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Taking Hengyang Central District for Example

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Taking Hengyang Central District for Example E3S Web of Conferences 118, 04022 (2019) https://doi.org/10.1051/e3sconf/201911804022 ICAEER 2019 Study on land use change and its impact on ecosystem service value –Taking Hengyang central district for example Fuqiang Huang1, Zengxiang Qi1,* 1School of Architecture, University of South China, 421001 Hengyang, China Abstract. Land use change on ecosystem service value(ESV) and its interaction is significant in the rapid urbanization. The GIS(Geographic Information System) incorporating with ESV equivalent factor is used to quantitatively study the change of land use change and its impact on the ecosystem service value in Hengyang central district. Further more, the Markov model is used to predict the change of land use and ESV in 2030 under the scenario of historical trend development. The results can serve as a useful tool that assists urban planners in their evaluation of ecosystem service value under the impact of land use change. 1 INTRODUCTION use is often used to predict the quantitative change of land use[9]. It is defined as follows: Ecosystem service is the natural environmental condition of human existence and development formed by S(n) = S(n − 1)P (1) ecosystem in the ecological process[1], Whose’s value can provide scientific basis for human beings to improve Where, S(n) and S(n − 1) is the state of the system at the quality of life and production[2]. Land use the time n and n-1 respectively; is the transition cover/change (LUCC) is the main cause of global probability matrix, which defined as follows: environmental change[3], which plays a decisive role in A A … A the change of ecosystem service. In the process of rapid A A … A urbanization, the improper use of land by human beings A = (2) ⋮⋮⋮⋮ has led to the increasing impact of ecological A A … A environment such as water quality purification[4], soil [5] [6] [7] conservation , biodiversity , nutrient cycle , climate Where, is the area of land use i to land use j, i is the [8] regulation and et al. As a result, the function of initial land use category, j is the land use category at the ecosystem services are weakened and degraded, which end of the study period, the row represents the direction seriously affects the balance of regional ecosystems. The of land use conversion, the column represents the source urban central district is the core area of urban of land use conversion. There are two rules in the . development, where the pressure of resources and ∑ =1( i, j=0, 1, 2……, n) (3) environment is becoming more and more prominent. So it is important to study on the land use change and its Where, the sum of elements per row of a matrix is equal to 1. impact on ESV in urban central district. In this study, the characteristics of land use and ESV dynamic change in 0≤≤1( i,j=0, 1, 2……, n) (4) urban central district are revealed based on the Where, each element of the matrix is not negative. LandSatTM data incorporated with ESV equivalent factor in GIS. Futher more, the Markov model is used to 2.2 Ecosystem service value evaluation predict the change of land use and ESV in 2030. The The ESV equivalent factor is the relative contribution results can serve as a useful tool that assists urban rate of ecosystem-generated services, which is equal to planners in their evaluation of ESV under the impact of 1/7 of the national average grain yield market price of land use change. the year[10, 11]. It is defined as follows: = ×× (5) 2 METHODOLOGY -2 Where, is the ESV equivalent factor (¥·hm ), P is 2.1 Markov model the national average grain price (¥·kg-1), Q is the Markov model, which is a special stochastic movement national average grain yield (kg·hm-2). process just like the process of dynamic change of land The formula for calculating ESV is defined as follows: * Corresponding author: [email protected] © The Authors, published by EDP Sciences. This is an open access article distributed under the terms of the Creative Commons Attribution License 4.0 (http://creativecommons.org/licenses/by/4.0/). E3S Web of Conferences 118, 04022 (2019) https://doi.org/10.1051/e3sconf/201911804022 ICAEER 2019 ESV = ∑( ×) (6) Table 2 shows the change of land use in Hengyang central district from 2000-2010. The cultivated land, ESVf = ∑ × (7) forest land, water area and construction land were the most important land use types in Hengyang central Where, ESV is the value of ecosystem services(¥), is district. During 2000-2010, the amount of land use 2 the area of I-th land use type(hm ), is the total value changed to varying degrees that the area of cultivated of ecosystem service function per unit area of land use land and forest land decreased greatly, while the 2 type(¥·hm ·year), ESVf is the value of the f-th service construction land increased greatly. The cultivated land function of the ecosystem(¥), is the total value of was the land type with the largest decrease, which the f-th ecosystem service function per unit area of land decreased by 2277.63hm2 and change rate of 8.69% in use type (¥·hm2·year). 11 years. The forest land, which decreased the change The ESV equivalent factor of Construction land is refer rate of 1384.02 hm2, by 9.32% in 11 years. The third was to the study of Zheng J K[2]. Table 1 shows the ESV per grassland, which decreased the change rate of 103.05 unit area of different landscape types. hm2, by 21.22% in 11 years. Finally, the change rate of 16.92 hm2 in unused land decreased by 30.62% in 11 Table 1. The ESV per unit area of different land use. years. It could be seen that a large number of cultivated Equivalent land and forest land had been transformed into Land use factor ESV(¥·hm-2) construction land to meet the needs of urban development. The construction land was the largest Cultivated land 3.95 11141.51 2 Forest land 23.09 65128.49 range land use, whose change rate of 3520.26 hm and Grassland 15.56 43889.10 had been increased by 56.94% in the past 11 years. The change range of water area was small during the study Water area 125.61 354300.13 2 Construction period, whose area increased by 261.36 hm and the land -6.64 18735.42 change rate of 7.16%. Unused land 0.65 1833.41 Table 2. The change of land use from 2000-2010. 2000 2010 Change 3 STUDY AREA AND DATASETS pr pr Hengyang city is located in the south-central part of op op Hunan Province(110°32′16′′-113°16′32′′), which is an ort ort devia ran sub-center city and important industrial city of Hunan Land Area/ ion Area ion tions ge 2 2 2 Province. Hengyang city plays a regional central role in use hm /% /hm /% /hm /% Changsha-Zhuzhou-Xiangtan urban agglomeration and Cultiva - Xiangnan area, which shoulders the heavy responsibility ted 2620 50. 2392 46. 2277 8.69 of promoting the development of the southern Hunan land 6.38 95 8.75 52 .63 region. The study area of this paper is the central area of - Hengyang city, including Shigu District, Yanfeng Forest 1485 28. 1346 26. 1384 9.32 District, Zhuhui District and Zhengxiang District. land 1.71 88 7.69 18 .02 To analyze how land use change will affect ecosystem - 21.2 service value, historial land-use patterns from 2000, Grassl 485.6 0.9 382. 0.7 103. 2 2010(Figure 1) are used in this study. and 4 4 59 4 05 Water 3651. 7.1 3913 7.6 261. 7.16 area 84 0 .20 1 36 Constr 56.9 uction 6182. 12. 9702 18. 3520 4 land 19 02 .45 86 .26 - Unuse 0.1 38.3 0.0 16.9 30.6 d land 55.26 1 4 7 2 2 4.2 Land use convertion Table 3 shows the convertion of land use during 2000- Fig. 1. Land use of Hengyang central district. (a)2000; (b)2010. 2010. There were four main types of conversion in the central district: the cultivated land, forest land, grassland 4 LAND USE CHANGE AND and water area converted into the construction land, 2 2 2 CONVERTION DURING 2000-2010 whose area were 2264.22 hm , 1391.85 hm , 57.15 hm and 91.89 hm2 respectively; the forest land, water area and construction land converted into the cultivated land, 4.1 Land use change whose area were 415.35 hm2, 154.62 hm2, and 249.39 hm2 respectively; the cultivated land, water area were 2 E3S Web of Conferences 118, 04022 (2019) https://doi.org/10.1051/e3sconf/201911804022 ICAEER 2019 converted into the forest land, whose area were 425.61 water and other reservoirs accounted for a certain hm2 and 60.84 hm2respectively. proportion of the total land use area and per unit area of ESV was the highest. Although the ESV of grassland Table 3. The land use convertion during 2000-2010 and unused land varied greatly, it had a small impact on the regional ESV for it’s low proportion of the total land 2010 use. W Un Land use Cult For ate Cons us 201 Table 4. The change of ESV caused by LUCC from 2000-2010. ivat est Gra r tructi ed 0 ed lan ssla are on lan Tot Land use ESV/108¥ Change of land d nd a land d al 2000 2010 ESV/108¥ Culti Cultivated 2.92 2.67 -0.25 vate 230 42 262 land d 84.
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