Spatio-temporal variations and drivers of ecological carrying capacity in a typical mountain-oasis-desert area, Xinjiang, China
Graphical abstract
Introduction
Ecological carrying capacity (ECC) was developed based on the carrying capacity concept, with its origins from Malthus's “population theory”, which describes the limitation of food supply on population growth (Seidl and Tisdell, 1999). Ecologists have adopted this concept to describe the relationship between population, environment, and social economy that an ecosystem can support. It is the ability to provide adequate resources and enabling environmental conditions for the healthy development of the human social system (Jin et al., 2018; Martire et al., 2015).
In recent decades, China's economy and population have experienced fast growth. During this period, in the relatively less-developed northwest region of Xinjiang, the Chinese government has implemented successively economic development policies such as “China's Western Development Policy” and “Silk Road Economic Belt” (Central Government Portal of China, 2014), bringing rapid social and economic development. Meanwhile, climate change is affecting all regions of the world (El-Beltagy and Madkour, 2012; Ripple et al., 2020), accentuating the impacts of human activities in Xinjiang. To achieve regional sustainable development, it is critical to balance economic development and environmental wellbeing (Miao et al., 2016; Shi et al., 2020).
Xinjiang is located in the arid and semi-arid region of Northwest China, with a fragile ecology and limited natural resources. Ecological problems such as land desertification (Li et al., 2014; Li et al., 2013) and salinization (Zhuang et al., 2021) are prominent. Due to the extensive distribution and complex evolution mechanisms of environmental impacts, it is difficult to evaluate quantitatively the overall regional ecological status. It is similarly challenging to analyze quantitatively the synergy of various driving factors on temporal and spatial changes. Lacking such knowledge could compromise the ecological restoration efforts (Ge et al., 2015). Dang and Liu (2012) observed that the primary problem in formulating a regional-scale ecological restoration plan is how it will affect the carrying capacity and sustainability of the target area. Zhang et al. (2020b) realized that the primary premise of ecological restoration is ascertaining the ecological carrying capacity (ECC) as the basis to formulate a detailed regional ecological restoration plan. It is also critical to monitor ECC decline in tandem with the continual population and economic growth (Skonhoft and Solem, 2001). Hence, the ECC concept offers a powerful tool to monitor and evaluate sustainable development, especially in ecologically stressed and fragile areas (Kessler, 1994; Świąder, 2018; Yue, 2012).
The ECC techniques have been applied to different situations in many regions. The data sources include Statistical Yearbook (Wei et al., 2020; Ariken et al., 2021), field measurements (Bu et al., 2020), and remote sensing (Wu et al., 2020). The common ECC evaluation methods include ecological footprint (Solarin and Bello, 2018; Swiader et al., 2020), net primary productivity (NPP) (Ren et al., 2020), state space model (Mao and Yu, 2001), and “3S” (remote sensing, geographic information system and global positioning system) technology comprehensive analysis (Wu and Hu, 2020; Yue, 2012). Despite the diverse data and methods, ECC research in China is still beset by limitations. Most data sources are statistical data. Due to inherent data limitations, the whole administrative region is often taken as the basic research unit. The study indicators often ignore intrinsic ecosystem attributes and focus on people-centered ones, such as gross land area per capita, waste treatment capacity, and industrial CO2 emission. The bias towards large-scale statistical data tends to restrict the studies to the provincial administrative units and broad-brush indicators, thus neglecting the complex local ecological reality (Wei et al., 2020; Ariken et al., 2021). In addition, a large amount of measured data has been used in studies related to water ecological carrying capacity (WECC). The measured data allows monitoring the ecological water health and the stresses caused by human activities, but they are limited to the county scale and water-resource perspective (Bu et al., 2020). Overall, many studies are one-sided, lack regional relevance and integration, and do not fully consider the innate study-area characteristics.
The rapid development of Xinjiang is closely associated with utilizing its scarce water resource to exacerbate the ecological crisis. The intensification of salinization and desertification has exerted undue pressure on the environment (Zhang and Huisingh, 2018; Zhou et al., 2020). The constrained consideration of a single ecological factor (e.g., water resources, vegetation, or land), the entire administrative division, and the short duration cannot fully reflect Xinjiang's ecological stresses, let alone understanding the trends and causes of ECC changes. Recent advances in research techniques for temporal and spatial analysis of ECC and availability of new data offer opportunities to strengthen relevant studies (Wan et al., 2017; He and Xie, 2019). The results may offer an important theoretical and practical basis for Xinjiang's ecological restoration and sustainable development.
This study evaluated ECC's spatio-temporal characteristics and internal drivers in Xinjiang from 1982 to 2017. A series of research techniques and data sources were applied in an integrated manner to conduct the research, including: (1) remote sensing data and geographic information system technology; (2) Global Inventory Modelling and Mapping Studies (GIMMS) Normalized Difference Vegetation Index (NDVI); (3) evapotranspiration data; (4) meteorological data; (6) statistical data on socio-demographic and economic domains; and (6) findings and data of previous studies of arid and semi-arid areas for a comprehensive assessment of the natural conditions of the study area (Wu et al., 2020).
The specific study objectives were to: (1) explore the spatio-temporal patterns and changes of ECC in Xinjiang using the remote sensing evaluation model; (2) analyze the status and multi-year changes of ECC in various prefectures using the cluster heat-map; and (3) explain the internal drivers of spatio-temporal ECC changes based on meteorological and human factors using partial correlation analysis and residual analysis. This study could provide a basis to inform the sustainable development of Xinjiang as a typical ecological vulnerable area. It could offer reference value for implementing ecological and environmental protection policies in similar areas in China and other countries.
Section snippets
Study area
China's Xinjiang Uygur Autonomous Region (equivalent to the province administrative unit; hereinafter referred to as Xinjiang) is selected as the study area. It is located in the hinterland of the Eurasian continent and the northwest border of China. Situated at 73° 20 ‘~ 96° 25′E and 34° 15’ ~ 49° 10′N (Fig. 1a), the large area covering about 1.66 × 106 km2 accounts for one-sixth of China's land area. Xinjiang includes 14 prefectures: Aksu Prefecture (Aksu); Altay Prefecture(Altay); Bayingol
Spatio-temporal pattern of ECC in Xinjiang
The spatial pattern of the average ECC in Xinjiang from 1982 to 2017 is depicted in Fig. 3. The average ECC of the whole Xinjiang was 0.29, indicating that a median ECC was getting very close to the good level. The ECC changes were evaluated by sampled years and geometrical patterns.
The extremely poor ECC areas are mainly distributed in the Tarim Basin in Southern Xinjiang, which includes the Taklamakan Desert (the largest desert in China). Not surprisingly, this area lacks water resources,
NDVI index and water availability as critical co-determinants of ECC trends
The spatial distribution of high ECC values was closely related to high NDVI values. Areas with high ECC values were distributed in oases and mountains in central and south Xinjiang with relatively better vegetation cover. Our ECC range and spatial distribution were similar to the findings of Wu et al. (2020) in the arid and semi-arid region of Central Asia. In addition, this study found differences in ECC spatial distribution in areas without vegetation. The general pattern indicated that the
Conclusion
Xinjiang is located in arid Northwest China, constituting the core area of the Silk Road Economic Belt. This paper analyzed the spatial patterns and trends of ECC in Xinjiang from 1982 to 2017 on the whole and at divisional and prefecture scales. The hierarchical structure and multi-year changes of ECC in the 14 prefectures were analyzed by cluster heat-map. Using partial correlation analysis and residual analysis, this study examined the internal drivers of ECC spatio-temporal patterns and
CRediT authorship contribution statement
Jianguo Wang: Writing – original draft, Conceptualization. Fei Zhang: Project administration. Chi-Yung Jim: Writing – review & editing. Ngai Weng Chan: Writing – review & editing. Verner Carl Johnson: Writing – review & editing. Changjiang Liu: Formal analysis, Methodology. Pan Duan: Visualization. Jupar Bahtebay: Supervision.
Declaration of Competing Interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgments
This research was supported by the Strategic Priority Program of the Chinese Academy of Science (CAS), Pan-Third Pole Environment Study for a Green Silk Road (XDA20040400), and the Tianshan Talent Project (Phase III) of the Xinjiang Uygur Autonomous Region. We thank the editor and anonymous reviewers for their valuable comments and suggestions to this paper.
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