基于3S技术的霍山县土壤侵蚀动态研究
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摘要
本研究运用3S技术,以安徽省霍山县为研究区域,以TM(MSS)遥感影像(包括1979、1994、2002和2006年度四个时期)为主要数据源,对霍山县土壤侵蚀现象进行动态研究,对比分析研究区内不同年份间的土壤侵蚀状况与演变趋势,结合历史资料和实地调查,并综合运用水土保持理论与方法,总结多年水土保持经验,寻找区域生态改良因子,对比选择出较适合研究区的土壤侵蚀治理措施,为探寻小流域更为有效的土壤侵蚀治理提供有用信息,并为示范推广区域的土壤侵蚀综合防治技术提供参考依据。通过研究,所得主要结论如下:
     1.通过对霍山县四个时段的遥感影像的解译及实地调查,分析研究土壤侵蚀状况,获得全县的土壤侵蚀的主要现状特征:目前,全县土壤侵蚀总面积为804.28km~2,占全县总面积的39.40%。研究区域内土壤侵蚀强度整体上是以轻度侵蚀为主,侵蚀面积为681.96km~2,占全县总面积的33.40%,局部区域以中度侵蚀类型为主;
     2.全县土壤侵蚀面积呈现减少趋势,土壤侵蚀强度明显降低。土壤侵蚀面积由1979的1276.52km~2减少到2006年的804.28km~2,20多年间减少了472.24 km~2,占全县总面积的23.13%。表明:20多年来霍山县的土壤侵蚀综合治理获得了明显成效,有效地遏制了土壤侵蚀的发生与发展,显著改善了全县的生态环境;
     3.不同时期的土壤侵蚀变化规律是,以轻度侵蚀为主,不同级别土壤侵蚀强度空间变化差异显著,在1979、1994、2002和2006年四个典型时期,轻度、中度和强度侵蚀面积分别占土壤侵蚀总面积的97.83%、96.55%、95.26%和84.20%,为土壤侵蚀强度的主要类型;
     4.不同时段土壤侵蚀强度变化规律是,土壤侵蚀呈现逐渐减少的趋势,表现为由较高强度级侵蚀向较低强度级侵蚀转化,不同等级的土壤侵蚀强度空间变化差异显著,但在不同时段土壤侵蚀强度的面积变化和空间变化有所不同,土壤侵蚀面积在不同时段的变化量排序依次为:2002~2006年(13.03km~2)<1979~1994年(316.96km~2)<1994~2002年(802.23km~2),表明:霍山县在1994~2002年期间的土壤侵蚀治理效果显著,水土保持工作进展顺利;
     5.霍山县土壤侵蚀表现为以轻度和中度侵蚀为主,强度侵蚀次之,总体来看,无强剧烈侵蚀的特征。同时,不同等级的土壤侵蚀强度分布具有较明显的空间分异特征。其中,强度和极强度侵蚀则主要分布在人为生产活动频繁的低覆盖度植被区或陡坡区域;中度侵蚀主要发生在岩石区域的中覆盖度植被区;而轻度侵蚀主要分布在受人为活动影响较少的高覆盖度植被区,以及水库、沟道两侧耕地、园地和缓坡区域。说明人为活动方式及其引起的植被覆盖状况和地面坡度等地形因子状况的变化,是影响区域土壤侵蚀的重要因子。
This research utilizes the 3S technology, take the Huoshan County in Anhui Province as the study geographic area, take the TM(MSS) remote sensing phantom (including four periods about 1979, 1994, 2002 and 2006) as the main data sources. Taking a dynamic study about the soil erosion phenomenon in Huoshan County. Comparative analysis soil erosion and the evolutionary trend during different years in study area. Combined with the historical data and field survey, and integrated use the theory and methods of soil and water conservation, summing up years of experience in soil and water conservation, searching for ecological improvement factors in regional, compared to select a more suitable control measures of the soil erosion. It is order that provide useful information for more effective utilization of soil erosion, and provide references for control the soil erosion of demonstrated promote regions. Through the research, the main conclusions are as follows:
     1. Through interpreting the four phrases’remote sensing images and field investigation in Huoshan County, to obtain the county's main current characteristics of soil erosion. At present, the total soil-erosion areas of the county is 804.28km~2, accounting for 39.40% of the total area of the county. Study area is slight erosion of the overall strength of the main erosion area of 681.96km~2, accounting for 33.40% of the total area of the county. Some area dominated by moderate erosion types.
     2. The areas of soil erosion showed a decreasing trend in all County. Soil erosion intensity decreased obvious. Areas of soil erosion reduced from 1276.52km~2 to 804.28km~2 during 1979 to 2006, reduced 472.24 km~2 during 20 years, which is accounting for 23.13% the total area of the County. It indicated, the comprehensive management of soil erosion obtained remarkable results during 20 years in Huoshan County, and curbed the occurrence of soil erosion and development effectively. It improved significantly the ecological environment in the County.
     3. The variation ruler of soil erosion in different periods is slight erosion mainly. Spatial variation in different levels of soil erosion intensity is significantly. Four typical periods of 1979,1994,2002 and 2006 showed the main types of soil erosion are mild, moderate and strength-erosion of soil erosion areas accounting for 97.83%, 96.55%, 95.26% and 84.20% of the total area respectively.
     4. The variation ruler of soil erosion intensity in different periods is gradually reduced. It shows the higher intensity level erosion transform to the lower. Spatial variation in different levels of soil erosion intensity is significantly. However, the variation of the soil erosion intensity between area and spatial indicated is difference in different periods. The soil erosion areas’variation order in different of the periods is 2002~2006(13.03km~2)<1979~1994(316.96km~2) <1994~2002 (802.23km~2). It indicated that significant effects of soil erosion control, soil conservation work has proceeded smoothly in the period from 1994 to 2002 in Huoshan County.
     5.Slight and moderate erosion is an integral part in Huoshan County, intense erosion followed. On the whole, it is no strong features erosion. At the same time, the distribution with different levels of soil erosion intensity has obvious spatial difference among them. The intense and extremely high erosions are distributed mainly in the regions where the activities of human production with the low-frequency coverage of vegetation or steep. Moderate erosion occurs mainly in rocky areas with the medium coverage of vegetation regions. Slight erosion mainly affected on the high coverage of vegetation areas by human activities in less effect, and reservoirs, channel on both sides of cultivated land, garden plot and the gentle slope area. It shows human activities and their methods with ground vegetation, slope and other conditions change is an important factor for affecting the soil erosion of region.
引文
[1]熊晓姣,张家来,闫峰陵,等.国内外水土流失与土壤退化现状及特点分析[J].湖北林业科技.2006.4:41-44.
    [2] Centre for Development and Environment and Geographical Bernensia.Precious Earth From Soil and Water Conservation to Sustainable Land Management, 1996, ISCO.
    [3] Hans, Hurni. From Soil & Water Conservation to Sustainable Land Management. Towards Sustainable land Use 9thISCO Conference,1996, ISCO.
    [4]周作亨.国内外水土保持发展的动态综述[J].江西水利科技. 1993.20(1):87-92.
    [5]蔡强国.紫色土坡坡地不同土地利用对水土流失过程的影响[J].水土保持通报,1998,(2):1-8.
    [6]杨光,丁国栋,屈志强.中国水土保持发展综述[J].北京林业大学学报(社会科学版).2006.5(增刊):72-77.
    [7]刘震.从我国水土流失现状看水土保持生态建设战略布局[J].中国水土保持.2002.(6):7-10.
    [8]张建凤,张福州,邵胜利.水土保持在水利可持续发展中的作用分析[J].今日科苑.2008.14:31.
    [9]孙厚才,赵健.中外水土保持理念对比[J].长江科学院院报.2008.25(3):9-13.
    [10]张金慧,邓淑珍,王莉,等.为了祖国山川更加秀美—中国水土流失与生态安全综合科学考察行动[J].中国水利.2009.(7):4-19.
    [11]赵园春.3S技术在可渡河流域水土流失动态监测中的应用研究[J].山西水土保持科技.2009.3:14-17.
    [12]索安宁,赵文喆,王天明,等.近50年来黄土高原中部水土流失的时空演化特征[J].北京林业大学学报.2007.29(1):90-97.
    [13]毕华兴.“3S”技术在水土保持中的应用[M].北京:中国林业出版社.2008
    [14]杨涛.基于3S技术的水土保持生态修复区土坡僵蚀调变研究:[硕士学位论文].泰安:山东农业大学,2007.
    [15]王礼先.水土保持学·中国大百科全书(农业卷)[M].北京:中国林业出版社. 2004.
    [16]郑粉莉,王占礼,杨勤科.土壤侵蚀学科发展战略[J].水土保持研究.2004.11(4):1-10.
    [17]宋颖.土壤侵蚀模型研究进展及发展方向[J].山西水利科技.2006.161(3):39-41.
    [18]孙厚才,赵健.中外水土保持理念对比[J].长江科学院院报.2008.25(3):9-13.
    [19]王青兰.水土保持生态建设概论[M].黄河水利出版社.2008.08.
    [20]中国数字科技馆(http://b2museum.cdstm.cn/swc/stbc/index.html).
    [21]王冬梅.农地水土保持[M].中国林业出版社.2002.10.
    [22]张富,余新晓,景亚安,等.黄土高原水土保持防治措施对位配置研究[M].黄河水利出版社.2007.04.
    [23]张峰,李珍存.两当县水土保持生态修复遥感监测技术初探.水土保持通报.2006,26(6):72-73,78.
    [24]袁利.基于“3S”技术的峨庄流域土壤侵蚀格局及动态:[硕士学位论文].泰安:山东农业大学,2008.
    [25]邬伦,刘瑜.地理信息系统:原理、方法和应用[M].北京:科学出版社,2005,289~299.
    [26]王礼先,朱金兆.水土保持学(第2版)[M].中国林业出版社.2005.03.
    [27]张广军,赵晓光.水土流失及荒漠化监测与评价[M].水利水电出版社.2005.09.
    [28]李占斌,朱冰冰,李鹏.土壤侵蚀与水土保持研究进展[J].土壤学报.2008.45(5):802-809.
    [29]牛崇桓,陈云明.国外水土保持概况(Ⅰ).水土保持科技情报.1997.2:1-5.
    [30]刘孝盈,汪岗,陈月红,等.美国水土保持的特点及对我国的启示[J].中国水土保持科学.2003.1(2):102-107.
    [31] Soil and water conservation society of Ameriea, 2000 fiseal budget for soil and water conservation in Ameriea, 2000.
    [32] Wischmeier, W.H. and Smith,D.D.Predicting rainfall erosion losses-a guide to conservation planning.Agriculture handbook.1978.USDA, 537.
    [33] Leopold L B, Thomas Maddock J R. The Flood Control Controlversy-Big dams, little dams, and land management.Newyork: The Ronald Press Company,1970:69-91.
    [34] Buie E C.USDA, A history of United States department of agriculture water resource activities, 1979.
    [35] Liu Xiaoying,Chen Yuehong,Wang Gang,et a.l Achievements, Approach and Benefits of Soil and Water Conservation in China: Proceedings of the 9th International Symposium on River Sedimentation[C].Beijing:Tsinghua University Press, 2004.
    [36] Renwick W H, Carison K J, Hayes-bohanan J K. Trends in recent reservoir sedimentation rates in Southwestern Ohio [J]. JournalofSoilandWaterConservation, 2005, 60(2):72-79.
    [37]牛崇桓,陈云明.国外水土保持概况(Ⅱ).水土保持科技情报.1997.3:1-4.
    [38]张科利,彭文英,张竹梅.日本近50年来土壤侵蚀及水土保持研究评述[J].水土保持学报.2005.19(2):61-64,68.
    [39]徐祝.日本水土流失规律研究进展[J].水土保持科技情报.2005.2:19-22.
    [40]狄俊一.日本估算土壤流失量的应用模型[J].水土保持应用技术.2007.1:46-48.
    [41]佟伟力.印度小流域综合治理考察[J].水土保持科技情报,1996,4:1-3.
    [42]刘东.亚洲几个国家的水土保持和小流域管理状况[J].水土保持科技情报.2004,2:8-29.
    [43]秦伟,刘孝盈,于琪洋,等.印度土壤侵蚀与防治研究概况及其对我国的启示[J].中国水利水电科学研究院学报.2009.7(1):42-50.
    [44] Barbiero L,Parate H R,Descloitres M,et al.Using a structural approach to identify relationships between soil and erosion in a semi-humid forested area,south India[J].Catena,2007,70(3):313-329.
    [45]胡延杰,施昆山,等.印度社会林业进展[J].世界林业研究,2001,14(3):55-60.
    [46] Honore G,Our Land.Ourselves—a Guide to Watershed Management in India[M].New Delhi:Government of India,1999.
    [47] Sivanappan R K.Soil and water management in the dry lands of India [J].Land Use Policy,1995,12(2):165-175.
    [48] Narayan D V V, Babu R.Estimation of soil erosion in India[J].J.Irrig.Drain.Engg.,1983,109(4):419-431.
    [49] Lekha K R.Field instrumentation and monitoring of soil erosion in coir geotextile stabilized slopes—A case study[J].Geotextiles and Geomembranes,2004,22:399-413.
    [50]殷心.印度水土流失严重[N].中国国土资源报,2002.6.2(3).
    [51] Sen K K,Rao K S,Saxena K G.Soil erosion due to settled upland farming in the Himalaya:A case study in Pranmati watershed[J].International Journal of Sustainable Development and World Ecology,1997,4(1):65-74.
    [52] Ram K A,Tsunekawa A,Sahad D K,et al.Subdivision and fragmentation of land holdings and their implication in desertification in the Thar Desert,India[J].Journal of Arid Environments,1999,41:463-477.
    [53] Maji A K, Nayak D C, Krishna N D R, et al.Soil information system of Arunachal Pradesh in a GIS environment for land use planning [J].JAG,2001,3(1):69-77.
    [54] Reddy G P O,Maji A K,Gajbhiye K S.Drainage morphometry and its influence on landform characteristics in a basaltic, Central India2a remote sensing and GIS approach[J].International Journal of Applied Earth Observation and Geoinformation,2004,6:1-16.
    [55] Babu R, Tejwani K, Agarwal G,et al.Distribution of erosion index and Isoerodent maps of India[J].Indian J.Soil Cons,1978,6(1):1-14.
    [56] Raghunath B,Khullar A K,Thomas P K.Rainfall energy maps of India[J].Indian J.Soil Cons,1982,10(2):1-17.
    [57]舒洪岚,李沛然.印度北部丘陵地区水土保持措施[J].江西林业科技,2005,2:47-48.
    [58]金永丽.流域发展计划—印度干旱、半干旱地区农业发展的新战略[J].世界农业,2005,3:37-40.
    [59]刘孝盈,秦伟,赵磊磊.印度土壤侵蚀及防治研究[J].国外水利.2008.16:53,56-58.
    [60] Bhandari P M,Bhadwal S,Kelkar U.Examining adaptation and mitigation opportunities in the context of the integrated watershed management programme of the Government of India[J].Mitig Adapt Strat Glob Change,2007,12:919-933.
    [61]杨光,丁国栋,屈志强.中国水土保持发展综述.北京林业大学学报(社会科学版).2006.5(Supp.):72-77.
    [62]王礼先.我国水土保持的理论与方法[J].中国水利,2006,(12):16-19.
    [63]唐克丽.中国水土保持[M].北京:科学出版社,2005.
    [64]杨勤科,李锐,曹明明.区域土壤侵蚀定量研究的国内外进展[J].地球科学进展,2006,21(9):31-38.
    [65]李锐.中国21世纪水土保持工作的思考[J].中国水土保持.2000.(7):325.
    [66]李锐,杨勤科,吴普特,等.中国水土保持科技发展战略思考[J].中国水土保持科学,2003,1(3):529.
    [67]夏卫生.具有中国特色的水土保持科学体系[J].水土保持通报,1989,9(4):30-35.
    [68]黄秉维.陕西黄土区域土壤侵蚀的因素和方式[J].科学通报,1953,(9):63-75.
    [69]黄秉维.陕西黄土区域土壤侵蚀的因素和方式.科学通报.1958(9):53-59.
    [70]姚文艺,陈界仁,秦奋.黄河多沙粗沙区分布式土壤流失模型研究[J].水土保持学报.2008.22(4):21-26.
    [71]周佩华,李银锄,黄义端,等.2000年中国水土流失趋势预测及其防治对策[J].中国科学院西北水土保持研究所集刊.1988.7:57-71.
    [72]胡良军,李锐,杨勤科.基于GIS的区域水土流失评价研究[J].土壤学报.2001.38(2):169-174.
    [73]李运学,邓吉华.水土保持是我国必须长期坚持的一项基本国策[J].水土保持学报.2002.16(5):142-144.
    [74]张学俭.水保宣传近10年[J].中国水土保持.2008.9:4-6,22.
    [75]水土保持司.全国首届水保新闻宣传培训班在大连举行.水土保持应用技术.2008.5:37.
    [76]蔡景平.水土保持“3S”集成智能决策系统开发与应用.水土保持科技情报.2003.5:10-11.
    [77]刘组文.“3S”原理与应用[M].北京:中国建筑工业出版社.2006.
    [78]王玲玲,任桂菊,张丽.简述水土保持综合治理措施的诸多要点[J].农村实用科技信息.2008.10:46.
    [79]夏彪,陈俊,雷香莲.民乐县内陆河小流域水土流失综合治理思路与创新模式研究[J].甘肃水利水电技术.2008.44(5):346-347,349.
    [80]安徽省霍山县林业志.霍山县林业局编.9-12.
    [81]六安市统计局.六安统计年鉴.六安市统计学会编.33,35,40,41.
    [82]姚孝友,周虹.淮河流域水土保持工作面临的问题及21世纪发展方向[J].治淮.2001.1:3-4.
    [83]鲁峰,赵全科.淮河流域水土流失及治理.枣庄师专学报[J].1994.4:115-117.
    [84]淮河信息中心.水利部领导关于治淮工作的有关论述.中国水利.2008.4:2-3.
    [85]覃德华,毕晓丽,葛剑平.近30年来卧龙自然保护区土地覆盖变化动态分析[J].安徽农业科学,2007,35(23):7237-7239.
    [86]任家强,周柄中,戴激光,等.RS与GIS支持的武义县城市化土地利用动态变化研究[J].吉林农业大学学报,2008,30(1):44-48,58.

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