石灰岩退化生态系统不同恢复阶段土壤酶活性研究

研究了石灰岩退化生态系统不同恢复阶段的土壤酶活性.结果表明,石灰岩退化生态系统土壤酶活性在土壤剖面上无明显的递减规律;随着演替进展,土壤酶活性增强,土壤酶活性随植被特征、土壤类型以及酶本身的性质不同而表现各异.整体上石灰岩各阶段土壤酶活性:灌木林>柏木乔林>草本,同一植被类型下石灰岩柏木林>紫色砂岩柏木林.石灰岩退化生态系统土壤酶活之间以及酶活与pH值之间无显著相关性,而含水率和土壤全氮则与土壤酶活性呈显著或极显著相关,说明水分以及养分是石灰岩地区生态恢复的关键性因子.不同类型的土壤酶在同一植被土壤系统中酶活性表现不一,同一种酶在同一土壤类型而不同的生态恢复阶段酶活性表现不一,同一植被类型下的不同土壤类型中酶活性也有分异.     

宁夏东部荒漠草原向灌丛地人为转变过程中土壤胞外酶活性响应

以宁夏东部荒漠草原-灌丛地典型镶嵌体内部荒漠草地、草地边缘、灌丛边缘、灌丛地为对象,对各样地植丛和空斑下土壤特性及6种土壤胞外酶活性(纤维二糖水解酶、β-1,4-木糖苷酶、β-1,4葡萄糖苷酶、β-1,4-乙酰基氨基葡萄糖苷酶、亮氨酸氨基肽酶和碱性磷酸酶)进行分析,研究荒漠草原向灌丛地人为转变过程中胞外酶的响应特征。结果表明: 荒漠草原向灌丛地转变过程中,土壤水分、有机碳、全氮、全磷、微生物生物量碳、微生物生物量氮均显著降低,且灌丛地显著低于草地26.0%～88.5%;除草地边缘土壤水分、有机碳空斑略高于植丛外,其他指标均表现为各样地植丛显著高于空斑3.9%～82.3%。6类土壤胞外酶活性在转变过程中均呈下降趋势,降幅为22.1%～82.4%,其中亮氨酸氨基肽酶和碱性磷酸酶降低最为显著,分别降低82.4%和75.5%;除灌丛地β-1,4-乙酰基氨基葡萄糖苷酶在空斑显著高于植丛外,其他胞外酶活性均表现为各样地植丛高于空斑10.7%～42.7%;转变过程中6类胞外酶活性之间呈显著正相关,且均与土壤特性呈不同程度正相关,其中各类土壤胞外酶活性对土壤微生物生物量碳、氮及全氮响应较为积极。     

黄土高原纸坊沟流域不同植物对土壤微生物生物量和土壤酶活性的影响

为了解不同植被类型对土壤微生物生物量和土壤酶活性的影响,以黄土高原纸坊沟流域的9种植物为研究对象,选取撂荒地为参照,分析了各类植被植物根际土土壤微生物生物量、土壤酶活性及其与土壤理化因子的相关性.结果显示:(1)与撂荒地相比,经过植被恢复后,乔木和灌木植被下土壤肥力、微生物生物量和土壤酶活性均有所提高,而草本植被下土壤的碱解氮含量、微生物生物量磷、脲酶活性和过氧化氢酶活性却有所降低.(2)不同植被类型土壤微生物生物量碳和氮、蔗糖酶和碱性磷酸酶活性符合灌木＞乔木＞草本的规律;土壤微生物生物量磷、脲酶和过氧化氢酶活性符合乔木＞灌木＞草本的规律.(3)土壤微生物生物量碳、氮、磷与土壤有机质、全氮及全磷含量呈极显著正相关;4种土壤酶活性与土壤有机质、全氮及碱解氮含量呈极显著正相关.研究表明,黄土高原纸坊沟流域土壤微生物生物量和土壤酶活性受植被类型及土壤养分等因素的共同影响,且人工灌木植被对土壤的恢复作用高于乔木和草本植被.     

五大连池新期火山熔岩台地不同植被类型土壤微生物群落的功能多样性

土壤微生物群落是陆地生态系统的重要生物活性成分,其结构和功能多样性直接影响到系统的碳、氮等生态过程,微生物群落功能多样性与地上植被类型变化密切相关,开展植被类型对土壤微生物群落功能多样性的影响研究具有重要意义。以五大连池新期火山熔岩台地苔藓、草本、灌丛、矮曲林、针阔混交林5种典型植被类型为对象,利用BIOLOG微孔板法研究不同演替阶段植被类型土壤微生物群落功能多样性特征。结果表明：不同植被类型土壤微生物群落功能多样性存在显著差异。平均颜色变化率（AWCD）随培养时间延长而逐渐增加,大小顺序为：苔藓 > 针阔混交林 > 矮曲林 > 草本 > 灌丛。灌丛土壤微生物多样性指数与其他植被类型间差异显著。主成分分析结果表明,主成分1和主成分2分别能解释变量方差的56.24%和29.59%,不同植被类型下土壤微生物的碳源利用格局差异主要是由氨基酸类和带磷基糖类引起,二者合计解释总变异量的47.51%。冗余分析表明,速效磷、铵态氮、C：N和pH对微生物功能多样性具有显著的影响,羧酸类、氨基酸类、酯类和胺类的降解更易受到环境因素的影响。研究结果为进一步探讨植被类型与土壤微生物之间在植被演替过程中的关系提供参考。     

高寒草甸退化对祁连山土壤微生物生物量和氮矿化速率的影响

为深入了解高寒草甸退化对草原生态系统中土壤微生物碳氮量、土壤氮矿化及土壤微生物相关酶的变化特征,以祁连山东缘4个不同退化程度(未退化、轻度退化、中度退化和极度退化)的高寒草甸为研究对象,采集了深度为0—10 cm的土壤样品,并对不同退化程度高寒草甸中植物因子、土壤理化性质、土壤氨化速率、土壤硝化速率、土壤净氮矿化速率以及转化氮素的相关酶和微生物进行了相关研究。结果表明:(1)随退化程度的加剧,高寒草甸土壤中氨化速率和净氮矿化速率逐渐降低,硝化速率逐渐升高;(2)高寒草甸的退化降低了有关氮素转化相关酶,如土壤蛋白酶、脲酶、亮氨酸氨基肽酶的活性,而β-乙酰葡糖胺糖苷酶的活性呈先下降后上升趋势,且在极度退化草地活性最高;(3)随退化程度的加剧,高寒草甸土壤中微生物生物量碳和氮的含量逐渐降低,同时土壤基础呼吸、土壤微生物熵和代谢熵的指数也呈下降趋势。RDA分析表明,高寒草甸中氨化速率和净氮矿化速率与微生物生物量碳、微生物生物量氮、土壤基础呼吸、植物高度、植被盖度、地上生物量、蛋白酶、脲酶以及亮氨酸氨基肽酶呈显著正相关,而硝化速率则表现为负相关性。因此,高寒草甸退化对土壤微生物特性以及氮素转化和循环具有重要影响。     

贺兰山不同海拔土壤酶活性及其化学计量特征

探讨干旱区脆弱山地森林生态系统土壤酶活性及其化学计量比沿海拔的变化特征及影响机制,对研究脆弱生态系统养分循环具有重要意义。本研究以贺兰山不同海拔(1380～2438 m)土壤为对象,分析土壤理化性质、土壤酶活性及酶化学计量比沿海拔的变化及其影响因素。结果表明: β-葡萄糖苷酶(βG)、β-N-乙酰氨基葡萄糖苷酶(NAG)、土壤C/N和土壤C/P酶活性比值均随海拔升高表现出先增后减的变化趋势,在海拔2139 m处均处于较高水平;碱性磷酸酶(AKP)活性随海拔的升高整体上呈递增的趋势,在海拔2438 m处最高;亮氨酸氨基肽酶(LAP)活性和土壤N/P酶活性比值随海拔升高变化趋势不显著。通过对比全球土壤酶化学计量值发现,贺兰山存在一定程度的N限制。除LAP外,其余3种酶活性均与土壤有机碳/全氮、土壤有机碳/全磷和全氮/全磷呈极显著正相关,与土壤pH值呈极显著负相关;LAP、土壤C/P和土壤N/P酶活性比值均与全磷呈极显著负相关。此外,AKP与土壤容重呈极显著负相关。     

漓江水陆交错带土壤理化性质及其分布特征

水陆交错带是水生生态系统与陆地生态系统之间的过渡带,是一种典型的生态交错区,承载着能量流动、物质循环和信息交换的重要作用。土壤作为水陆交错带系统的重要组成部分,是水陆交错带功能实现的基础之一。鉴于此,以桂林漓江水陆交错带纵向梯度(上游、中游、下游)不同植被覆盖条件下的土壤为研究对象,采用野外取样调查、实验分析与统计检验相结合,系统的分析了土壤理化性质及其分布特征,旨在为该区域退化生态系统恢复与重建提供依据。结果表明:11个土壤理化性质,其中5个指标(土壤含水量、全氮、全磷、速效氮和速效钾)在上游、中游和下游均差异性显著。不同梯度下的土壤理化性质的相关性及相关性大小也不尽相同,但在总体上存在一些较相似的变化规律,如上游、中游和下游的土壤容重和孔隙度均呈现显著负相关,土壤全磷和有机质与多数土壤化学性质呈显著正相关;土壤含水量在下游与多数土壤化学性质均显著相关,但在上游仅与土壤全磷显著负相关。PCA主成分分析表明,土壤容重、土壤孔隙度和土壤全磷含量的贡献均大于其他环境因子的平均贡献率,体现了它们是影响漓江水陆交错带土壤理化性质的重要环境因子。     

青藏高原高寒草甸不同海拔土壤酶化学计量特征

土壤酶在生态系统物质循环和能量流动中起着关键作用,研究土壤酶活性对于探讨生态系统功能有着重要意义.采用Biolog微平板技术,研究不同海拔(4300～5100 m)土壤酶活性和酶计量比的变化特征及影响机制.结果表明:与C循环密切相关的β-1,4-葡萄糖苷酶(βG)、与N循环密切相关的β-1,4-N-乙酰氨基葡萄糖苷酶(NAG)、L-亮氨酸氨基肽酶(LAP)以及与P循环密切相关的酸性磷酸酶(AP)活性均随海拔升高呈现先上升后下降的单峰变化趋势,整体表现出4800 m>4950 m>4400 m>4650 m>5100 m>4300 m;土壤N∶P酶活性比呈现与土壤酶活性相同的先上升后下降单峰变化趋势,在4950 m处达到最高值;而土壤C∶N和C∶P酶活性比表现出沿海拔升高逐渐增加的趋势.有机碳(SOC)、土壤全氮(TN)、土壤含水量与4种酶活性均呈显著正相关;年均温度与NAG、AP呈显著正相关;年降水量与NAG、AP呈显著负相关;土壤C∶P酶活性比、土壤N∶P酶活性比与年均温度、年降水量、植被Shannon多样性指数、植被丰富度指数、植被盖度和TN呈显著正相关.年均温、年降水量、植被丰富度、植被覆盖度、土壤全氮和溶解性有机碳显著影响土壤C∶N酶活性比.青藏高原草甸不同海拔土壤酶活性和酶计量比呈现显著的海拔差异,且高海拔地区存在一定的N限制.土壤酶活性海拔差异主要受到土壤含水量、TN、SOC、年降水量和年均温度的影响.     

生物炭施用对桂北桉树人工林土壤酶活性的影响

为探究土壤酶活性对生物炭输入的响应特征，以及为合理应用桉树枝条生物炭提供理论参考，该研究基于桂北桉树人工林田间试验，以桉树人工林采伐剩余物枝条为原料，在500℃条件下厌氧制备生物炭，施用质量分数分别为0(CK)、0.5%(T1)、1%(T2)、2%(T3)、4%(T4)和6%(T5)的桉树枝条生物炭，输入1 a后，分析了不同处理下土壤酶活性的变化特征。结果表明：(1)沿着土层垂直深度，土壤酶含量减小。(2)各土层脲酶、过氧化氢酶、β-葡萄糖苷酶和脱氢酶的含量随生物炭施用量的增加而增大，在生物炭施用量为6%时含量最高。(3)酸性磷酸酶、蔗糖酶、亮氨酸氨基肽酶和纤维二糖苷酶的含量随着生物炭施用量的增加呈现先增加后减少的趋势，其中酸性磷酸酶和亮氨酸氨基肽酶在生物炭施用量为2%时含量最高，蔗糖酶和纤维二糖苷酶则在生物炭施用量4%时含量最高。总体上，桉树枝条生物炭施用不同程度地提高了桉树人工林的土壤酶活性。该研究结果可为林业废弃物制备生物炭资源化利用途径及其在桉树人工林的应用提供科学依据。     

海拔对高山峡谷区土壤微生物生物量和酶活性的影响

为了解土壤微生物生物量和酶活性随海拔的变化特征,以川西海拔1563 m到3994 m的高山峡谷区的干旱河谷、干旱河谷-山地森林交错带、亚高山针叶林、高山森林和高山草甸土壤为研究对象,采用原位培养法研究了5种不同海拔生态系统中有机层(0～15 cm)和矿质层(15～30 cm)土壤微生物生物量碳氮、土壤蔗糖酶、脲酶及酸性磷酸酶活性的变化.结果表明:有机层土壤中微生物生物量碳氮和3种土壤酶活性呈现出先增加后减少再增加的变化特征,从2158 m开始不断增加,到3028 m左右达到峰值后减少,在3593 m出现最小值后,逆势增加直到3994 m后再次减少;矿质层土壤的微生物生物量碳氮和3种土壤酶活性表现为亚高山针叶林(3028 m)>高山草甸(3994 m)>干旱河谷-山地森林交错带(2158 m)>高山森林(3593 m)>干旱河谷(1563 m).各海拔梯度土壤有机层的微生物生物量和酶活性显著高于矿质层.高山峡谷区土壤微生物生物量与土壤酶活性呈极显著正相关.土壤微生物生物量和土壤酶与土壤含水量、有机碳和全氮呈极显著正相关,土壤蔗糖酶与土壤全磷含量呈极显著正相关,土壤酸性磷酸酶与土壤全磷和土壤温度呈极显著正相关.可见,高山峡谷区海拔变化引起的植被和其他环境因子的变化显著影响了土壤生化特性.     

Exoenzyme activities as indicators of dissolved organic matter composition in the hyporheic zone of a floodplain river

1. We measured the hyporheic microbial exoenzyme activities in a floodplain river to determine whether dissolved organic matter (DOM) bioavailability varied with overlying riparian vegetation patch structure or position along flowpaths. 2. Particulate organic matter (POM), dissolved organic carbon (DOC), dissolved oxygen (DO), electrical conductivity and temperature were sampled from wells in a riparian terrace on the Queets River, Washington, U.S.A. on 25 March, 15 May, 20 July and 09 October 1999. Dissolved nitrate, ammonium and soluble reactive phosphorus were also collected on 20 July and 09 October 1999. Wells were characterised by their associated overlying vegetation: bare cobble/young alder, mid‐aged alder (8–20 years) and old alder/old‐growth conifer (25 to >100 years). POM was analysed for the ash‐free dry mass and the activities of eight exoenzymes (α‐glucosidase, β‐glucosidase, β ‐N‐acetylglucosaminidase, xylosidase, phosphatase, leucine aminopeptidase, esterase and endopeptidase) using fluorogenic substrates. 3. Exoenzyme activities in the Queets River hyporheic zone indicated the presence of an active microbial community metabolising a diverse array of organic molecules. Individual exoenzyme activity (mean ± standard error) ranged from 0.507 ± 0.1547 to 22.8 ± 5.69 μmol MUF (g AFDM)^?1 h^?1, was highly variable among wells and varied seasonally, with the lowest rates occurring in March. Exoenzyme activities were weakly correlated with DO, DOC and inorganic nutrient concentrations. 4. Ratios of leucine aminopeptidase : β‐glucosidase were low in March, May and October and high in July, potentially indicating a switch from polysaccharides to proteins as the dominant component of microbial metabolism. 5. Principal components analysis indicated that there were patch effects and that these effects were strongest in the summer. 6. DOM degradation patterns did not change systematically along hyporheic flowpaths but varied with overlying forest patch type in the Queets River hyporheic zone, suggesting that additional carbon inputs exist. We hypothesise that the most likely input is the downward movement of DOM from overlying riparian soils. Understanding this movement of DOM from soils to subsurface water is essential for understanding both the hyporheic metabolism and the carbon budget of streams and rivers.     

黄土高原不同植被带土壤团聚体有机碳和酶活性的粒径分布特征

为探究土壤中各粒级团聚体不同形态有机碳和酶活性的分布特征,以黄土高原延河流域森林带、森林草原带、草原带土壤为对象,研究了不同粒级团聚体总有机碳、易氧化碳和腐殖质碳含量,以及纤维素酶、β-D葡糖苷酶、过氧化物酶、蔗糖酶和脲酶活性,分析了土壤团聚体有机碳及其组分与酶活性之间的相关关系.结果表明： 3种植被带土壤团聚体有机碳及其组分含量表现为森林带＞草原带＞森林草原带,3种形态有机碳含量在0.25～2 mm粒径均最高;不同植被带土壤团聚体有机碳及其组分含量和酶活性在0～10 cm土层大于10～20 cm土层;3种植被带纤维素酶、β-D葡糖苷酶、蔗糖酶和脲酶活性表现为森林带＞草原带＞森林草原带,过氧化物酶活性表现为森林带＞森林草原带＞草原带;3种植被带土壤中各种酶活性随着粒径的减小呈递增趋势.土壤纤维素酶、过氧化物酶、蔗糖酶和脲酶活性与团聚体各种形态碳含量均呈显著正相关.
     

The relative importance of invertebrate and microbial decomposition in a rainforest restoration project

Tropical rainforests are increasingly disturbed by human activities. While restoration projects often succeed in replacing tree cover, they rarely manage to restore soil function. Consequently, there is an urgent need to understand the changes that occur during soil restoration. Model ecosystems such as the Eden Project present an ideal opportunity to investigate these changes. The Eden Project was built 15 years ago, and its plants grown from seedlings, or sown directly into a soil made up of standardized mixtures of recycled organic material. Today, the Eden Project's rainforest biome consists of a diverse community of plants, invertebrates, and microorganisms. Different areas within the biome are managed differently, allowing us to separate the relative contributions of decomposers under differing physical conditions. Litterbag experiments revealed significant differences in decomposition rates in bags of different mesh sizes. Phospholipid fatty acid analysis revealed that microbial biomass and community structure varied under different management regimes. Soil enzyme assays revealed that glucosidase activity increased in soils with more organic matter, whereas phenol oxidase activity increased in more alkaline soils. Our study takes a step toward understanding the interactions between invertebrates and microbes, and the way in which soils function during restoration.     

Seasonal variation in enzyme activities and temperature sensitivities in Arctic tundra soils

Arctic soils contain large amounts of organic matter due to very slow rates of detritus decomposition. The first step in decomposition results from the activity of extracellular enzymes produced by soil microbes. We hypothesized that potential enzyme activities are low relative to the large stocks of organic matter in Arctic tundra soils, and that enzyme activity is low at in situ temperatures. We measured the potential activity of six hydrolytic enzymes at 4 and 20 °C on four sampling dates in tussock, intertussock, shrub organic, and shrub mineral soils at Toolik Lake, Alaska. Potential activities of N‐acetyl glucosaminidase, β‐glucosidase, and peptidase tended to be greatest at the end of winter, suggesting that microbes produced enzymes while soils were frozen. In general, enzyme activities did not increase during the Arctic summer, suggesting that enzyme production is N‐limited during the period when temperatures would otherwise drive higher enzyme activity in situ. We also detected seasonal variations in the temperature sensitivity (Q₁₀) of soil enzymes. In general, soil enzyme pools were more sensitive to temperature at the end of the winter than during the summer. We modeled potential in situβ‐glucosidase activities for tussock and shrub organic soils based on measured enzyme activities, temperature sensitivities, and daily soil temperature data. Modeled in situ enzyme activity in tussock soils increased briefly during the spring, then declined through the summer. In shrub soils, modeled enzyme activities increased through the spring thaw into early August, and then declined through the late summer and into winter. Overall, temperature is the strongest factor driving low in situ enzyme activities in the Arctic. However, enzyme activity was low during the summer, possibly due to N‐limitation of enzyme production, which would constrain enzyme activity during the brief period when temperatures would otherwise drive higher rates of decomposition.     

青藏高原不同高寒草地类型土壤酶活性及其影响因子

土壤酶活性作为生态系统养分循环的关键因素, 是反映土壤质量和生态系统功能的重要指标, 但是关于高寒草地生态系统中不同草地类型间酶活性的差异研究还很少。因此, 该研究在藏北高寒草地选择高寒草甸、高寒草原、高寒草甸草原、高寒荒漠草原和高寒荒漠5种草地类型进行野外原位调查和采样, 测定了涉及碳(C)、氮(N)和磷(P)循环的14种酶的活性, 并建立了高寒草地酶活性与土壤微生物和土壤理化性质等环境因子的关系。结果表明: C循环酶(蔗糖酶、纤维素酶、β-葡萄糖苷酶、多酚氧化酶和过氧化物酶)和P循环酶(碱性磷酸酶)在不同高寒草地类型间活性差异明显, N循环酶中仅芳香氨基酶和亚硝酸盐还原酶两种酶在不同高寒草地类型间活性差异明显。同时, C、N和P循环酶之间存在一定的相关关系, 其中, 蔗糖酶和碱性磷酸酶、纤维素酶和α-乙酰氨基葡萄糖苷酶活性显著正相关, 多酚氧化酶与亚硝酸还原酶和β-乙酰氨基葡萄糖苷酶活性显著负相关。在测定的19个环境指标中, 土壤有机质(SOM)含量、革兰氏阴性菌数量、土壤N和P含量计量比、革兰氏阳性菌数量、细菌数量、放线菌数量、全氮含量、真菌数量是影响土壤酶活性的关键因子, 且SOM含量的影响最大(解释量为11.9%)。综上所述, 不同高寒草地类型间C循环酶、P循环酶和两种N循环酶(芳香氨基酶和亚硝酸还原酶)活性差异显著, SOM含量、微生物数量和N含量等是影响高寒草地生态系统土壤酶活性的关键因子。     

Trajectories of change: riparian vegetation and soil conditions following livestock removal and replanting

Riparian zones provide critically important ecological functions, including the interception of nutrients and sediments before they enter waterways. Consequently, riparian zones, and the vegetation they support, are often considered as an important ‘final buffer’ between waterways and adjacent land. In agricultural ecosystems, riparian zones are therefore increasingly recognized as an important component of strategies aimed at minimizing the flow of nutrients and sediments into waterways. Accordingly, riparian zones are increasingly afforded protection and are targeted for restoration. Here we present results of a study in which we aimed to identify patterns of change in soil and vegetation properties in riparian zones, under different management regimes, adjacent to tributary streams in one of south‐eastern Australia's main agricultural regions. We compared riparia that were heavily impacted by agricultural activities, were in remnant condition or had undergone some restoration activities and were thus in a transitional state. There was an increase in plant cover and soil C concentration between impacted through to remnant sites, with transitional sites intermediate, suggesting that improvements in soil conditions were becoming evident following restoration activities. In our assessment of soil physicochemical properties we investigated the relationships between riparian condition and soil properties, taking into account the influence of adjacent land use on these relationships. Importantly, the concentrations of NO₃^‐ and plant available P in riparian surface soils were more or less influenced by concentrations in the adjacent land depending upon riparian condition. This will, in turn, have consequences for nutrient inputs into streams. This study emphasizes that riparian zones need to be managed within their wider landscape context. Furthermore, the results of this study will inform efforts seeking to minimize impacts of agricultural activities on waterways, through the conservation and/or restoration of riparian ecosystems.     

Effects of dissolved organic matter from different plant sources on soil enzyme activities in subtropical forests

探究不同植物来源可溶性有机质(DOM)进入土壤后对酶活性的影响, 可以为降水淋溶下亚热带地区不同森林生态系统土壤碳循环提供科学依据。该研究提取杉木(Cunninghamia lanceolata)、木荷(Schima superba)和楠木(Phoebe zherman) 3种植物鲜叶中的DOM分别输入杉木人工林土壤中, 以等量的去离子水添加为对照, 进行25天的室内培养。培养结束后测定土壤理化性质、微生物生物量和酶活性等指标。结果表明: 与对照处理(CT)相比, 添加3种叶片DOM后, 土壤总有机碳(SOC)、总氮(TN)含量和碳氮比均无显著变化。杉木叶片DOM添加处理(CL)的TN含量显著低于木荷叶片DOM添加处理(SL)和楠木叶片DOM添加处理(PL), 碳氮比显著高于SL和PL。3种叶片DOM输入整体上提高了土壤溶解有机碳(DOC)和溶解有机氮(DON)的含量。叶片DOM输入后土壤微生物生物量碳(MBC)含量无显著变化, 然而CL和SL的土壤微生物生物量氮(MBN)含量分别比CT降低了50.9%和51.1%, PL的MBN含量比CT提高了54.0%。与CT相比, 不同植物来源DOM输入后, β-葡萄糖苷酶(βG)、纤维素水解酶(CBH)和过氧化物酶(PEO) 3种酶活性均显著上升, 而多酚氧化酶(PPO)活性则显著下降; 此外, βG和CBH活性均表现出CL > SL > PL的特征。相关性分析的结果表明, 添加叶片DOM 3种处理的SOC、TN、MBN含量和βG、CBH活性都与所输入DOM的DOC含量和腐殖化指数(HIX)显著相关, 此外, 土壤MBN含量和PPO活性与输入叶片DOM的pH呈正相关关系。冗余分析(RDA)结果表明, 叶片DOM输入后引起土壤酶活性变化的关键因子是DON和DOC含量。总体来说, 不同植物来源DOM性质的差异会影响土壤碳循环水解酶的活性, 而叶片DOM输入后增加了土壤碳和氮的有效性, 引起4种碳循环酶的不同响应。     

城市化地区河岸带植被特征及其与河岸硬度的关系——以晋江市为例

确立了滨河河道硬度与滨河土地硬度两个指标,用以研究城市化地区河岸带的植物构成、多样性与均匀度、优势植物等特征与河岸硬度的关系。选定晋江市都市区12条主要河流作为研究对象,通过样地调查收集数据,并采用相应指数进行数据处理分析,结果表明:(1)调查河流的河岸带植被物种共计70科143属159种,其中乔木20科30属41种,灌木15科15属20种,草本35科98属98种,草本居主导地位,河流间种类分布不均衡;(2)河岸带植物乔灌草区系均以广义热带性成分居多,其次为世界性成分、温带性成分,无中国特有分布类型,乔木中广义热带成分占绝对主导,直观反映地带性特征,灌木与草本中的温带成分多于乔木中的温带成分,类型趋于多元,种类更丰富;(3)从河岸植被优势植物构成来看,主要优势乔木与灌木基本为本土植物,而主要草本中外来植物入侵严重,对地带性植物景观的指示显然不及乔木与灌木;(4)从河岸植被的人工美学属性来看,灌木优势植物中园林观赏植物的种类数显著多于乔木、草本优势植物,反映出晋江人工审美主导的滨河景观空间主要改变与塑造了灌木层植被景观;(5)从河岸植物的人居需求属性来看,龙眼、杨桃等多见于庭院林、水岸林的水果树种也在河岸植被中频繁出现,反映出人口密集区由于对植物生产用途的重视而对河岸植被产生的影响;(6)滨河土地硬度与河道硬度对河岸带灌木植物的影响最强烈,二者均对河岸带植物多样性造成威胁,且前者具有更大的影响力,而后者直接影响了河岸植物的分布形态,出于生产与审美目的的人为干扰对河岸带植物优势种的影响力随滨河硬度的增加而加强,低滨河硬度有助留存原生植被群落;(7)天然弯曲的河流形态对河流植被特征具有积极影响,有助于保留更多本土植被类型,并能在某种程度上丰富乔灌草的植物种类,但这种缓和作用无法根本扭转河岸硬化对植物多样性的胁迫影响。研究表明,城市化地区河流的岸带植被特征与沿线人为干扰类型和强度密切相关,恢复与塑造河岸生态景观要以乡土植被为主,通过乔木景观塑造地带性景观,并以灌木与草本丰富植被景观。     

不同植物来源可溶性有机质对亚热带森林土壤酶活性的影响

探究不同植物来源可溶性有机质(DOM)进入土壤后对酶活性的影响, 可以为降水淋溶下亚热带地区不同森林生态系统土壤碳循环提供科学依据。该研究提取杉木(Cunninghamia lanceolata)、木荷(Schima superba)和楠木(Phoebe zherman) 3种植物鲜叶中的DOM分别输入杉木人工林土壤中, 以等量的去离子水添加为对照, 进行25天的室内培养。培养结束后测定土壤理化性质、微生物生物量和酶活性等指标。结果表明: 与对照处理(CT)相比, 添加3种叶片DOM后, 土壤总有机碳(SOC)、总氮(TN)含量和碳氮比均无显著变化。杉木叶片DOM添加处理(CL)的TN含量显著低于木荷叶片DOM添加处理(SL)和楠木叶片DOM添加处理(PL), 碳氮比显著高于SL和PL。3种叶片DOM输入整体上提高了土壤溶解有机碳(DOC)和溶解有机氮(DON)的含量。叶片DOM输入后土壤微生物生物量碳(MBC)含量无显著变化, 然而CL和SL的土壤微生物生物量氮(MBN)含量分别比CT降低了50.9%和51.1%, PL的MBN含量比CT提高了54.0%。与CT相比, 不同植物来源DOM输入后, β-葡萄糖苷酶(βG)、纤维素水解酶(CBH)和过氧化物酶(PEO) 3种酶活性均显著上升, 而多酚氧化酶(PPO)活性则显著下降; 此外, βG和CBH活性均表现出CL > SL > PL的特征。相关性分析的结果表明, 添加叶片DOM 3种处理的SOC、TN、MBN含量和βG、CBH活性都与所输入DOM的DOC含量和腐殖化指数(HIX)显著相关, 此外, 土壤MBN含量和PPO活性与输入叶片DOM的pH呈正相关关系。冗余分析(RDA)结果表明, 叶片DOM输入后引起土壤酶活性变化的关键因子是DON和DOC含量。总体来说, 不同植物来源DOM性质的差异会影响土壤碳循环水解酶的活性, 而叶片DOM输入后增加了土壤碳和氮的有效性, 引起4种碳循环酶的不同响应。