Journal of Geographical Sciences >
The effects of urbanization on ecosystem services for biodiversity conservation in southernmost Yunnan Province, Southwest China
*Corresponding author: Liu Shiliang, PhD and Professor, E-mail: shiliangliu@bnu.edu.cn
Author: Cheng Fangyang, PhD, specialized in landscape ecology and ecosystem ecology. E-mail: chengfangyan@mail.bnu.edu.cn
Received date: 2018-05-10
Accepted date: 2019-01-22
Online published: 2019-07-25
Supported by
National Key Research and Development Program of China, No.2016YFC0502103
National Natural Science Foundation of China, No.41571173
Copyright
Urbanization can profoundly influence the ecosystem service for biodiversity conservation. However, few studies have investigated this effect, which is significant for maintaining regional sustainable development. We take the rapidly developing, mountainous and biodiversity hotspot region, Jinghong, in southern Yunnan Province as the case study. An integrated ecosystem service model (PANDORA) is used to evaluate this regional BESV (ecosystem service value for biodiversity conservation). The modeled BESV is sensitive to landscape connectivity changes. From the 1970s to 2010, regional urban lands increased from 18.64 km2 to 36.81 km2, while the BESV decreased from $6.08 million year-1 to $5.32 million year-1. Along with distance gradients from the city center to the fringe, BESV varies as an approximate hump-shaped pattern. Because correlation analysis reveals a stronger influence of landscape composition on spatial BESV estimates than the landscape configuration does, we conclude that the projected urban expansion will accelerate the BESV reduction. Of the projected urban land, 95% will show a decreasing BESV trend by approximately $2 m-2 year-1. To prevent this, we recommend compact urban planning for the mountainous city.
Key words: urban expansion; ecosystem service; PANDORA; landscape pattern; urban planning
CHENG Fangyan , LIU Shiliang , HOU Xiaoyun , WU Xue , DONG Shikui , Ana COXIXO . The effects of urbanization on ecosystem services for biodiversity conservation in southernmost Yunnan Province, Southwest China[J]. Journal of Geographical Sciences, 2019 , 29(7) : 1159 -1178 . DOI: 10.1007/s11442-019-1651-9
Figure 1 Location of Jinghong County and its urban land expansion during three periods |
Table 1 The socio-economic development of Jinghong County from 1970 to 2010 |
Year | GDP (thousand $) | AOV (%) | TI (%) | UP (%) |
---|---|---|---|---|
1970 | 0.074 | 46.98 | 30.28 | 11.27 |
1990 | 0.26 | 59.83 | 27.48 | 22.76 |
2010 | 2.11 | 25.34 | 42.71 | 40.57 |
Figure 2 Schematic framework of the study (a) and the framework of the PANDORA model (b) (Pelorosso et al., 2017). BESV represents the ES for biodiversity conservation. The full line represents the steps of the study, the dashed line represents the indexes and methods used in this study, and the dotted line represents the original data and the implementation of PANDORA model. |
Figure 4 The uncertainty analysis of the PANDORA model. a, b, c, and d represent the Scenario 1 (the original sample), Scenario 2 (reduces roads based on the original sample), Scenario 3 (adds roads based on the original sample), and Scenario 4 (increases the local fragmentation based on the original sample), respectively. e, f, g, and h represent the BESV of Scenario 1, the BESV of Scenario 2, the BESV of Scenario 3, and the BESV of Scenario 4, respectively. |
Table 2 Indexes of analyses of landscape changes and the BESV variation |
Figure 3 Land use map of the study area in 2010 (a), and the comparison of the performance of the PANDORA model (b), a unit value-based approach (c), and the InVEST model to evaluate the BESV (d). UL, IU, OP, SC, AV, AL, PL, FO, WA, and WE separately represent urban fabric, industrial units, open spaces, scrub, green space, arable land, plantation, forests, inland water, and inland wetland. b, c, and d represent the BESVs evaluated by PANDORA model ($·m-2 year-1), by the unit value-based approach (Costanza et al., 1997a; Ng et al., 2013) ($·m-2 year-1), and the carbon storage evaluated by the InVEST model (mg ha-1) in 2010, respectively. The classification of low, medium and high level applies the equal interval method. |
Figure 5 Annual variation of both urban land and the region’s BESV. ACV and ACI represent annual change velocity and annual change intensity, respectively. |
Figure 6 Distributions of urban land and its expansion from the 1970s to 2010 (a. The distribution of urban land; b. The distribution of the newly grown urban land) |
Figure 7 The distance gradients for the difference between urban land areas (∆Area) and the difference between BESVs (∆BESV) in different periods. The left longitudinal axis shows the standardized ∆Area, and its value increases from bottom to top along the axis. The right longitudinal axis shows the standardized ∆BESV, and its value decreases from bottom to top. The 0 in the X-axis represents the city center. Because of the normalization, the plus-minus state in the Figure is not the same as those in the raw data while the fluctuated trends of these data were consistent with those of the raw data. |
Table 3 Pearson correlation coefficients between the difference (∆) of BESVs and the difference (∆) of landscape metrics |
Period | Moving-window size/km2 | ∆AI | ∆DI | ∆EN | ∆LP | ∆ME | ∆PD | ∆PL | ∆SH |
---|---|---|---|---|---|---|---|---|---|
∆BESV (1970s-1990) | 0.1 | -0.13 | 0.35 | 0.14 | -0.65 | -0.62 | 0.14 | -0.65 | 0.15 |
1 | 0.10 | 0.22 | 0.06 | -0.43 | -0.40 | 0.19 | -0.42 | 0.20 | |
5 | 0.09 | 0.12 | 0.02 | -0.21 | -0.21 | 0.11 | -0.26 | 0.15 | |
∆BESV (1990-2010) | 0.1 | -0.16 | 0.19 | 0.14 | -0.55 | -0.45 | 0.08 | -0.55 | -0.01 |
1 | 0.07 | 0.14 | 0.10 | -0.31 | -0.24 | 0.10 | -0.30 | 0.07 | |
5 | 0.01 | 0.04 | 0.03 | -0.18 | -0.14 | 0.06 | -0.16 | 0.04 |
Table 4 The stepwise regression analysis for the difference (∆) of BESVs and the difference (∆) of landscape metrics |
Period | R2 | p | Regression model |
---|---|---|---|
1970s-1990 | 0.480 | <0.001 | ∆BESV=0.053+0.005∆AI-1.624∆DI-0.038∆LP-0.019∆PL+1.552∆SH |
1990-2010 | 0.327 | <0.001 | ∆BESV=0.001+0.003∆AI-0.902∆DI-0.063∆LP+0.226∆ME+0.890∆SH |
Figure 8 Statistics of BESV changes (∆BESV) of projected urban land in 2030. Different colors represent the different range of variations in BESV. The small figure with different colors above represents the spatial distribution that the color represents below. |
The authors have declared that no competing interests exist.
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