اشتراک امرجی برای بهره برداری از منابع زیست توده های کشاورزی در چین
|کد مقاله||سال انتشار||مقاله انگلیسی||ترجمه فارسی||تعداد کلمات|
|20315||2007||16 صفحه PDF||سفارش دهید||8736 کلمه|
Publisher : Elsevier - Science Direct (الزویر - ساینس دایرکت)
Journal : Energy Policy, Volume 35, Issue 9, September 2007, Pages 4704–4719
On the basis of Odum's ecological economic measure of emergy as embodied solar energy, a system account of biomass resource exploitation by agriculture in China 2004 is developed in this paper, which supplements a former study on corresponding long-term historical trends during 1978 to 2000 (Chen et al., 2006. Emergy-based analysis of the Chinese agriculture. Agriculture, Ecosystems and Environment 115, 161–173). The aggregate fluxes and indicators for biomass resource exploitation in China 2004 are calculated and illustrated when compared with those for 2000 to elucidate the latest status of the Chinese agriculture as the exploitation sector for biomass resource. Data sources and algorithm are presented in detail as basic references for related analysis involving the ecological economy of biomass exploitation in agriculture.
As the socioeconomic sector for exploitation of biomass resource, the Chinese agriculture, with a long history and fundamental status in the national economy, fed 22% of the world's population with only 10% of the world's arable land. Its impact is further reinforced due to the growing exploitation of agricultural product as biomass resource (NDRC, 2006). The efficient exploration and utilization of agriculture-related resources demand systematic researches based on overall and unified accounting in different scales, which have made considerable progress recently (Chen and Chen, 2006a and Chen and Chen, 2006bChen et al., 2006a and Chen et al., 2006b; Chen and Chen, 2007d, Chen and Chen, 2007e, Chen and Chen, 2007f, Chen and Chen, 2007a, Chen and Chen, 2007b and Chen and Chen, 2007c; Chen et al., 2007). Based on the concept of embodied energy out of a combination of energetic (Lotka, 1956) and systems ecology (Odum, 1983, Odum and Odum, 1983, Odum, 1996 and Odum, 1994; Odum, 1996; Odum, 1994), emergy analysis was firstly presented in 1983 by Odum, to fully integrate the value of free environment investment, goods, services and information in a common unit. As a thermodynamic-based environmental accounting approach, emergy evaluation tracks the total amount of resources required to produce something by tracing all resource flows back to the conventionally believed Earth's ultimate energy source of solar radiation (Odum, 1994; Scienceman, 1987). Emergy in terms of embodied solar energy represents all the solar energy insolated by the earth to produce and sustain a certain level of output. As a measure of energy used in the past, emergy analysis is totally different from conventional energy analysis which merely accounts for the remaining available energy at present, therefore proved a more feasible approach to evaluate the status and position of different energy carriers in the universal energy hierarchy. Till now, various systems have been evaluated by emergy analysis on a regional (Higgins, 2003) or national scale (Ulgiati et al., 1994) around the world. Emergy analyses have also been carried out for agro-ecosystems and agricultural industries, such as some farming systems (Bastianoni et al., 2001), ethanol production (Bastianoni and Marchettini, 1996) and meat and dairy production (Serrano et al., 2003). In the mainland China, emergy analyses of Chinese society on national and regional scales were first introduced by S.F. Lan (Lan and Yu, 1993; Lan and Odum, 1994; Lan et al., 2002). Referring to the Chinese literatures published in the mainland in recent years, a research upsurge of emergy-based analysis emerged, involving the exploration of the theory itself (Cai and Qin, 2004; Shen et al., 2004), the application of emergy approach on macro social economic systems on different scales (Zhao and Li, 2004; Dai and Zhou, 2005), and in various fields including industries (Feng et al., 2005; Wang et al., 2006 and Wang et al., 2006), business (Wang, 2005) and agricultural systems, of which agriculture as one of the most important sectors in mainland China was paid more attention and related studies were more than 60 covering most Chinese provinces, autonomous regions or municipalities as shown in Fig. 1 (Liu et al., 1999; Su et al., 1999; Zhang et al., 1999; Li et al., 2001; Chen and Xu, 2002; Dong and Gao, 20003; Min et al., 2004; Li et al., 2003; Dong, 2003; Dong et al., 2004; Liu et al., 2004; Ai and Liu, 2004; Lu et al., 2004; Zhang, 2004; Zhang et al., 2005 and Zhang et al., 2005; Fu et al., 2005; Lu et al., 2005a; Lu et al., 2005b; Liu and Li, 2005; Liu and Li, 2005a; Zhang et al., 2005 and Zhang et al., 2005; Zhang et al., 2006; Li et al., 2006; Duan and Xu, 2006; Wang et al., 2006 and Wang et al., 2006; Zeng et al., 2006; Bai et al., 2006; Lu et al., 2006; Dong et al., 2006). Full-size image (41 K) Fig. 1. Regions in mainland China covered by emergy analysis for biomass exploitation via agriculture. Figure options Most researchers focused on some specific areas, such as the cropping and pasture ecotone in North China (Dong, 2003; Lu et al., 2004; Fu et al., 2005; Li et al., 2006; Dong et al., 2006), the arid region of Northwest China (Li et al., 2001; Chen and Xu, 2002; Min et al., 2004; Li et al., 2003; Liu et al., 2004; Liu et al., 2005b), and the Loess Plateau (Dong and Gao, 2003; Dong et al., 2004; Zhang, 2004). On a national scale, Yan integrated the national and provincial agricultural products in 1995 (Yan, 2001). In 2002, Lan presented a preliminarily study for three departments of farming, animal husbandry and fishery with the data in the separate years of 1988 and 1998 (Lan et al.,2002; Lan, 1995). A recent paper by Chen et al (Chen et al., 2006b) revealed the overall panorama of the Chinese agriculture during 1980–2000 against historical background with drastic political and socioeconomic transitions, in which emergy analysis was applied to diagram, explain and illustrate the Chinese agro-ecosystem, to evaluate environmental and economic inputs and harvested yield, and to assess the sustainability of the Chinese agriculture as a whole. In the work mentioned above, the structure of inputs/outputs and various system indicators were also examined from a historical perspective for the contemporary Chinese agriculture in the two decades after Reform and Open in the late 1980s. As a result, the temporal variation of indicators such as increasing environmental load ratio (ELR), decreasing emergy self-support ratio (ESR) and emergy yield ratio (EYR) illustrated a weakening sustainability of the Chinese agro-ecosystem characteristic of profound transition from a self-supporting system to a modern industry based on nonrenewable resources (NR) consumption. As a basic reference for the related analysis involving the ecological economy of agriculture as exploitation sector of biomass resource and also an elucidation of the latest development, this paper presents an emergy system account of the exploitation of biomass resource via Chinese agriculture for the year 2004 focusing on the data sources and corresponding algorithms.
نتیجه گیری انگلیسی
With a unified ecological economic measure of emergy as embodied solar energy, this paper presents a system account for the Chinese agriculture as exploitation sector of biomass resource in 2004, as a supplement to a recent study on corresponding long-term historical trends during 1978–2000. All aggregate fluxes and indicators for the Chinese agriculture in 2004 have been estimated, illustrated and compared with those for 2000 to elucidate the recent development of the Chinese agriculture. Data sources and algorithm are presented in detail as basic references for related analysis involving the ecological economy of agriculture. As the system indicator values for the exploitation sector of biomass resource in China 2004 as against those for 2000 indicates, although the overall status of resource utilization remains relatively stable within recent years, the Chinese agriculture increasingly depends on economic investment in terms of more consumption of resources such as soil, fuels and fertilizers, thus associated with a weakening sustainability along with the profound transition from a self-supporting tradition of intensive manure and labor force input to the modernized style with intensive consumption of industrial products.