we observe the countercyclical characteristics of pollution emission intensity. To explain this finding, this paper constructs a two-sector DSGE model with environmental constraints to analyze the relationship between business cycles and pollution emission intensity. In the model, both high-emission and low-emission projects are established. Low-emission projects introduce cleaner production equipment into the production function, so their pollution emission intensity is lower than in high-emission projects, resulting in lower environmental negative externalities. The model also includes enterprise heterogeneity with respect to management ability for cleaner production equipment, such that enterprises' choice of optimal project depends on their own ability to manage low-emission projects. Specifically, enterprises with high management skills are more likely to choose low-emission projects. To describe the externality of pollution emissions, this paper introduces pollutant-adjusted labor into the household utility function. This setting helps to elucidate the general equilibrium effects of pollution emissions on the macro-economy. Subsequently, through impulse response functions, this paper analyzes the key mechanism underlying the countercyclical characteristics of pollution emission intensity from both the enterprise and household sectors as well as policy response methods. The results show that when the economy is in a downturn, the return on investment falls more sharply for enterprises that invest in low-emission projects than for those that invest in high-emission projects, leading to a decrease in the number of enterprises investing in low-emission projects and a rise in pollution emission intensity. At the same time, as pollution emission intensity rises, it increases the negative externality of pollution emissions on labor, which lowers enterprise profits through decreased labor supply and increased labor costs, further hindering sustainable economic development. Policy analysis shows that when the economy is in a downturn, policies that target pollution emission intensity, such as emissions taxes, price subsidies for cleaner equipment, and credit restrictions on polluting enterprises, can effectively curb the rise in pollution emission intensity. Specifically, emissions tax policies and subsidy policies have positive effects on the environment through structural effects in the enterprise sector, helping to promote corporate low-emission transformation. The marginal contribution of this paper mainly lies in discovering a negative relationship between US manufacturing output and industry-specific pollution emission intensity documented in the existing literature. However, the relationship between China's business cycle and pollution emission intensity remains unknown. Based on empirical analysis, we find that pollution emission intensity is countercyclical. Moreover, we construct a model to attempt to explain this feature, providing preliminary empirical evidence and theoretical support for the relationship between business cycles and pollution emissions. This paper focuses on analyzing the short-term impacts of taxation, subsidies, and other environmental policies. Future research directions include studying long-term policy effects based on growth models from cost-benefit perspectives.
[1]陈登科,2020,《贸易壁垒下降与环境污染改善——来自中国企业污染数据的新证据》,《经济研究》第12期,第98~114页。 [2]陈诗一、张建鹏和刘朝良,2021,《环境规制、融资约束与企业污染减排——来自排污费标准调整的证据》,《金融研究》第9期,第51~71页。 [3]郭晔和房芳,2021,《新型货币政策担保品框架的绿色效应》,《金融研究》第1期,第91~110页。 [4]解学梅和韩宇航,2022,《本土制造业企业如何在绿色创新中实现“华丽转型”?——基于注意力基础观的多案例研究》,《管理世界》第3期,第76~106页。 [5]李永友和沈坤荣,2008,《我国污染控制政策的减排效果——基于省际工业污染数据的实证分析》,《管理世界》第7期,第7~17页。 [6]罗知和齐博成,2021,《环境规制的产业转移升级效应与银行协同发展效应——来自长江流域水污染治理的证据》,《经济研究》第2期,第174~189页。 [7]马理、张人中、马威和牛慕鸿,2023,《能源结构有序调整与绿色信贷政策调控》,《金融研究》第1期,第94~112页。 [8]马勇和陈雨露,2014,《经济开放度与货币政策有效性:微观基础与实证分析》,《经济研究》第3期,第35~46页。 [9]潘冬阳、陈川祺和Michael Grubb,2021,《金融政策与经济低碳转型——基于增长视角的研究》,《金融研究》第12期,第1~19页。 [10]彭俞超和方意,2016,《结构性货币政策、产业结构升级与经济稳定》,《经济研究》第7期,第29~42页。 [11]彭俞超和何山,2020,《资管新规、影子银行与经济高质量发展》,《世界经济》第1期,第47~69页。 [12]宋科、徐蕾、李振和王芳,2022,《ESG投资能够促进银行创造流动性吗?——兼论经济政策不确定性的调节效应》,《金融研究》第2期,第61~79页。 [13]王馨和王营,2021,《环境信息公开的绿色创新效应研究——基于〈环境空气质量标准〉的准自然实验》,《金融研究》第10期,第134~152页。 [14]王遥、潘冬阳、彭俞超和梁希,2019,《基于DSGE模型的绿色信贷激励政策研究》,《金融研究》第11期,第1~18页。 [15]张军,2002,《资本形成、工业化与经济增长:中国的转轨特征》,《经济研究》第6期,第3~13页。 [16]庄子罐、崔小勇和赵晓军,2016,《不确定性、宏观经济波动与中国货币政策规则选择——基于贝叶斯DSGE模型的数量分析》,《管理世界》第11期,第20~31页。 [17]Acemoglu, D., P. Aghion, L. Bursztyn and D. Hemous, 2012, “The Environment and Directed Technical Change”, American Economic Review, 102(1), pp.131~166. [18]Annicchiarico, B. and F. Di Dio, 2015, “Environmental Policy and Macroeconomic Dynamics in a New Keynesian Model”, Journal of Environmental Economics and Management, 69, pp.1~21. [19]Bernanke, B.S., M. Gertler and S. Gilchrist, 1999, “The Financial Accelerator in a Quantitative Business Cycle Framework”, Handbook of Macroeconomics, 1, pp.1341~1393. [20]Boissay, F., F. Collard and F. Smets, 2016, “Booms and Banking Crises”, Journal of Political Economy, 124(2), pp.489~538. [21]Brandt, L., J. Van Biesebroeck and Y. Zhang, 2012, “Creative Accounting or Creative Destruction? Firm-level Productivity Growth in Chinese Manufacturing”, Journal of Development Economics, 97(2), pp.339~351. [22]Calvo, G.A., 1983, “Staggered Prices in a Utility-maximizing Framework”, Journal of Monetary Economics, 12(3), pp.383~398. [23]Chang, C., K. Chen, D.F. Waggoner and T. Zha, 2016, “Trends and Cycles in China's Macroeconomy”, NBER Macroeconomics Annual, 30(1), pp.1~84. [24]Copeland B. R. and M. S. Taylor, 2003, “Trade and the Environment: Theory and Evidence”, Princeton University Press. [25]Dong, F., Y. Guo, Y. Peng and Z. Xu, 2022, “Economic Slowdown and Housing Dynamics in China: A Tale of Two Investments by Firms”, Journal of Money Credit and Banking, 54(6), pp.1839~1874. [26]Fischer, C. and M. Springborn, 2011, “Emissions Targets and the Real Business Cycle: Intensity Targets versus Caps or Taxes”, Journal of Environmental Economics and Management, 62(3), pp.352~366. [27]Grossman, G.M. and A.B. Krueger, 1995, “Economic Growth and the Environment”, The Quarterly Journal of Economics, 110(2), pp.353~377. [28]Hanna, R. and P. Oliva, 2015, “The Effect of Pollution on Labor Supply: Evidence from a Natural Experiment in Mexico City”, Journal of Public Economics, 122, pp.68~79. [29]Shapiro, J. S., and R. Walker, 2018, “Why is Pollution from US Manufacturing Declining? The Roles of Environmental Regulation, Productivity, and Trade”, American Economic Review, 108(12), pp.3814~3854. [30]Ye, H. J., Z. Huang and S. Chen, 2023, “Air Pollution and Agricultural Labor Supply: Evidence from China”, China Economic Review, 82, pp.102075.