四面山阔叶林土壤大孔隙特征与优先流的关系

为研究土壤大孔隙数量、分布特征与优先流发生之间的关系,在使用亮蓝染色法划分林地优先流发生区域基础上,利用穿透曲线理论方法,对重庆四面山典型亚热带阔叶林土壤剖面染色和未染色区域内的土壤大孔隙进行了量化分析.结果表明：研究林地土壤剖面内大孔隙半径多在0.3～3.0 mm,大孔隙率为6.3%～10.5%,随着土壤深度的增加,大孔隙呈现出聚集态的分布特征.各孔径范围内,染色区域的土壤大孔隙数量较未染色区域高出约1个数量级.半径＞0.3 mm,尤其是半径＞1.5 mm的大孔隙数量,是影响林地优先流发生的主要通道.森林土壤0.3～3.0 mm孔径范围内,大孔隙数量与其对应的土壤水分稳定出流速率呈显著的正相关关系,其中在0.7～1.5 mm和1.5～3.0 mm孔径范围内大孔隙数量与稳定出流速率相关程度最大,相关系数分别为0.842和0.879.发生优先流的染色区内大孔隙联通状况优于未染色区,两区中1.5～3.0 mm孔径范围内的联通大孔隙数量差异最大,相差78.3%.染色区内大孔隙数量随土壤深度的增加逐渐减少,“漏斗”状的孔隙分布特征可以形成有效的水压梯度,有利于水分优先运移.     

长白山北坡两种类型森林土壤的大孔隙特征

运用亮蓝溶液染色示踪法和图像分析技术,对长白山北坡棕色针叶林土和暗棕色森林土大孔隙特征及分布进行研究,探讨影响2种类型土壤大孔隙形成的因素．结果表明：由水平剖面染色面积随土层深度的变化情况,可间接得出大孔隙在垂直土壤剖面上的变化规律;随着土层深度的增加,2种土壤的染色面积均呈减少趋势;在24h内,棕色针叶林土较暗棕色森林土大孔隙流的运移深度多10～20cm,且其大孔隙流路径多,相同面积上,前者达6条,后者只有1条;大孔隙流的存在可以使水分在土壤中的运移速度增加2～3倍;生物因素是2种土壤大孔隙形成的主要因素,由土壤动物运动形成的大孔隙数量较多,直径多为2～4mm．     

荒漠绿洲湿地土壤优先流与水分入渗特征

地表水分、溶质和污染物以土壤优先流的形式下渗到深层土壤或地下水中,将导致土壤养分流失与地下水污染等问题。因此,土壤优先流研究将为干旱区荒漠绿洲湿地水分运移与盐分积累过程提供理论依据。以荒漠绿洲湿地为研究区,选取柽柳灌丛、盐碱草地和杨树林,以道路为对照,采用室外染色示踪法对湿地土壤优先流特征与水分入渗进行研究。结果表明:不同植被类型土壤优先流入渗深度存在显著差异,其柽柳灌丛和盐碱草地几乎是杨树林和道的2倍;染色面积比随深度的增加而波动下降,0—20 cm土层染色面积比占总染色面积的54.42%—89.27%;染色路径宽度以20—250 mm和250 mm为主;优先流类型以高相互作用混合流和非均质指流为主。在荒漠绿洲湿地,砾石促进土壤优先流发生,增加了侧向流;同时,粗根的减少抑制了优先流的发生;此外,土壤盐分通过影响土壤大孔隙分布而影响水分入渗过程。因此,荒漠绿洲湿地土壤优先流与水分入渗差异是土壤质地、根系分布与盐分离子共同作用的结果。     

六盘山典型植被下土壤大孔隙特征

利用水分穿透曲线法和Poiseuille方程研究了六盘山8种典型植被类型下土壤大孔隙的半径与密度特征.结果表明:研究区典型植被下土壤大孔隙半径在0.4~2.3 mm,加权平均半径为0.57~1.21 mm,平均值为0.89 mm;大孔隙密度变化范围为57~1117个.dm-2,平均408个.dm-2;半径>1.4 mm的大孔隙密度较小,其数量仅占大孔隙总数量的6.86%;大孔隙面积与土柱水分出流面积的百分比(简称土壤大孔隙面积比)介于0.76%~31.26%,平均为10.82%.研究区土壤大孔隙密度为阔叶林大于针叶林,亚高山草甸与阔叶林相当,灌丛与针叶林相当;土壤大孔隙面积比为阔叶林高于针叶林,灌丛与阔叶林相当,亚高山草甸与针叶林相当.     

三峡库区森林土壤大孔隙特征及对饱和导水率的影响

土壤大孔隙是土体内孔径较大能优先传导水分的根孔、洞穴或裂隙,大孔隙内优先流的产生是土壤水分运动研究由均衡走向非均衡的标志。利用原状土柱的水分穿透试验,对三峡库区山地不同林型覆盖下土壤的大孔隙结构进行了研究,分析了温性阔叶林棕壤、针阔混交林黄棕壤、暖性针叶林黄壤及弃耕草地剖面内大孔隙的剖面分布特征及其对土壤饱和导水率的影响。结果表明:研究区内森林土壤的大孔隙当量孔径在0.3—3 mm之间,占土壤总体积的0.15%—4.72%。大孔隙中孔径0.3—0.6 mm的大孔隙密度最大,占大孔隙总数量的72.2%—90.4%;而孔径1 mm的孔隙仅占大孔隙总数量的1.26%—8.55%。土壤大孔隙密度和大孔隙面积比的顺序为:温性阔叶林棕壤针阔混交林黄棕壤针叶林黄壤弃耕坡地。各孔径段的大孔隙密度在不同样点均呈现A层-B层-C层逐渐减小的趋势,大孔隙密度与有机质含量呈显著正相关关系。土壤饱和导水率与不同孔径大孔隙的密度、面积比均成显著正相关关系,孔径1mm的大孔隙仅占大孔隙总数量的1.26%—8.55%,但决定了饱和导水率84.7%的变异。此外,森林土壤饱和导水率与各土壤层的有机质含量成显著正相关关系,有机质的增多有利于改善土壤的入渗性能。     

土壤大孔隙流研究进展

介绍了大孔隙及大孔隙流的定义、多种表现形式及其重要特征、产生机理和室内外实验研究概况,以及染色示踪、切片、穿透曲线、张力入渗仪、X射线CT扫描摄像和雷达探测等方法的研究进展,揭示这些实验方法的优点与存在的问题.并指出由于影响大孔隙及大孔隙流的因素较复杂,应将大量的野外实验和室内实验相结合,同时改进观测方法, 提高模拟手段,不断完善大孔隙流理论,使大孔隙流研究迈上一个新台阶.     

土壤大孔隙及其研究方法

阐述了土壤大孔隙的定义、孔径划分类型及其成因,比较了各种研究方法的适用性和局限性,土壤大孔隙是可以提供优先水流路径的孔隙,其孔径大小为＞0.03mm。大孔隙形状具有多样性,既有形状不规则的袭隙和裂疑,也有近似圆柱状的管道。土壤动物对土壤的挖掘作用,植物根系在土壤中的穿插作用,冻融和干湿交替过程及化学过程是产生大孔隙的主要原因,大也民隙的研究方法分为直接观测法和间接描述法,并各有其适用性和局限性,土壤大孔隙研究的最终目的是调控它,为减少地下水污染、控制养分和水分的流失提供一条新途径。     

干湿交替对红河干旱河谷区土壤优先流形成特征的影响

为明确干旱河谷气候区干湿交替作用对土壤优先流形成的影响,本研究以红河干旱河谷区的荒草地为对象,通过模拟干湿交替的方法,基于染色示踪和水分穿透曲线试验并利用图像处理技术,对比分析模拟前后土壤优先流特征的差异性规律。结果表明: 模拟干湿交替条件下基质流发生区在0~10 cm土层,染色深度高达35 cm,其优先路径的水平宽度仅为3～10 cm,且染色面积曲线波动小。模拟干湿交替条件导致土壤稳定出流速率、大孔隙数量和大孔隙率明显增加,在0~20 cm土层,实施干湿交替后的土壤稳定出流速率较非干湿交替条件高约0.27 cm³·s^-1,染色区的大孔隙数量增加约1.4倍,大孔隙率则高13.4%。大孔隙数量与稳定出流速率呈极显著正相关,模拟干湿交替后大孔隙数量从大到小依次为: 0.6～0.8 mm＞0.8～1.0 mm＞1.0～1.5 mm＞1.5～2.0 mm＞2.0～3.7 mm,非干湿交替条件下为: 0.8～1.0 mm＞0.6～0.8 mm＞1.0～1.5 mm＞2.0～3.7 mm＞1.5～2.0 mm。各孔径范围的大孔隙数量与染色面积比呈极显著相关关系,经过模拟干湿交替处理后,其相关性增大,且影响优先流发生的主导因素由孔径1.5～2.0 mm的大孔隙数量变为孔径0.8～1.0 mm的大孔隙数量。干湿交替作用会通过影响大孔隙特征进而导致土壤更易发生优先流且程度增强。     

宁夏荒漠草原不同林龄人工柠条林地土壤优先流研究

土壤优先流作为土壤中常见的水分流动方式,会造成土壤水分流失、地下水污染及坡面土体稳定性降低等问题。以位于宁夏盐池县的典型荒漠草原为研究区域,通过土壤水分入渗染色法、CT扫描法、图像处理技术相结合的分析方式,选取人工营造9、14、24、35年的柠条灌丛林地,以空白草地作为对照,探究不同恢复年限人工柠条林土壤优先流特征及其与土壤大孔隙与根系的关系。结果表明：(1)不同林龄柠条林地土壤优先流特征及大孔隙度具有显著差异,表现为随着种植年份的增加,土壤大孔隙度逐渐升高,土壤入渗染色深度随之加深,同时染色面积比随着柠条林林龄的增加而增大。(2)土壤基质流深度表现为随着种植年份的增加而增大,人工柠条林地的土壤优先流程度显著高于草地。(3)随着人工柠条林龄的增加,土壤根系数量增加,而灌丛生长发育过程中的根系活动使得灌丛林地土壤具有更多迂曲度低、连通性强的大孔隙,这些大孔隙是导致土壤水分优先迁移的主要因素。因此,植物根系和土壤大孔隙变化是影响荒漠草原人工柠条恢复过程中土壤水分分布的关键因素,合理配置人工林以改善根系及土壤结构特征,或可有效提高荒漠草原地区的土壤水分利用效率。     

岷江上游森林土壤大孔隙特征及其对水分出流速率的影响

大孔隙是森林土壤中常见的现象 ,对土壤壤中流的产生有重要的影响。但由于大孔隙研究方法的不成熟 ,各种方法得到的大孔隙半径范围并不一致。一般认为田间持水量和饱和含水量之间的土壤孔隙为大孔隙 ,利用水分穿透曲线和 Poiseuille方程研究了岷江上游不同植被下土壤的大孔隙状况 ,这种方法一方面与传统的研究方法相衔接 ,另一方面所得到的大孔隙与土壤水分运动有关 ,反映了土壤大孔隙的研究目的 ,因而是一种相对合理的研究方法。岷江上游几种主要植被下土壤大孔隙半径主要集中于 0 .3～ 2 .4 mm之间 ,平均在 0 .4 8～ 1.17mm之间 ,均值为 0 .84 mm,均方差为 0 .2 2 6 ;且随着剖面的发育表现出上部土层多 ,下部土层少的特点。同时 ,半径在 2 .4～ 1.4 m m之间的特大孔隙较少 ,<1.0 m m的小孔隙较多。大孔隙的平均半径对于水分出流速率有重要的影响 ,特别是半径 >1.4 mm的孔隙数量影响最大 ,虽然其数量仅占大孔隙数量的 5 %以下 ,但决定了稳定出流速率 70 %的变异。大孔隙所占过水断面的最高比例为 2 1.2 2 % ,最低为 2 .6 % ;在大孔隙所占过水断面的比例小于 2 0 %的条件下 ,稳定出流速率随大孔隙的增多而增大     

稻田硒循环转化与水稻硒营养研究进展

稻田土壤氧化还原电位的交替变化和土壤组分的特殊性决定了硒在稻田环境中的循环转化机制明显有别于旱地土壤,并且影响到土壤硒的有效性及水稻对硒的吸收与积累.深入研究稻田土壤硒的循环转化及水稻硒营养吸收对实现土壤无机硒向有机硒的转化具有重要意义.本文对稻田土壤硒的循环机制及形态转化、水稻体内硒的代谢机制及吸收积累特性进行综述,分析硒在土壤 水稻系统中转化及向水稻体内迁移的研究现状与发展趋势,为土壤硒有效性研究及培育富硒营养稻米提供参考.     

连栽桉树人工林土壤大孔隙特征及其对饱和导水率的影响

速生人工林多代连栽容易导致土地水源涵养能力下降。土壤大孔隙以优先流的形式补充地下水,是定量研究土壤水分运动的重要指标。以连栽1-4代桉树人工纯林为研究对象（记录为Ⅰ、Ⅱ、Ⅲ、Ⅳ）,采用水分穿透曲线法,绘制水分穿透曲线,结合Poiseulle方程计算出大孔隙数量、半径及饱和导水率等指标,对土壤大孔隙特征及其对饱和导水率的影响进行研究。结果表明：（1）桉树人工林土壤的出流速率总体表现先匀速增加后趋于稳定,稳定出流速率总体表现为I > II > III > IV。（2）大孔隙半径范围在0.3-1.5 mm,主要集中于0.4-0.6 mm,随土层深度增加显著减小（P<0.05）。大孔隙数量范围在3.56×10⁴-4.81×10⁵个/m²。随着连栽代次的增加,大孔隙孔径范围变小,同一孔径范围的大孔隙数量减少。土壤容重与大孔隙特征呈极显著负相关关系;有机质含量与大孔隙特征呈极显著正相关关系。（3）各样地土壤饱和导水率范围在0.41-4.50 mm/min,并随着连栽代次增加而降低。将大孔隙的总数量、平均体积与土壤饱和导水率进行线性拟合,拟合方程为：y=ax+b=,（R²>0.66）。综上,随着桉树人工林连栽代次的增加,土壤大孔隙孔径范围缩小、同等半径的大孔隙数量减少,饱和导水率降低,土壤入渗及导水性能减弱,容易造成水土流失。     

Differentiation of soil properties related to the spatial association of wheat roots and soil macropores

Under certain soil conditions, e.g. hardsetting clay B-horizons of South-Eastern Australia, wheat plants do not perform as well as would be expected given measurements of bulk soil attributes. In such soils, measurement indicates that a large proportion (80%) of roots are preferentially located in the soil within 1 mm of macropores. This paper addresses the question of whether there are biological and soil chemical effects concomitant with this observed spatial relationship. The properties of soil manually dissected from the 1–3 mm wide region surrounding macropores, the macropore sheath, were compared to those that are measured in a conventional manner on the bulk soil. Field specimens of two different soil materials were dissected to examine biological differentiation. To ascertain whether the macropore sheath soil differs from rhizosphere soil, wheat was grown in structured and repacked cores under laboratory conditions. The macropore sheath soil contained more microbial biomass per unit mass than both the bulk soil and the rhizosphere. The bacterial population in the macropore sheath was able to utilise a wider range of carbon substrates and to a greater extent than the bacterial population in the corresponding bulk soil. These differences between the macropore sheath and bulk soil were almost non-existent in the repacked cores. Evidence for larger numbers of propagules of the broad host range fungus Pythium in the macropore sheath soil were also obtained. This revised version was published online in June 2006 with corrections to the Cover Date.     

PestLCI 2.0: a second generation model for estimating emissions of pesticides from arable land in LCA

Purpose

The spatial dependency of pesticide emissions to air, surface water and groundwater is illustrated and quantified using PestLCI 2.0, an updated and expanded version of PestLCI 1.0.

Methods

PestLCI is a model capable of estimating pesticide emissions to air, surface water and groundwater for use in life cycle inventory (LCI) modelling of field applications. After calculating the primary distribution of pesticides between crop and soil, specific modules calculate the pesticide??s fate, thus determining the pesticide emission pattern for the application. PestLCI 2.0 was developed to overcome the limitations of the first model version, replacement of fate calculation equations and introducing new modules for macropore flow and effects of tillage. The accompanying pesticide database was expanded, the meteorological and soil databases were extended to include a range of European climatic zones and soil profiles. Environmental emissions calculated by PestLCI 2.0 were compared to results from the risk assessment models SWASH (surface water emissions), FOCUSPEARL (groundwater via matrix leaching) and MACRO (groundwater including macropore flow, only one scenario available) to partially validate the updated model. A case study was carried out to demonstrate the spatial variation of pesticide emission patterns due to dependency on meteorological and soil conditions.

Results

Compared to PestLCI 1.0, PestLCI 2.0 calculated lower emissions to surface water and higher emissions to groundwater. Both changes were expected due to new pesticide fate calculation approaches and the inclusion of macropore flow. Differences between the SWASH and FOCUSPEARL and PestLCI 2.0 emission estimates were generally lower than 2 orders of magnitude, with PestLCI generally calculating lower emissions. This is attributed to the LCA approach to quantify average cases, contrasting with the worst-case risk assessment approach inherent to risk assessment. Compared to MACRO, the PestLCI 2.0 estimates for emissions to groundwater were higher, suggesting that PestLCI 2.0 estimates of fractions leached to groundwater may be slightly conservative as a consequence of the chosen macropore modelling approach. The case study showed that the distribution of pesticide emissions between environmental compartments strongly depends on local climate and soil characteristics.

Conclusions

PestLCI 2.0 is partly validated in this paper. Judging from the validation data and case study, PestLCI 2.0 is a pesticide emission model in acceptable accordance with both state-of-the-art pesticide risk assessment models. The case study underlines that the common pesticide emission estimation practice in LCI may lead to misestimating the toxicity impacts of pesticide use in LCA.     

Identification of the composite parameters of the BBH-B model specifying the effects of biohydrologic processes on the water balance of crop fields

A model of soil hydrology incorporating rainfall interception and macropore flow, which are representative biohydorologic processes, (BBH-B model) has two composite parameters, Π and Φ. These parameters express the ratios of rainfall interception and macropore flow to gross rainfall, respectively. Their values, however, change widely with the vegetation, soil texture and wetness. The results of experiments that have been carried out for various objectives under various conditions by the present authors were reanalyzed to evaluate these two parameters. Further, two supplemental experiments were designed to identify the two parameters. In the experiments, the monthly mean of Π for a cornfield ranged from 0.18 to 0.64 in the summer months, while Φ for a weed-grown field reached a maximum of 0.8 when daily rainfall was more than 40 mm day⁻¹. From these analyses and experiments, we concluded that the effects of biohydrologic processes on the water balance of crop fields are rather large and not negligible.     

全球气候变化对陆地植物碳氮磷生态化学计量学特征的影响

全球气候变化背景下生物地球化学循环的响应规律和陆地植物适应对策已受到广泛关注.本文在分析气候变暖和降水变化对不同生态系统植物C∶N∶P的影响、CO₂浓度升高对不同光合途径物种元素的影响,以及氮沉降对土壤 植物元素影响的短期和长期效应等基础上,从植物生理特性和土壤有效营养元素变化等方面揭示了其可能存在的内在机理,以期为研究C、N、P化学元素在土壤 植物之间传递与调节机制、陆地生态系统结构和功能,以及生物地球化学元素循环对气候变化的响应提供理论依据.最后提出了该领域研究中存在的问题及对今后研究的展望.