Elsevier

Building and Environment

Volume 49, March 2012, Pages 259-269
Building and Environment

Effectiveness and equity implications of carbon policies in the United States construction industry

https://doi.org/10.1016/j.buildenv.2011.10.002Get rights and content

Abstract

With an increasing American public desire to regulate carbon emissions from stationary and mobile sources, and with more states adopting renewable energy standards and green building codes as an effort toward green environment initiatives, there is an imperative need to evaluate the effectiveness and equity implications of using different mechanisms to reduce carbon emissions in the construction and facility management industry. After all, building construction and operation contributes more than one-third of the carbon emissions in the United States (US). However, the impact of emerging carbon regulatory policies on the construction industry is still unclear. This paper presents a carbon regulation based duopoly model to evaluate the effectiveness and equity of various carbon policies including emission standards, carbon tax, and emissions trading. An empirical analysis of the US housing industry is conducted to illustrate the impacts on the industrial production, emission reduction target, market structure, technology selection, and carbon cost allocation etc. The results encompass emission reduction contributions from large and small firms, the extent of carbon cost burden pass-through to consumers, changes in house price, industry output, and market share. Especially, the analysis shows the market-based mechanisms outperform the emission standards in terms of effectively achieving emission targets while maintaining a stable industrial production. To meet the 17% emission reduction target, a carbon price of $22.3 per metric ton is expected for construction firms. About 54% of carbon cost will be passed through to the end consumers at this carbon price.

Highlights

► The study establishes an integrated carbon policy analysis model. ► Market-based policies have less negative impact on industry structure, output, and price. ► Large firms take greater responsibility for emission reduction and adopting Low Carbon Technologies. ► Carbon price is $22.3 per ton to meet the 17% emission reduction target. ► Contractors bear increasing cost burden as carbon price goes up.

Introduction

Over the last century, the average global surface temperature has increased by 0.74 ± 0.18 °C (1.33 ± 0.32 F). This growing temperature, primarily due to increasing concentrations of Greenhouse Gases (GHG) from human activities, has caused severe global climate change, sea level rise, massive flooding, landscape changes, and infectious diseases spread, etc. [1]. Failing to address climate change can also inflict considerable economic damages. According to the Stern Review on the Economics of Climate Change [2], global Gross Domestic Product (GDP) will reduce by roughly 5% annually for inaction on climate change. Under the most severe scenario, the loss could amount up to 20% of the world’s economic output. By contrast, the cost of reducing GHG emissions (mainly CO2) and adapting to climate change could be limited to only 1% of global GDP annually.

World leaders have been collaborating closely to combat climate change and to reduce carbon emissions over the last two decades. The development led to the first global agreement in 1997, the Kyoto Protocol. The Kyoto Protocol set legally binding targets for 37 industrialized countries and the European community to reduce GHG emissions by 2012 [3]. More recently, over 110 countries signed on to the nonbinding Copenhagen Accord at the United Nations Climate Change Conference in 2009 [4]. The Copenhagen Accord emphasizes urgent climate change initiatives in accordance with the principles of common but differentiated responsibilities and respective capabilities, recognizes that the increase in global temperature should be less than 2 °C, and commits to take actions to meet this objective consistent with science and on the basis of equity and finance plans.

Furthermore, both developed and developing countries have made strong commitments to reduce carbon emissions in a long term [4], [5]. The Obama Administration is committed to reduce carbon emissions by 17% below 2005 levels by 2020, 83% below by 2050 [6]. European Union countries unconditionally commit to adequately reduce their emissions by at least 20% below 1990 levels, and to conditionally reduce them by 30% below 1990 levels by 2020 if other developed countries and more advanced developing nations commit to comparable emission reductions. China pledges to reduce emissions per unit of economic output by 40–45% relative to 2005 levels. India is obligated to reduce its emission intensity by 20–25% by 2020. And Brazil aims to reduce emissions by 38–42% from business-as-usual levels by 2020. It is obvious that carbon intensive industries including power generation, petrochemical, transportation, and construction must be strictly regulated to successfully achieve these emission reduction targets.

The construction industry had the third highest carbon emissions among the US industrial sectors. The US Environmental Protection Agency (EPA) [7] reported that 131 million metric ton carbon dioxide equivalent (MMTCO2e) were produced by construction site activities in 2002. Among those emissions, 76% of emissions result from fossil fuel combustion for on- and off-road construction equipment, and 24% come from purchased electricity. Moreover, the embodied emissions from construction material processing and transportation account for a great amount [8], [9]. For example, cement production emitted almost 77 MMTCO2e annually [10]. The construction process consumes 16% of total iron and steel production annually [11], which contributes more than 20 MMTCO2e in 2002 [12]. Taking all embodied emissions from other sectors into consideration, the emissions from the construction industry are estimated at 470 MMTCO2e or approximately 6.8% of the US total emissions according to the Green Design Institute at Carnegie Mellon University [13]. Additionally, construction emissions sources would cover facility operation and maintenance when the life cycle project emission is to be determined [14]. Based on the estimates from the US Department of Energy, building operations were responsible for approximately 38% of total US carbon emissions in 2002 [15]. This number remains close for both developed and developing countries even when different emission estimation methods are used [16], [17], [18], [19].

The US federal and state governments have already taken actions. The US EPA endorsed the goal of reducing 46 MMTCO2e GHG emissions in the building sector (compared to the 2002 level) by 2012 [20]. On October 5, 2009, the Executive Order 13514 was signed by President Obama that requires all federal agencies to lead by example in building clean energy economy and reduce carbon emissions [21]. At the state level, by passing Assembly Bill 32, the state of California calls for 26 MMTCO2e of emission reductions from the green building sector, which represents 15% of California’s 2020 GHG emission reduction target of 169 MMTCO2e [22]. With an increasing public desire to regulate carbon emissions, and with more agencies adopting building and energy standards in their efforts toward green environment initiatives, there are imperative needs for the construction industry to understand emerging carbon policies and evaluate the impact of various policy options.

Section snippets

Carbon regulation and policy

Various regulations and policy approaches exist to mitigate carbon emissions. These polices, in addition to addressing the global environment and public health, must be able to correct the market failure caused by the negative environmental externality. The externality arises when the cost of carbon emissions from construction activities is not factored in the market price, although, carbon emissions cause significant social and economic impacts. The following sections describe three major

Unregulated market

This research aims to investigate the effectiveness and economic impact of carbon policies on the US construction industry. Among a number of theoretical models, the Nash–Cournot model is recognized as offering the best performance to explain the behavior of firms in an oligopoly market compared to other popular models, e.g. the Stackelberg leadership model and the Bertrand competition model [44]. The classic Nash–Cournot competition model was therefore modified to incorporate carbon regulation

Model initialization

The construction industry involves different market segments: housing, industrial, and heavy construction. It appears unreasonable to assume one single product or service for the whole industry considering quite different construction services among construction sectors. It is also oversimplified to define a single demand function or one emission measurement factor for the whole construction industry given unique characteristics of individual construction sector. In this research, we select the

Conclusion

This paper develops a series of models to illustrate how carbon regulatory policies affect the construction industry. Practically, the paper presents an empirical analysis of the US housing industry to evaluate the effectiveness and equity implications for all sizes of companies under three regulatory policies including emission standards, carbon tax, and emissions trading. The analysis shows the market-based mechanisms outperform the emission standards in terms of effectively achieving

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