地理学报
地理學報
지이학보
ACTA GEOGRAPHICA SINICA
2015年
4期
591-603
,共13页
廖谌婳%封志明%李鹏%张景华
廖諶婳%封誌明%李鵬%張景華
료심획%봉지명%리붕%장경화
刀耕火种农业%时空变化%轮歇周期%利用频率%植被恢复%老挝北部
刀耕火種農業%時空變化%輪歇週期%利用頻率%植被恢複%老撾北部
도경화충농업%시공변화%륜헐주기%이용빈솔%식피회복%로과북부
swidden agriculture%spatio-temporal changes%swidden cycle%frequency of swidden use%fallow vegetation recovery%Landsat%Laos
基于“3S”技术研究了老挝北部1990-2011年刀耕火种农业时空变化的总体特征及其不同阶段土地利用变化、刀耕火种农业土地利用强度(利用频率、轮歇周期)及其对休耕期次生林自然恢复过程的影响。结果表明:①1990-2011年,刀耕火种农业总体上呈增加趋势,由15.38万hm2增加到了23.84万hm2,增幅为54.98%;刀耕火种农业的增加主要发生在波乔省南部和琅勃拉邦省,减少主要发生在丰沙里省。②刀耕火种农业主要分布在海拔高度500~1500 m、坡度10°~30°的地区,增加主要发生在海拔高度500~800 m、300~500 m和800~1000 m的地区,以及坡度10°~20°和20°~30°的地区。刀耕火种农业的地类转变方向主要是有林地,转入和转出率均高达80%。③2000-2011年,老挝北部刀耕火种农业的利用频率约为2~3次,时间间隔1~7年不等;轮歇周期有所缩短,变化幅度不大。④老挝北部刀耕火种农业的休耕期次生林自然恢复状况与轮歇周期关系显著,二者相关系数为0.9698。当轮歇周期长达10年时,次生林能够恢复到该区域有林地NDVI的平均水平。
基于“3S”技術研究瞭老撾北部1990-2011年刀耕火種農業時空變化的總體特徵及其不同階段土地利用變化、刀耕火種農業土地利用彊度(利用頻率、輪歇週期)及其對休耕期次生林自然恢複過程的影響。結果錶明:①1990-2011年,刀耕火種農業總體上呈增加趨勢,由15.38萬hm2增加到瞭23.84萬hm2,增幅為54.98%;刀耕火種農業的增加主要髮生在波喬省南部和瑯勃拉邦省,減少主要髮生在豐沙裏省。②刀耕火種農業主要分佈在海拔高度500~1500 m、坡度10°~30°的地區,增加主要髮生在海拔高度500~800 m、300~500 m和800~1000 m的地區,以及坡度10°~20°和20°~30°的地區。刀耕火種農業的地類轉變方嚮主要是有林地,轉入和轉齣率均高達80%。③2000-2011年,老撾北部刀耕火種農業的利用頻率約為2~3次,時間間隔1~7年不等;輪歇週期有所縮短,變化幅度不大。④老撾北部刀耕火種農業的休耕期次生林自然恢複狀況與輪歇週期關繫顯著,二者相關繫數為0.9698。噹輪歇週期長達10年時,次生林能夠恢複到該區域有林地NDVI的平均水平。
기우“3S”기술연구료로과북부1990-2011년도경화충농업시공변화적총체특정급기불동계단토지이용변화、도경화충농업토지이용강도(이용빈솔、륜헐주기)급기대휴경기차생림자연회복과정적영향。결과표명:①1990-2011년,도경화충농업총체상정증가추세,유15.38만hm2증가도료23.84만hm2,증폭위54.98%;도경화충농업적증가주요발생재파교성남부화랑발랍방성,감소주요발생재봉사리성。②도경화충농업주요분포재해발고도500~1500 m、파도10°~30°적지구,증가주요발생재해발고도500~800 m、300~500 m화800~1000 m적지구,이급파도10°~20°화20°~30°적지구。도경화충농업적지류전변방향주요시유임지,전입화전출솔균고체80%。③2000-2011년,로과북부도경화충농업적이용빈솔약위2~3차,시간간격1~7년불등;륜헐주기유소축단,변화폭도불대。④로과북부도경화충농업적휴경기차생림자연회복상황여륜헐주기관계현저,이자상관계수위0.9698。당륜헐주기장체10년시,차생림능구회복도해구역유임지NDVI적평균수평。
Swidden agriculture is an age-old, prevalling but controversial farming practice in Montane Malnland Southeast Asia (MMSEA). In the uplands of northern Laos, swidden agriculture has become the predominant land use type for centuries. The swidden system has undergone dramatic transformations since the mid-1990s. The debate on the change of swidden cultivation is linked to global critical issues of land use/cover change, biodiversity and climate change. Since the implementation of Reducing Emissions from Deforestation and forest Degradation (REDD) by the United Nations, an increasing attention has been given to swidden agriculture in the humid tropics nationally and internationally. However, very little is known or reported about the explicit spatial information of swidden agriculture and the consequences of the transitions at macroscopic scale. For the purpose of understanding the spatial and temporal dynamics of swidden system, the intensity of swidden use and fallow forest recovery in northern Laos, in this study, the swidden agriculture in 1990, 2002, and 2011 were mapped and delineated with Landsat Thematic Mapper (TM) and Enhanced Thematic Mapper plus (ETM+) imagery (30 m) with a decision tree classification method, followed by the analysis of spatio-temporal changes of swidden agriculture. Then, annual successive TM/ETM+ images during the period 2000-2010 were used to delineate the dynamics of burning phase and cropping phase. Subsequently, the burned pixels derived in 2000 were compared with those in the following years (2001-2011) under ArcGIS 10.0 to investigate the temporal development, land use frequency and swidden cycle with time-series Landsat-based NDVI data. Finally, as the swidden cycle changed from 1 to 11 years, the fallow vegetation recovery process was studied. The results showed that: (1) From 1990-2011, the area of swidden agriculture increased by 54.98%, from 153,800 to 238,400 ha. The increased swidden cultivation were malnly found in Luang Prabang and southern Bokeo; while the decreased parts were malnly in Phongsali. (2) The swidden agriculture malnly increased at the elevations of 500-800 m, 300-500 m and 800-1000 m and on the slopes of 10°-20° and 20°-30°. More than 80%of swidden farming land was transformed from forests. (3) During the period 2000-2011, the frequency of swidden use in northern Laos was about 2 or 3 times. The intervals of any two swidden use phases ranged from 1 to 7 years. In comparison with swidden cycles and the related proportion of swidden farming in the years of 2000, 2003 and 2007, swidden cycles in most parts were shortened. (4) There was a significant correlation between fallow vegetation recovery and swidden cycle, with a correlation coefficient of 0.9698. The NDVI of regenerated vegetation could be equal to the average NDVI value of forest when the swidden cycle reaches 10 years.