Energy consumption patterns in the accommodation sector—the New Zealand case

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Energy consumption patterns in the accommodation sector—the New Zealand case

ReferencesShowing 9 of 9 papers
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Greenhouse gas emissions from hydropower: The state of research in 1996
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Energy requirements of household consumption: a case study of The Netherlands
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The development of environmental initiatives in tourism: responses from the London hotel sector
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Residential energy demand in OECD-countries and the role of irreversible efficiency improvements
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A study of energy performance of hotel buildings in Hong Kong
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Environmental Auditing: A Tool for Assessing the Environmental Performance of Tourism Firms
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Die globale Faktor Vier-Strategie für Klimaschutz und Atomausstieg
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Residential energy consumption across different population groups: comparative analysis for Latino and non-Latino households in USA
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CitationsShowing 10 of 192 papers
  • Research Article
  • Cite Count Icon 52
  • 10.1016/j.ijhm.2012.02.001
Energy benchmarking in support of low carbon hotels: Developments, challenges, and approaches in China
  • Mar 3, 2012
  • International Journal of Hospitality Management
  • Wilco Chan

Energy benchmarking in support of low carbon hotels: Developments, challenges, and approaches in China

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  • Research Article
  • Cite Count Icon 47
  • 10.3390/su13126574
The Role of Performance and Environmental Sustainability Indicators in Hotel Competitiveness
  • Jun 9, 2021
  • Sustainability
  • Zorica Duric + 1 more

Environmental protection and environmental sustainability are becoming increasingly important factors in the hotel business and their competitiveness, in a market that brings numerous benefits. Environmental sustainability is, increasingly, considered one of the most important functions of the hotel business, as well as communication and marketing, which attracts a larger number of guests. Some of the key aspects of hotel environmental sustainability are performance and environmental sustainability indicators, as well as hotel management of environmental performance in order to establish efficiency in that process. The principal question arising is how environmentally sustainable business affects hotel performance, and what are the most important indicators of the environmental hotel business. The aim of this article is to offer an insight into, and analysis of, performance and indicators of the environmental sustainability of hotels through the relevant literature. A case study from Serbia is used to point out the complexity and the significance of these indicators in the hotel business, as well as to emphasise the importance of environmental reports in the case of Serbia. The findings of our study are significant because they help hotel managers identify new opportunities for employing more sustainable processes for saving resources.

  • Research Article
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  • 10.1016/j.jclepro.2016.03.177
Reprint of: Quantifying direct and indirect carbon dioxide emissions of the Chinese tourism industry
  • Jul 19, 2017
  • Journal of Cleaner Production
  • Weiqing Meng + 4 more

Reprint of: Quantifying direct and indirect carbon dioxide emissions of the Chinese tourism industry

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  • 10.3390/su10072118
The Relationship between Tourism, Carbon Dioxide Emissions, and Economic Growth in the Yangtze River Delta, China
  • Jun 21, 2018
  • Sustainability
  • Lingling Chen + 2 more

Quantifying the dynamics of regional tourism in a low-carbon economy context is a pivotal issue to develop energy policies, and to decompose the national carbon abatement. Based on a case study approach for the Yangtze River Delta (YRD), China, the relationship between tourism, carbon dioxide (CO2) emissions, and economic growth were examined. The bottom-up approach, decoupling analysis, and Logarithmic Mean Divisia Index (LMDI) decomposition were integrated and applied. The results from 2001 to 2015 indicated that tourism-induced energy consumption and CO2 emissions in YRD increased from 896.90 × 108 MJ to 3207.40 × 108 MJ, and 673.55 × 104 t to 2152.27 × 104 t, respectively. Tourism-related transport from Shanghai was the major contributor towards emissions. The decoupling relation between CO2 emissions and economic growth, in general, were desirable in YRD’s tourism, except in 2004. However, the situation in Shanghai was complicated. Additionally, industry size and expenditure size effect were principal factors to promote carbon emissions growth, whereas energy intensity, spatial structure, and sectorial structure had negative effects. Key issues for policymakers have been highlighted and discussed.

  • Book Chapter
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  • 10.1016/b978-0-12-812746-9.00004-3
Chapter 4 - The Role of Potential Factors/Actors and Regime Switching Modeling
  • Jan 1, 2018
  • The Economics and Econometrics of the Energy-Growth Nexus
  • Roula Inglesi-Lotz

Chapter 4 - The Role of Potential Factors/Actors and Regime Switching Modeling

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  • Cite Count Icon 40
  • 10.1016/j.ecolecon.2003.08.007
Exploring methods and practicalities of conducting sector-wide energy consumption accounting in the tourist accommodation industry
  • Jan 1, 2004
  • Ecological Economics
  • Jan Warnken + 2 more

Exploring methods and practicalities of conducting sector-wide energy consumption accounting in the tourist accommodation industry

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  • 10.1016/j.tourman.2007.03.024
Tourism-induced rural energy consumption in the Annapurna region of Nepal
  • May 21, 2007
  • Tourism Management
  • Sanjay K Nepal

Tourism-induced rural energy consumption in the Annapurna region of Nepal

  • Research Article
  • Cite Count Icon 277
  • 10.2167/jost547.0
Measuring National Carbon Dioxide Emissions from Tourism as a Key Step Towards Achieving Sustainable Tourism
  • Jul 1, 2006
  • Journal of Sustainable Tourism
  • Susanne Becken + 1 more

Most tourism-related activities require energy directly in the form of fossil fuels or indirectly in the form of electricity often generated from petroleum, coal or gas. This consumption leads to the emission of greenhouse gases, mainly carbon dioxide. Tourism is not a traditional sector in the System of National Accounts and as a result no country possesses comprehensive national statistics on the energy demand or emissions specifically resulting from tourism. This paper suggests two approaches for accounting for carbon dioxide emissions from tourism: a bottom-up analysis involving industry and tourist analyses, and a top-down analysis using environmental accounting. Using the case study of New Zealand, we demonstrate that both approaches result in similar estimates of the degree to which tourism contributes to national carbon dioxide emissions. The bottom-up analysis provides detailed information on energy end-uses and the main drivers of carbon dioxide emissions. These results can be used for the development of targeted industry-based greenhouse gas reduction strategies. The top-down analysis allows assessment of tourism as a sector within the wider economy, for example with the purpose of comparing tourism&#x2019;s eco-efficiency with other sectors, or the impact of macroeconomic instruments such as carbon charges.

  • Book Chapter
  • Cite Count Icon 7
  • 10.1007/978-94-010-0616-3_2
Timelines, Environments and Issues of Risk in Health: The Practical Algebra of (x,y,t,a)
  • Jan 1, 2002
  • Pip Forer

Life, as lived, is essentially a health risk, and it is a risk in terms of the environment we encounter just as surely as it is a risk in terms of the inherited genetics and lifestyle choices of individuals. We may make wise, or less wise, choices about how we equip ourselves to face health risks in the environment day by day. We may show similar variations in sagacity about where, when and what we choose to visit. But in the end we cannot avoid interaction with our environment and its highly variable risks. Such risks may be localised and short term, such as the risk of cutting one’s foot on glass on a beach on New Year’s Day, after revellers have been at work. They may be more widespread, cumulative and severe, such as the danger from exposure to sunshine in a summer, or a lifetime in environments with low levels exposures to, or absence of, subtle factors which spur or deter long-term deterioration in health (Schaerstrom 1996, Sabel 2000). There may be factors which are vague and generally invisible to the population, such as abnormal levels of background natural radiation, and/or there may be factors which act with a lag and only after extreme exposure (see Chapter 1). And risks may also be highly dynamic in space and time, as instanced by a range of biological vectors or the impact of a human carrier of a transmittable disease (Cliff et al. 1993). As discrete organisms ourselves, we may seek to modify our environment to mitigate such risks, and often succeed, but there remain relict risks of varying degrees of concern wherever we are.

  • Open Access Icon
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  • Cite Count Icon 3
  • 10.1108/s2042-1443(2010)0000003004
Chapter 1 Tourism and Climate Change
  • Jan 1, 2010
  • Christian Schott + 2 more

This chapter contextualizes the interrelationships between tourism and climate change and thus provides an introduction to this volume. It commences with a brief but comprehensive overview of the key issues identified by climate change research, including an update since the 2007 report by the Intergovernmental Panel on Climate Change as well as a brief discussion of the latest rounds of climate change negotiations. The pursuing discussion is informed by these points and explores climate change's indirect and induced impacts on tourism and possible ramifications. Both of these parts highlight behavioral change as a critical factor to both adaptation and mitigation thus motivating the psychological contribution in an effort to shed light on the obstacles to behavioral change. In the concluding section, the chapter synthesizes the discussion grounded in multiple disciplines into a set of research themes that the volume subsequently begins to address.

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Energy use is an indicator of economic growth. However, high energy intensity has two main disadvantages. First, low energy efficiency increases a country’s dependence on other countries, especially when the country lacks energy sources. Second, if the country’s energy needs are met using traditional fossil fuels, this increases its CO2 emissions and reduces its air quality. Improving energy efficiency and reducing energy intensity are essential to reach the sustainability targets. This paper investigates the determinants of energy use in Turkiye for the period 1991–2019 by taking a dual approach. First, utilizing the Tapio decoupling factor, the decoupling factor analysis is not only being done for total energy use and real GDP, but also for industrial energy use and industrial income. Second, the factors determining the country’s total energy use are also examined, followed by an investigation of the indicators of energy use in the industry sector, which is highly energy intensive. For the industrial sector, two different decomposition analyses are performed and results are compared. The refined Laspeyres index method is adopted, and for each analysis, three main factors are considered. The empirical findings demonstrate that the income effect and population effect increased Turkiye’s total energy use, whereas the energy intensity effect decreased it. The first decomposition analysis for the industrial energy use reveals partly contrasting results with the previously published articles. For the industry sector, the second analysis show that productivity and employment increased Turkiye’s sectoral energy use; however, the sector’s energy intensity reduced it. Turkiye achieved some success in terms of reducing energy intensity at the sectoral and aggregate levels; however, as the findings of the present study demonstrate, further efforts are needed to lessen the country’s energy dependence and also to achieve future environmental sustainability targets. Trends relating to the determining factors in total and sectoral energy use are also compared in this paper, and some policy implications are presented.

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An assessment of the energy requirements of different intensive forage production systems was carried out at the Indian Grassland Fodder, and Agroforestry Research Institute, Jhansi. This included assessment of energy use and output for five intensive crop production systems: (1) sorghum (single‐cut)–berseem, (2) cowpea–sorghum (single‐cut)–berseem + mustard–maize + cowpea, (3) sorghum (multi‐cut)–berseem + oats, (4) guar–oats–maize and (5) sorghum (single‐cut)–wheat–fallow. In all the systems, the Napier bajra hybrid (IGFRI‐3) was transplanted in regular plots of 50 m × 13 m. Results revealed that the total annual energy use was highest for sorghum (multi‐cut)–berseem + oats (36 606 MJ ha−1), followed by sorghum (single‐cut)–berseem + mustard, sorghum (single‐cut)–berseem–cowpea, guar–oats–maize and sorghum (single‐cut)–wheat–fallow (for which values were 31 086, 30 449, 29 867 and 25 956 MJ energy ha−1, respectively). The high value found for sorghum (multi‐cut)–berseem + oats might be attributable to the multi‐cuts in this system. Energy use by fertilizers represented the major part of the total energy use, amounting to 28–38 % in all treatments, followed by energy used in electricity, machinery, seeds, human labour and farmyard manure (FYM), in case of all with slight increase in input. In sorghum–wheat, energy use by seeds occupied the second position, followed by energy used in electricity, human labour, FYM and machinery/diesel. Pesticides contributed the least energy utilization in all the treatments. Herbicides were used for the control of weeds. Among the five forage production systems, sorghum (single‐cut)–berseem + mustard–maize + cowpea was found to be the most energy efficient, followed by sorghum (multi‐cut)–berseem + oats–sorghum (multi‐cut), sorghum (single‐cut)–berseem–cowpea, guar–oats–maize and sorghum (single‐cut)–wheat–fallow. Sorghum (single‐cut)–berseem + mustard–maize + cowpea increased the fertility of the soil, resulting in a higher percentage of organic carbon, higher availability of nitrogen and optimal balancing of the C:N ratio in the upper layers of the soil. These intensive crop production systems also maintain the optimum microbial population in the crop root zone. The benefit–cost ratio (B:C ratio) for the most energy‐efficient forage production system was 1.37 : 1. However, the highest B:C ratio was found in the sorghum–wheat rotation (1: 1.57).

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The goals of the project were to: (1) improve the environment by reducing fossil fuel emissions and reducing the total energy used on small animal farms; (2) stimulate the economy of local and regional communities by creating or retaining jobs; and (3) improve the profitability of Missouri livestock producers by reducing their energy expenditures. Historically, Missouri scientists/engineers conducted programs on energy use in agriculture, such asmore » in equipment, grain handling and tillage practices. The MAESTRO program was the first to focus strictly on energy efficiency associated with livestock production systems in Missouri and to investigate the applicability and potential of addressing energy efficiency in animal production from a building efficiency perspective. A. 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  • Zhaojie Wang

Agricultural activities emit about 10-12% greenhouse gases each year. Moreover, the total amount is on the rise, which can significantly contribute to global warming. To get governments to pay more attention to greenhouse gas emissions from agricultural activities, so that the necessary regulations can be implemented. This paper studies the relationship between agricultural land expansion and greenhouse gas emissions. My initial hypothesis was that ceteris paribus, the agricultural land expansion would cause a rise in greenhouse gas emissions. I obtained 25 years of data for 12 countries from the World Development Indicators Database of the World Bank. And created a panel data frame. The variables exist in it are: Total greenhouse gas emissions (kt of CO2 equivalent), Energy use (kg of oil equivalent per capita), Alternative and nuclear energy (% of total energy use), Agricultural land (% of land area), GDP per capita (current US$). In order to cope with the possible heteroscedasticity problem in the regression, several of the variables were processed logarithms. This paper used a Two-way Fixed effect model which controls fixed effects from both cross section and time. The explained variable is log (GHG emissions), and the explanatory variables are log (energy use per capita), log (GDP per capita), clean energy using rate, and percentage of agricultural land in total land. However due to the presence of multicollinearity, log (GDP per capita) was removed. This paper also tested the autocorrelation and used the Cochrane-Orcutt Iterative Process to estimate the autocorrelation coefficient to transform all variables so that solve the autocorrelation issue. The final regression model is as follows: ln(Greenhouse Gases emission)= + 1.06*ln(Energy use per capita) – 0.009*(Alternative and nuclear energy % of total energy use) + 0.0074*(Agricultural land % of land area). = . The overall F-test of this model is significant, and the individual t-tests of the coefficients of each variable are all significant. R2=92.18, adjR2=91.04. This shows that the explanatory power of the model is strong. This outcome is consistent with my initial hypothesis that agricultural land expansion does lead to an increase in greenhouse gas emissions. The other two coefficients are also consistent with our common sense. This result can help governments to decide on the planning of land use. If the current amount of energy used and the types of energy used do not change, a country develops agriculture, it will inevitably lead to more greenhouse gas emissions. More Importantly, it is not like industrial manufacture, normally there are few regulations and policies on agricultural GHG emissions. But the quantitative results of the model tell us that as agriculture expands, it is necessary for the government to implement regulations and policies on it.

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