黄土高原地区生态建设的关键问题

从黄土高原地区水土保持生态建设的实际情况出发,结合历史经验教训,探讨了生态建设与农业发展、农民脱贫致富的关系.指出生态环境问题归根结底是人的问题,减少人类对生态环境的破坏和干扰,因地制宜地进行植被建设和生态恢复,激励广大农民自觉参与生态建设对黄土高原地区水土保持生态建设成败至关重要.     

Profile of Methane Concentrations in Soil and Atmosphere in Alpine Steppe Ecosystem on Tibetan Plateau

The methane concentration profile from -1.5m depth in soil to 32m height in air was measured in alpine steppe located in the permafrost area. Methane concentrations showed widely variations both in air and in soil during the study period. The mean concentrations in atmosphere were all higher than those in soil, and the highest methane concentration was found in air at the height of 16m with the lowest concentration occurring at the depth of 1.5m in soil. The variations of atmospheric methane concentrations did not show any clear pattern both temporally and spatially, although they exhibited a more steadystable state than those in soil. During the seasonal variations, the methane concentrations at different depths in soil were significantly correlated （R^2〉0.6） with each other comparing to the weak correlations （R^2〈0.2） between the atmospheric concentra- tions at different heights. Mean methane concentrations in soil significantly decreased with depth. This was the compositive influence of the decreasing production rates and the increasing methane oxidation rates, which was caused by the descent soil moisture with depth. Although the methane concentrations at all depths varied widely during the growing season, they showed very distinct temporal variations in the non-growing season. It was indicated from the literatures that methane oxidation rates were positively correlated with soil temperature. The higher methane concentrations in soil during the winter were determined by the lower methane oxidation rates with decreasing soil temperatures, whereas methane production rates had no reaction to the lower temperature. Relations between methane contribution and other environmental factors were not discussed in this paper for lacking of data, which impulse us to carry out further and more detailed studies in this unique area.     

Present status and changes of the phytoplankton community after invasion of Neosalanx taihuensis since 1982 in a deep oligotrophic plateau lake, Lake Fuxian in the subtropical China

Phytoplankton assemblages in the subtrophical oligotrophic Lake Fuxian, the second deepest lake in China, were investigated monthly from September 2002 to August 2003. A total of 113 species belonging to seven phyla were identified, among them, a filamentous green alga, Mougeotia sp., dominated almost throughout the study period and comprised most of the total phytoplankton biomass.Mougeotia sp. has made a substantial development during the past decades: it was absent in 1957, only occasionally present in 1983,increased substantially in 1993, and became predominant in 2002--2003. It is likely that natural invasion of the Taihu Lake noodlefish (Neosalanx taihuensis) has led to a change of dominant herbivorous zooplankton from small to large calanoid, which has increased grazing pressure on small edible algae, and thus has indirectly favored the development of the inedible filamentous Mougeotia sp.     

川西高原河流水体CDOM的光化学降解特性

川西高原部分河流溶解性有机碳(DOC)含量极高,因有色溶解性有机质(CDOM)具有独特的光学特性,其光降解特征与规律对于分析高寒区天然水体DOC动态及区域水-陆碳循环具有重要的环境意义.本文选取川西高原两种主要地貌类型的河流共5条,即高山峡谷区河流杂谷脑河、抚边河及岷江,丘状高原区河流白河、黑河,对河流水体CDOM三维荧光光谱(EEMs)与紫外-可见光吸收光谱(UV-Vis)采用平行因子分析(PARAFAC)与二维相关光谱(2D-COS)进行分析.结果表明:①白河和黑河CDOM的5 d降解率分别为64. 85%和63. 43%,光降解速率常数分别为0. 167 d-1和0. 173 d-1;抚边河CDOM浓度低(0. 71 m-1)光降解现象不明显,杂谷脑河和岷江CDOM光降解行为较为复杂;②在光降解过程中,除岷江外其余4条河流荧光溶解性有机质(FDOM)内源特征(FI)逐渐减弱,黑河和白河CDOM芳香性、疏水性特征(SUVA254和SUVA260)及腐殖化程度(HIXa)逐渐降低;③川西高原5条河流中FDOM组分均呈2类4个组分,即C1(275/310 nm,类酪氨酸)、C2 [280(250)/400 nm,UVA类腐殖质]和C3(255/440 nm,UVA类腐殖质)、C4[270(360)/492 nm,UVA类腐殖质],类腐殖质FDOM较易光降解;④5条河流中UVA类腐殖质FDOM(尤其是500 nm发射波段)光降解反应先于类酪氨酸物质;丘状高原河流中UVA类腐殖质FDOM对于光照的敏感度大于高山峡谷区河流;⑤白河的主成分分析中识别出了2个因子,解释了这些参数变化的87. 28%,反映了光降解过程对于CDOM特征、荧光组分等方面的影响.     

拉萨市近49年气温变化特征研究

2019年6月24日拉萨市出现了30.8℃的高温,创历史新高.为了更好的了解拉萨市气候变暖的机理以及评估该区域未来气候的变化状况,本文基于拉萨市自动气象站近49年的观测数据,采用线性趋势法、Mann-Kendall (M-K)突变检验、小波分析、R/S分析等方法深入研究了多时间尺度上气温的时空演变特征.结果 显示:(a...     

长江源区各拉丹冬峰雪冰中微粒季节变化及其环境意义

分析了长江源区各拉丹冬峰冰川区不同海拔采集的3个雪坑SP1、SP2和SP3样品中δ18O、不溶微粒数量浓度及主要离子浓度,以探讨本研究区域雪冰微粒含量变化及其来源.结果显示,不同粒径微粒含量变化趋势一致,3个雪坑中细微粒含量分别占总微粒的88%、78%、86%.中微粒分别占10%、19%、11%;不同粒径微粒数量浓度之间的相关系数均达0.9以上(置信度可达99%),具有良好的相关性.雪冰中不溶微粒浓度同Ca2 、Mg2 、SO2-4一样,具有明显的季节波动.非季风期微粒浓度要高于季风期2～4倍.3个雪坑非季风期微粒通量分别占一个年层雪冰中微粒总通量的73.6%、92.3%、97%,即初春季节沙尘暴对于各拉丹冬雪冰中微粒沉降贡献远大于夏.秋季节.结合NCAR/NCEP再分析资料.应用HYSPLIT-4模式模拟的不同季节5 d后向气团轨迹图表明,各拉丹冬峰冰川I区雪冰中不溶性微粒可能来源于中亚、南亚和青藏高原本身,其中影响最大的可能是青藏高原自身的沙尘源区,同时冰川区裸露基岩对雪冰中不溶微粒含量亦有贡献.     

青藏高原土壤柴油降解菌的筛选及降解实验研究

青藏高原北麓河地区土壤为典型的低温土壤环境,夏季高温季节表层土壤(5 cm处)温度仅为9℃,中层(20 cm处)为7.5℃,而40 cm处仅为4℃左右。土壤高温季节为7月中旬至9月上旬,而10月至来年6月土壤日平均温度下降为0℃以下。针对青藏高原低温土壤环境,在北麓河试验现场进行人工模拟柴油污染,16个月后采集污染土样,进行土著低温菌的复合筛选,柴油菌的筛选驯化温度为10℃。经过4次转接复合培养驯化后,菌液中微生物数量可达2.7×1012CFU/mL。筛选后的柴油降解菌90%以上为杆状菌,长度为2~3μm,少见球菌,其直径约为0.5μm。通过柴油摇瓶模拟降解实验,17 d后柴油去除率可达到62%。研究为青藏高原低温条件下的土壤柴油污染土著微生物修复提供了研究基础。     

低纬高原大气电场特征及其在预警中的应用

通过对2006年7月- 2007年6月云南地闪定位网探测资料和玉溪大气电场仪资料分析,研究了高原晴天大气电场和雷暴天气过程的电场演变特征.结果表明:高原晴天大气电场具有明显的日变化和月变化特征.低纬高原地区雷暴云具有偶极性和三极性两种结构,但大多数雷暴具有偶极性电荷结构,不同电荷结构的雷暴云的放电特征不同,偶极性时主要为负地闪,地闪活动较活跃;三极性时主要是正地闪,地闪活动较少.根据雷暴云近地面电场变化特征,探讨了大气电场仪预警地闪的方法,首次提出极性变化预警法,其命中率和提前预警时间都明显优于阈值预警法.     

云南高原典型林分林下枯落物持水特征研究

森林枯落物具有重要生态水文功能,通过实地调查与实验分析,对云南高原湖泊纳帕海流域3种典型林分枯落物储量、持水量和持水过程进行了研究。结果表明：高山松（pinus densata）林下枯落物储量最大,白桦林（Betula platyphylla Suk.）次之,川滇高山栎（Quercus aquifolioides）灌丛最小,林下枯落物储量最大持水量和有效拦蓄量大小排序表现出和枯落物储量相同的顺序;不论是储量、最大持水量还是有效拦蓄量,各林分枯落物都表现出半分层大于未分解层。3种林下枯落物在0～2 h内吸水较快,在10 h后吸水速明显减缓,用对数方程对3种林下枯落物未分解层和半分解层持水量与浸水时间进行拟合,用幂函数方程对吸水速率与浸水时间进行拟合,结果显示相关系数都较高。     

温度和氮素输入对青藏高原三种高寒草地土壤碳矿化的影响

选取了海北高寒草甸、那曲高寒草原和当雄高寒湿地3种典型高寒草地生态系统类型为研究对象,采集了表层0~10 cm土壤,在实验室内进行可控温度下的碳矿化培养实验。结果表明,青藏高原土壤碳矿化在不同高寒草地类型间存在显著差异（P≤0.05）。在较低的温度下,高寒湿地土壤的碳矿化速率显著低于高寒草甸土壤,而温度在15℃左右时,高寒湿地土的碳矿化速率略高于高寒草甸土壤,当温度处于较高的水平时（〉20℃）,高寒湿地土壤碳矿化速率远高于高寒草甸土壤,高寒湿地土壤碳矿化的Q10显著大于高寒草甸。无论是低温还是较高的温度,高寒草原土壤碳矿化速率最低,数值范围也最窄。高寒草甸和高寒湿地土壤碳矿化均受温度的显著影响（P≤0.05）,其速率均跟温度呈现一级指数函数方程关系,而高寒草原土壤碳矿化速率与温度间未呈现明显的函数关系,但不同温度间的土壤碳矿化速率存在显著差异。氮素输入对高寒草甸和高寒湿地土壤碳矿化的影响不明显,但显著促进了高寒草原土壤碳矿化作用。