农业工程学报
農業工程學報
농업공정학보
2013年
19期
224-232
,共9页
土地利用%生态%风险评价%珠江三角洲
土地利用%生態%風險評價%珠江三角洲
토지이용%생태%풍험평개%주강삼각주
land use%ecology%risk assessment%Pearl River Delta
为了探讨经济快速发展地区土地利用变化对土地生态系统造成的风险,该文以珠江三角洲为研究对象,分析了其1990-2006年土地利用变化特征,构建了区域生态风险指数,并以5 km×5 km的单元网格进行系统采样,借助空间自相关和半方差分析方法,探讨了珠江三角洲的生态风险空间分布及变化特征,结果表明:1990-2006年,珠江三角洲土地利用发生变化的面积高达12105.05 km2,占土地总面积的29.35%,建设用地快速扩张,基塘持续增加,耕地、林地迅速减少;整个珠江三角洲的生态风险指数由1990年的0.2713增至2006年的0.3318,风险程度增加了22.31%,在空间分布上具有明显的正相关性,空间集聚逐渐增强,深圳、东莞、广州市区、花都、南海、顺德、佛山市区及中山等是生态风险指数高值聚集区,指数变化更为明显,风险程度明显提高;高、较高生态风险区面积快速增加,由1990年的4874.52 km2增加到2006年的12494.93 km2,占土地总面积的比例由11.82%增至30.30%;生态风险程度呈现明显的圈层结构,以佛山市区-广州市区-深圳为轴向外风险程度逐渐降低。研究结果为区域土地可持续利用提供新的思路和方法,从而促进土地利用与生态环境的协调发展。该研究为生态风险管理政策的制定提供科学依据。
為瞭探討經濟快速髮展地區土地利用變化對土地生態繫統造成的風險,該文以珠江三角洲為研究對象,分析瞭其1990-2006年土地利用變化特徵,構建瞭區域生態風險指數,併以5 km×5 km的單元網格進行繫統採樣,藉助空間自相關和半方差分析方法,探討瞭珠江三角洲的生態風險空間分佈及變化特徵,結果錶明:1990-2006年,珠江三角洲土地利用髮生變化的麵積高達12105.05 km2,佔土地總麵積的29.35%,建設用地快速擴張,基塘持續增加,耕地、林地迅速減少;整箇珠江三角洲的生態風險指數由1990年的0.2713增至2006年的0.3318,風險程度增加瞭22.31%,在空間分佈上具有明顯的正相關性,空間集聚逐漸增彊,深圳、東莞、廣州市區、花都、南海、順德、彿山市區及中山等是生態風險指數高值聚集區,指數變化更為明顯,風險程度明顯提高;高、較高生態風險區麵積快速增加,由1990年的4874.52 km2增加到2006年的12494.93 km2,佔土地總麵積的比例由11.82%增至30.30%;生態風險程度呈現明顯的圈層結構,以彿山市區-廣州市區-深圳為軸嚮外風險程度逐漸降低。研究結果為區域土地可持續利用提供新的思路和方法,從而促進土地利用與生態環境的協調髮展。該研究為生態風險管理政策的製定提供科學依據。
위료탐토경제쾌속발전지구토지이용변화대토지생태계통조성적풍험,해문이주강삼각주위연구대상,분석료기1990-2006년토지이용변화특정,구건료구역생태풍험지수,병이5 km×5 km적단원망격진행계통채양,차조공간자상관화반방차분석방법,탐토료주강삼각주적생태풍험공간분포급변화특정,결과표명:1990-2006년,주강삼각주토지이용발생변화적면적고체12105.05 km2,점토지총면적적29.35%,건설용지쾌속확장,기당지속증가,경지、임지신속감소;정개주강삼각주적생태풍험지수유1990년적0.2713증지2006년적0.3318,풍험정도증가료22.31%,재공간분포상구유명현적정상관성,공간집취축점증강,심수、동완、엄주시구、화도、남해、순덕、불산시구급중산등시생태풍험지수고치취집구,지수변화경위명현,풍험정도명현제고;고、교고생태풍험구면적쾌속증가,유1990년적4874.52 km2증가도2006년적12494.93 km2,점토지총면적적비례유11.82%증지30.30%;생태풍험정도정현명현적권층결구,이불산시구-엄주시구-심수위축향외풍험정도축점강저。연구결과위구역토지가지속이용제공신적사로화방법,종이촉진토지이용여생태배경적협조발전。해연구위생태풍험관리정책적제정제공과학의거。
Land use changes not only affect the land structure and types, but also affect the degree of health of the land ecological system. In order to explore the ecological risks caused by the land use change, and provide scientific support for the formulation of the relevant policies and the measures, this paper described a case study on the Pearl River Delta. The characteristics of land use change were analyzed during 1990 to 2006, and the ecological risk was conducted based on the land use change, the ecological risk plots of 5km×5km were applied. Spatial distribution and gradient differentiation characters of the ecological risk in the study area were analyzed by means of spatial autocorrelation and sub-analysis of variance. The conclusions were as follows:1) The changed land (12105.05km2) occupied 29.35%of the total land in the Pearl River Delta during 1990 to 2006. The area of construction land expanded quickly, while dike-pond increased intensively, and farmland and forests evidently decreased. Population growth, economic development, industrialization, urbanization, and the swarm of foreign investment were the main factors which led to the land use changes. 2) In 1990, the ecological risk value of the whole region was 0.2713, which increased to 0.3318;the degree of risk has increased by 22.31%. Moran’s I was used to estimate the spatial autocorrelation of the ecological risks. From 1990 to 2006, the global Moran’s I from 0.6451 increased to 0.7137. The spatial distribution of ecological risk showed a positive autocorrelation and significant local spatial clustering pattern. The spatial variability was primarily the result from structural factors. The high-value regions included Shenzhen, Dongguan, Guangzhou Urban District, Huadu, Nanhai, Shunde, Foshan Urban District, and Zhongshan. The changes of ecological risk in these regions were more significant, and the degree of risk increased intensively. 3) The area of high risk region and relatively high risk region expanded quickly, from 4874.52 km2 in 1990 to 12494.93 km2 in 2006, and the proportion of the total land from 11.82%to 30.30%. Meanwhile, the area of low risk region and inferior risk region decreased from 18901.54 km2 in 1990 to 13983.87 km2 in 2006, and the proportion of the total land from 45.84%to 33.91%. 4) Ecological degree of risk showed an obvious ring structure, and decreased from the axis of Foshan Urban District-Guangzhou Urban District-Shenzhen to other regions. From 1990 to 2006, the high and relatively high risk region expanded gradually from the two banks of Pearl River Estuary to the middle area of Pearl River Delta, and the degree of risk reduced gradually towards the west and the east of the Pearl River Delta. With the speeding up of the economic development and urbanization course in the Pearl River Delta, land use has intensively changed, which obviously increases land ecological risks. These conclusions can provide new ideas and methods for sustainable land use and ecological risk management, and help promote the coordination of land use and the ecological environment.