半干旱黄土高原沟垄微型集雨产流特征与马铃薯种植技术

对膜垄和土垄的降雨量和径流量进行直线回归分析,结果表明,粘土夯实集雨垄临界产流降雨量为2.83 mm,产流后的平均集水效率为24.6%,地膜覆盖集雨垄临界产流降雨量为0.23 mm,产流后的平均集水效率为91.1%。在沟垄微型集雨种植马铃薯试验中,30 cm垄宽膜垄、45 cm垄宽膜垄、60 cm垄宽膜垄、30 cm垄宽土垄、45 cm垄宽土垄和60 cm垄宽土垄(沟宽均为60 cm)的经济产量分别比传统耕作高173%、168%、119%、28%、24%和18%,水分利用效率分别比传统耕作高3.98、3.74、2.25、1.10、0.93和0.72 kg.mm-1.hm-2。膜垄种植马铃薯经济产量提高119%~173%,土垄种植马铃薯经济产量提高18%~28%。     

城市不同下垫面的降雨径流污染

当点源污染被有效控制后,面源污染成为城市水质恶化的主要原因之一。屋面和路面等不透水面以及绿地是城市的3种主要下垫面形式。当暴雨产生时,各种下垫面特别是屋面和路面上汇聚大量污染物质产生径流,对城市生态环境造成严重的污染。以文教区为例,对屋面、路面、草坪的径流水质进行了监测,指标包括pH、悬浮固体(SS)、化学需氧量(COD)、总氮(TN)、总磷(TP)和生化需氧量(BOD5)等。比较分析发现,3种下垫面类型的径流水质均较差,COD、TN、TP、BOD5平均浓度超过地表水环境质量Ⅴ级标准。COD、TN和TP浓度与SS含量之间相关性较好,相关系数可达0.85以上。径流中污染物浓度受多个因素的影响,其中降雨量和降雨强度是两个重要因素,雨强越大,雨水对城市下垫面的冲刷就越强;在相同的污染物累积量条件下,降雨量越大,径流中污染物浓度越低。     

太湖典型菜地土壤氮磷向水体径流输出与生态草带拦截控制

农业面源氮磷输出是导致太湖流域地表水富营养化主要原因之一,查明该地区农田土壤地表径流氮磷向水体迁移形态与通量,并实施径流控制,对水体富营养化治理具有重要现实意义。蔬菜地是太湖流域重要的农业种植方式。通过设置野外径流小区,观测了春夏季蔬菜地土壤氮磷径流输出,并探讨了生态拦截草带对径流中不同形态氮磷拦截效果。结果表明,2004年10月25日至2005年8月17日,菜地土壤氮磷径流输出总量分别为3 010.9和695.0 g.hm-2;其中颗粒态为主,分别占64%和75%。可溶态氮中,NH4 -N为主,占50%,可溶态磷中H2PO4-为主,占87%。生态拦截草带对径流氮和磷拦截效率分别为42%~91%,30%~92%。生态草带对颗粒态氮磷拦截效率大于可溶态。拦截草带可有效地控制蔬菜地土壤氮、磷通过径流向水体迁移。     

利用人工湿地去除农业径流中农药的研究进展

人工湿地对农业径流污染物去除效果显著,已成为控制农业径流污染的有效措施.本文结合国内外研究,介绍了当前水体农药污染的现状;从物理、化学及生物角度阐述了人工湿地对农药的去除机理和关键过程;归纳总结了人工湿地对农药的去除效率,指出人工湿地对农药的去除效率随农药类型的不同而差异较大:农药的平均去除率,按农药用途分为杀虫剂＞杀菌剂＞除草剂,按农药化学结构分为拟除虫菊酯类>有机磷类>三唑类＞酰胺类＞三嗪类＞脲类;综合考虑,潜流人工湿地在农药去除方面的效果优于表面流人工湿地.在此基础上分析了农药理化性质、人工湿地工艺类型及运行参数、进水中农药浓度、湿地植物等因素对农药在人工湿地中去除的影响.最后指出了当前研究中存在的问题,并提出了研究展望.     

Emergence chronology of brook charr,Salvenus fontinalis,alevins in an acidic stream

Synopsis The emergence chronology of brook charr alevins in the Chikanishing River, Ontario, Canada and the concurrent changes in stream chemistry resulting from acidic snowmelt runoff were examined during the spring, 1986–1988. Emergence patterns were similar among years with the most intense emergence (> 70%) occurring during the declining stream discharge following the spring flood. This period coincided with stream pH depressions (minimum pH 5.2) in 2 of 3 years, suggesting emergence behaviour frequently subjects the earliest free-swimming life interval of brook charr to episodic acidification events.     

Effects of afforestation on water yield: a global synthesis with implications for policy

Carbon sequestration programs, including afforestation and reforestation, are gaining attention globally and will alter many ecosystem processes, including water yield. Some previous analyses have addressed deforestation and water yield, while the effects of afforestation on water yield have been considered for some regions. However, to our knowledge no systematic global analysis of the effects of afforestation on water yield has been undertaken. To assess and predict these effects globally, we analyzed 26 catchment data sets with 504 observations, including annual runoff and low flow. We examined changes in the context of several variables, including original vegetation type, plantation species, plantation age, and mean annual precipitation (MAP). All of these variables should be useful for understanding and modeling the effects of afforestation on water yield. We found that annual runoff was reduced on average by 44% (±3%) and 31% (±2%) when grasslands and shrublands were afforested, respectively. Eucalypts had a larger impact than other tree species in afforested grasslands (P=0.002), reducing runoff (90) by 75% (±10%), compared with a 40% (±3%) average decrease with pines. Runoff losses increased significantly with plantation age for at least 20 years after planting, whether expressed as absolute changes (mm) or as a proportion of predicted runoff (%) (P<0.001). For grasslands, absolute reductions in annual runoff were greatest at wetter sites, but proportional reductions were significantly larger in drier sites (P<0.01 and P<0.001, respectively). Afforestation effects on low flow were similar to those on total annual flow, but proportional reductions were even larger for low flow (P<0.001). These results clearly demonstrate that reductions in runoff can be expected following afforestation of grasslands and shrublands and may be most severe in drier regions. Our results suggest that, in a region where natural runoff is less than 10% of MAP, afforestation should result in a complete loss of runoff; where natural runoff is 30% of precipitation, it will likely be cut by half or more when trees are planted. The possibility that afforestation could cause or intensify water shortages in many locations is a tradeoff that should be explicitly addressed in carbon sequestration programs.     

Sources and flowpaths of dissolved organic carbon during storms in two forested watersheds of the Precambrian Shield

Dissolved organic carbon (DOC) concentrations and export were studied in two small catchments in central Ontario to examine DOC sources and to assess the hypothesis that organic matter adjacent to the stream is a significant contributor of DOC during storms. Different DOC dynamics and exports were observed according to the depth of the riparian water table. In Harp 4-21, riparian flowpaths were predominantly through A and upper B soil horizons and riparian soils contributed between 73 and 84% of the stream DOC export during an autumn storm. In Harp 3A, riparian flowpaths were predominantly through lower B horizons. Consequently, riparian soils were less important and hillslopes contributed more than 50% of the stream DOC export in subcatchments without wetlands during storms. Wetlands and adjacent soils contributed significantly to DOC export in Harp 3A; 8% of the total catchment area exported 32 to 46% of the storm runoff DOC. DOC export dynamics in wetlands and riparian soils were distinctly different. In wetlands, transport was affected by leaching and flushing of DOC at the wetland surface leading to lower DOC concentrations with successive storms. In riparian soils, groundwater flowpaths were more important and stronger positive relationships between discharge and DOC concentration were observed. Precipitation, throughfall and stemflow were minor sources of stream DOC during storms and contributed less than 20% of the total export.     

Peat accretion and phosphorus accumulation along a eutrophication gradient in the northern Everglades

Recent rates of peat accretion (as determined by¹³⁷Cs) and N, P, organic C, Ca and Na accumulation were measured along a 10 km eutrophication gradient in the northern Everglades area of Water Conservation Area 2A (WCA 2A) that has received agricultural drainage from the Hillsboro canal for the past 25–30 yrs. Rates of peat accretion were highest at sampling locations closest to the Hillsboro canal, 1.6 km downstream, (5.67 ± 0.50 mm/yr) and decreased to 2.01 ± 0.31 mm/yr at distances of 7.1 to 10.7 km downstream. Phosphorus and Na accumulation were a function of both peat accretion and soil P and Na concentrations. The concentration and accumulation of P in peat deposited in the past 26 years was highest near the Hillsboro canal (1478 ± 67 ug/g, 0.66 ± 0.06 g/m²/yr) and decreased to 560 ± 20 ug/g and 0.10 ± 0.02 g/m²/yr at distances of 8.8 to 10.7 km downstream. Like phosphorus, the concentration and rate of Na accumulation was highest near the Hillsboro canal (3205 ± 1021 ug/g, 1.48 ± 0.53 g/m²/yr). Although sodium enrichment of the peat was limited to 1.6 km downstream of the Hillsboro canal, increased rates of Na accumulation penetrated 5.2 km downstream of the Hillsboro canal, the extent of the area of enhanced peat accretion. In contrast to P and Na, there was no difference in the concentration of soil organic C, N and Ca along the eutrophication gradient. However, there was a gradient of organic C, N and Ca accumulation corresponding to the area of enhanced peat accretion. The highest rates occurred 1.6 km south of the Hillsboro canal (212 ± 5 g organic C/m²/yr, 14.1 ± 0.4 g N/m²/yr, 22.1 ± 5.2 g Ca/m²/yr). Accumulation of organic C, N and Ca at distances of 7.1–10.7 km downstream averaged 87 ± 11, 6.3 ± 0.7 and 6.5 ± 0.9 g/m²/yr, respectively. The areal extent of enhanced peat accretion and organic C, N, Ca and Na accumulation encompasses approximately 7700 ha of the northern part of WCA 2A. The area of enhanced P accumulation is larger, covering 11,500 ha or 26% of the total area of WCA 2A. The 11,500 ha area has functioned as a sink for P for the past 25–30 yr removing 74% (49.3 MT/yr) of the 67 MT/yr that enters via agricultural drainage and rainfall. Moreover, P accumulation along the gradient was related to mean (1989–1990) surface water P concentration, decreasing as surface water P decreases. These findings suggest that P accumulation is dependent on the P concentration in the water column and that decreasing P loadings per unit area result in less P storage per unit area. The potential longterm equilibrium of the 11,500 ha area as a sink for P is based on a mean annual loading of 67 metric tons P/yr. Input rates exceeding this loading rate could result in an expansion of the 11,500 ha area until a new equilibrium size is reached.     

Transport and retention of matter in riparian ecotones

The stream ecosystem is described as a three-layered system, vertically as well as horizontally. The land/stream ecotone is defined as the area where lotic and edaphic characters overlap at the time of observation. The study site — Oberer Seebach, near the Biological Station Lunz — and the methods employed are described. Only a surprisingly small fraction (less than 10 %) of total imports is transported across the surface ecotones. The driving variables determining bank runoff and aerial drift are described and discussed. The importance of channel areas which are periodically flooded is stressed.Dedicated to Professor Agnes Ruttner-Kolisko on the occasion of her 80th birthday.Dedicated to Professor Agnes Ruttner-Kolisko on the occasion of her 80th birthday.     

应用SWAT模型研究潮河流域土地利用和气候变化对径流的影响

为定量分析潮河流域土地利用和气候变化对流域径流变化的影响,应用SWAT模型对流域上游至下游的大阁、戴营和下会3个水文站径流进行模拟,采用情景法分析径流对土地利用和气候变化的响应。在模型校准期和验证期采用两个参数:p因子和r因子来评价模拟的拟合度及不确定性。结果表明,3个水文站在校准期和验证期的p因子值分别为:0.70和0.77,0.87和0.82,0.92和0.78,r因子值分别为0.63和0.90,0.97和0.79,0.88和0.92,评价整个流域模拟有效性的模型目标函数g最佳值为0.66,说明该模型对潮河流域的产水量模拟具有很好的适用性。以1981—1990年为基准期,1991—2000年流域土地利用变化造成年径流量减少了4.10 mm,而气候变化导致年径流增加了29.68 mm;2001—2009年土地利用变化造成年径流量减少2.98mm,气候变化造成年径流量减少了14.30 mm。与1999年土地利用条件模拟径流值相比,几种极端情景法模拟分析结果表明:灌木林地情景下年径流增加了158.2%,草地情景下年径流增加了4.1%,林地和耕地情景下年径流分别减少23.7%和41.7%;不同气候变异情景模拟结果显示,径流对降水的变化敏感性高于对温度变化的敏感性,降水每增加10%,径流平均增加23.9%。温度每增加12%,径流平均减少6%。因此,在气候变化背景下,优化土地利用结构与方式是实现流域水资源科学管理的途径之一。