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111.
生物土壤结皮(BSC)是荒漠生态系统组成和地表景观的重要特征,在荒漠系统碳的源-汇功能中发挥着重要的作用。本文以沙坡头人工植被区两种典型的BSC(苔藓结皮和藻类结皮)为研究对象,通过对土壤水分的连续测定,确定BSC光合和呼吸作用的有效湿润时间及其与土壤水分、温度和太阳辐射的关系,建立了土壤水分驱动下的固碳模型。以2012年5月19—25日为例,计算了苔藓结皮和藻类结皮在试验期间的日固碳量,并估算了两类结皮的年际固碳量。结果表明:苔藓结皮和藻类结皮由于自身水文物理性质的差别显著影响到其下层土壤水分和温度的变化;降雨是BSC固碳活性的重要来源,并且苔藓结皮更容易受到非降雨水(如雾水、凝结水等)的影响而使其固碳潜力大于藻类结皮。初步估算苔藓结皮和藻类结皮的年固碳量分别可以达到33.33 g·m-2·a-1和14.01 g·m-2·a-1,其中由非降雨水所引起的固碳量达到了6.58 g·m-2·a-1和2.65 g·m-2·a-1,分别占到了全年固碳量的19.7%和18.9%。充分肯定了BSC在荒漠人工植被区碳汇的功能。 相似文献
112.
Ian Smalley 《Area》2008,40(1):131-134
A study of loess in Australia brings the idea of 'desert' loess back into view. Production of particles in deserts still presents problems, but deserts do make adequate storage regions for loess particles – usually produced in adjacent mountains. Straightforward for Central Asia or China (a particle source in High Asia and convenient deserts en route to eventual deposition), but the Sahara and Australian deserts traditionally present problems. If loess material is allowed to be silt-sized clay agglomerate particles as well as the usual clastic primary minerals, then loess in Australia seems reasonable. Loess acquires its remarkable loessic qualities via aeolian deposition – the nature of the particles is perhaps of lesser importance. A more generalised approach to airborne sediments might be attempted, with two major types of suspension material recognised: large dust (maybe coarse and very coarse silt, say 20–60 µm, or perhaps 4–6 phi) and small dust (fine and very fine silt, 2–8 µm, 7–9 phi). Loess is made from large dust. 相似文献
113.
Late Holocene upper bounds of flood magnitudes and twentieth century large floods in the ungauged, hyperarid alluvial Nahal Arava, Israel 总被引:1,自引:0,他引:1
Yael Jacoby Tamir Grodek Yehouda Enzel Naomi Porat Eric V. McDonald Ofer Dahan 《Geomorphology》2008,95(3-4):274-294
The impact of large twentieth century floods on the riparian vegetation and channel morphology of the relatively wide anabranching and braided Nahal Arava, southern Israel, was documented as part of developing tools to (a) identify recent large floods, (b) determine these flood's respective magnitudes in alluvial ungauged streams, and (c) determine long-term upper bounds to flood stages and magnitudes. Along most of its course Nahal Paran, a major tributary that impacts the morphology, floods and sediments of Nahal Arava at the study reach, is a coarse-gravel, braided ephemeral stream. Downstream of the Arava–Paran confluence, aeolian and fluvial sand delivered from eastern Arava valley alters the channel morphology. The sand has accreted up to 2.5 m above the distinct current channels, facilitating the recording of large floods. This sand enhances the establishment of denser riparian vegetation (mainly Tamarix nilotica and Haloxylon persicum) that interacts with floods and affects stream morphology. A temporal association was found between specific floods recorded upstream and tree-ring ages of re-growth of flood-damaged tamarix trees (‘Sigafoos trees’) in the past 30 years. This association can be utilized for developing a twentieth century flood chronology in hyperarid ungauged basins in the region. The minimum magnitude of the largest flood that covered the entire channel width, estimated from flood deposits, is approximately 1700–1800 m3s− 1. This is a larger magnitude than the largest gauged flood of 1150 m3s− 1 that occurred in 1970 about 30 km upstream in Nahal Paran. Our estimation agrees with flood magnitude estimated from the regional envelope curve of the largest floods. Based on Holocene alluvial stratigraphy and OSL dating in the study reach we also conclude that flood stages did not reach the late Holocene ( 2.2 ka) surface and therefore we estimate a non-exceedance upper bound of 2000 m3s− 1 flood magnitudes for Nahal Arava during that interval. This study indicates that in unfavorable areas the combination of hydrology, fluvial morphology and botanic evidence can increase our understanding of ungauged basins and give information crucial for hydrology planning. 相似文献
114.
The contribution of aeolian processes to fluvial sediment yield from a desert watershed in the Ordos Plateau,China 总被引:2,自引:0,他引:2
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In arid zones, many active aeolian dunes terminate at ephemeral and perennial desert rivers. The desert rivers show very high rates of sediment transport that cause deleterious downstream effects on the river system and ecology. High sediment loading has been attributed to severe water erosion of sparsely covered watersheds during infrequent but heavy rainfall. Although aeolian erosion is known to lead to high rates of wind‐blown sand transport, direct confirmation of whether the aeolian processes accelerate or inhibit fluvial sediment loss is lacking. Here, we show that an aeolian‐fluvial cycling process is responsible for the high rate of suspended sediment transport in a Sudalaer ephemeral desert channel in the Ordos Plateau of China. Frequent aeolian processes, but low frequency (once every 3 years on average) flooding, occur in this region. Wind‐blown saltating grains appeared to be unable to cross the desert channel because of interruption of channel‐induced recirculating air flow, and therefore tended to settle in the channel during the windy seasons, leading to channel narrowing. During flooding, this narrowed channel was found to yield a threefold increase in suspended sediment loading and a 3.4‐fold increase in the weight percentage of the 0.08–0.2 mm sediment fraction on 18 July 2012. Loss of stored aeolian sand due to channel erosion accounted for about half of the total sediment yield in this watershed. These findings show that aeolian processes play an essential role in accelerating the sediment yield from a watershed characterized by aeolian‐fluvial interplay and also suggest that the drier the region and the greater the aeolian process, the more the aeolian process contributes to fluvial sediment yield. Copyright © 2013 John Wiley & Sons, Ltd. 相似文献
115.
116.
东准噶尔北部荒漠区植被属土砾质荒漠植被类型,占优势的植物群落为白茎绢蒿(Seriphidium terrae-albae(Krasch)Poljak),覆盖度为20%~25%。为探讨植物地球化学方法在荒漠区找矿的有效性,本文选择了隐伏于荒漠覆盖下的喀拉通克铜镍矿、希勒库都克铜钼矿和阿克塔斯金铜矿作为实例,研究生长在这些矿床地表的白茎绢蒿植物地球化学异常特征及其与矿化的关系。研究发现:这些矿床上部均发育植物地球化学综合异常,综合异常的宽度略大于矿体或矿化带的宽度,异常元素组合具有套合性和分带性。本文认为:(1)植物异常中强度较高、清晰度及连续性较好、规模较大的主导元素组合及其异常参数可以作为区分不同矿化类型的标志或指标,进而圈定成矿靶区;(2)植物综合异常的空间分布及其套合性和分带性,能大致确定隐伏矿床(体)的位置;(3)植物异常的元素组合、异常规模和异常强度,能大致推测隐伏矿床(体)的埋藏深度和矿化规模。 相似文献
117.
巴丹吉林沙漠湖泊及地下水化学特征 总被引:7,自引:0,他引:7
通过对巴丹吉林沙漠丘间湖泊和古日乃、雅布赖、阿拉善右旗等地及其周围浅层地下水离子化学成分分析,探讨了沙漠地区湖水与地下水化学成分特点、水化学类型、空间变化和湖水补给来源。结果显示,巴丹吉林沙漠湖泊水的pH、盐度、TDS和电导率均远远大于地下水。湖水样品中Na+和Cl-含量占绝对优势,大多数盐度较高的湖泊属于Na(K)-Cl-(SO4) 型,个别盐度较低的微咸湖属于Na-(Mg)-(Ca)-Cl-(SO4)-(HCO3) 型。地下水的化学类型多数为Na-(Ca)-(Mg)-Cl-(SO4)-(HCO3)型,属微咸水,个别为Na-Cl-SO4型的咸水。沙漠东南部湖群水的pH值、盐度、TDS和电导率比较低,呈微碱性,属微咸湖;而北部湖群水的pH、盐度、TDS和电导率远远大于东南部湖群,呈中等碱性,为盐水湖。湖水离子化学特征显示沙漠东南部湖群自南向北的演化趋势为:微咸湖→咸水湖→盐水湖。湖水离子化学成分短时间序列变化指示,近9 年宝日陶勒盖、巴丹东湖、巴丹西湖、诺尔图、呼和吉林湖水中的大多数离子的含量有所降低,表明其近9 年来淡水补给量增多。湖水化学成分与湖水位高度显示,巴丹吉林沙漠湖群湖水流向是由东南流向西北。水化学成分和水位分布高度表明,该区沙漠湖水主要来自当地降水补给和来自沙漠东南缘雅布赖山和南缘的黑山头山地降水的补给,而来自祁连山区来水补给的可能性很小。 相似文献
118.
阿拉善高原荒漠植被组成分布特征及其环境解释:Ⅱ.C_4植物组成、分布特征与环境的关系 总被引:5,自引:5,他引:0
研究了阿拉善典型干旱荒漠植被区C4植物的组成特征、空间分布及其与环境因子的相关性。发现C4植物主要集中在藜科(Chenopodiaceae)和禾本科(Gramineae),生活型以一、二年生草本为主,占到70%以上;旱生和旱中生C4植物所占比例较大,达到48.89%,其区系成分以世界成分、亚洲中部成分和古地中海成分为主。C4植物分布特征表现出不同的规律性:在垂直地带分布上与温度呈正相关关系、与降雨呈负相关关系;在水平经度地带分布上主要与降水呈正相关关系,与温度无显著相关,尤其是在极端高温、干旱(主要是额济纳戈壁荒漠区)地区,C4植物的生存受到了限制。这一结果对于揭示阿拉善地区C4植物的水分利用效率,及其与降水资源的空间分布之间的关系提供了一定的理论解释。 相似文献
119.
荒漠植物红砂叶绿素荧光参数日变化及其与环境因子的关系 总被引:10,自引:3,他引:7
在自然条件下以分布于兰州九州台(LZJ)、张掖临泽(ZYL)和武威民勤(WWM)3个地区的红砂为试材,利用PAM-2100便携式叶绿素荧光分析仪和Lcpro+便携式光合作用测定系统,在红砂生长季节对其叶绿素荧光参数及其环境因子进行测定和分析。结果表明:3个地区红砂叶片的初始荧光(Fo)、PSⅡ最大光化学量子产量(Fv/Fm)、实际光化学反应量子效率(ΦPSⅡ)和非光化学淬灭系数(qN)均存在明显的日变化。其中Fv/Fm和ΦPSⅡ均呈反正态分布曲线日进程,在中午13:00强光下降低至最低值;Fo和qN则呈正态分布曲线日进程,在中午13:00达到最大值。3个地区红砂的Fv/Fm虽在中午呈降低趋势,但因其值均高于0.8,所以并未发生光抑制现象。在环境因子中,光合有效辐射(PAR)、温度(Ta)以及水分条件协同作用于红砂的光化学效率。当水分条件较高时,PAR成为影响光化学效率降低的首要因子;而当水分降低时,RH成为加速光化学效率下降的主要因子。在土壤极端干旱叠加强光、高温和低湿的逆境中红砂主要采取依赖于叶黄素循环的热耗散和PSⅡ反应中心可逆失活两种保护机制来适应外界环境的变化。 相似文献
120.
利用遥感和GIS空间信息分析技术,以长江源地区的4期遥感数据为主要信息源,将荒漠分为高寒荒漠、裸岩石砾地、戈壁、沙地、裸土地、盐碱地,通过目视解译提取了长江源区4期荒漠信息,在此基础上进行荒漠动态变化及驱动力分析。结果表明,长江源区荒漠分布范围较广,荒漠面积占源区总面积的28%左右,荒漠中以高寒荒漠、裸岩石砾地、戈壁、沙地为主,其次是裸土地和盐碱地。近30 a来的变化趋势是20世纪70年代中期到1990年荒漠化发展较快,荒漠面积增加了43 935.00 hm2,1990年到2000年荒漠面积减少了32 821.28 hm2,2000年到2005年荒漠面积增加了29 611.30 hm2。 相似文献