青海云杉林凋落物分解早期微生物生物量时空动态变化

凋落物分解过程中的微生物生物量动态对于深入了解森林生态系统凋落物分解机理具有重要意义。为了解高寒山地森林典型树种凋落物分解过程中的微生物生物量动态特征,采用凋落物袋野外原位分解法,研究了海拔2850 m、2950 m、3050 m、3150 m和3250 m树冠中心(CC)与树冠边缘(CE)青海云杉(Picea crassifolia)叶凋落物分解过程中凋落物和土壤中的微生物生物量碳(MBC)、微生物生物量氮(MBN)和微生物生物量磷(MBP)时空动态变化。时间尺度上,不同海拔CC与CE凋落物中的MBC、MBN和MBP在生长季节初期上升,生长季节后期下降;但土壤中的MBC、MBN和MBP却在生长季节初期下降,生长季节后期上升。然而,3050 m海拔CE和3250 m海拔土壤中的MBP含量呈“先下降-后上升-再下降”的倒“N”型变化格局。空间尺度上,凋落物中的MBC和MBN含量高于土壤中的,但MBP出现相反情况;CE处的MBC、MBN和MBP含量均显著(P<0.05)高于CC;总体而言,MBC、MBN和MBP含量以中海拔显著最高(P<0.05),其次为低海拔,高海拔显著最低(...     

宁夏罗山自然保护区3种典型林分凋落物和土壤层水源涵养能力综合评估

森林凋落物层和土壤层是森林生态水文效应中的主要贡献层，对森林生态系统水土保持功能和水源涵养能力有重要影响。对比宁夏罗山自然保护区3种典型林分类型凋落物和土壤层水文效应的变化规律和水源涵养能力大小，为该地区的森林生态水文、水土保持和森林管理提供科学依据。以该自然保护区青海云杉纯林、油松纯林和青海云杉油松混交林为研究对象，运用称量、室内浸泡、环刀法和回归分析法对凋落物和土壤层的水文效应进行测定和拟合，并使用熵权法对二者的水源涵养能力进行评估。结果表明：（1）青海云杉油松混交林凋落物的总厚度和总储量显著高于青海云杉纯林和油松纯林（P<0.05），3种林分类型的半分解层的厚度和储量高于未分解层。（2）凋落物层最大持水量范围为63.29-95.08t/hm²，最大持水率范围为335.97%-353.85%，有效拦蓄量范围为34.09-63.92t/hm²，三者均为青海云杉油松混交林>云杉纯林>油松纯林。（3）3种林分类型的凋落物持水量（Q）与浸泡时间（t）呈对数函数关系，吸水速率（V）与浸泡时间（t）呈幂函数关系。（4）从3种林分类型的土壤物理性质和持水特性得出，3种林分类型的土壤层水文效应的等级排序为云杉油松混交林>油松纯林>青海云杉纯林。（5）凋落物层和土壤层的水源涵养能力大小为青海云杉油松混交林（0.43）>油松林（0.3）>青海云杉林（0.27）。综合来看，青海云杉油松混交林的凋落物层和土壤层的水源涵养能力最优，其次是纯林，说明混交林在水土保持和水源涵养方面比纯林更具优势。     

香樟凋落叶分解过程对两种间作作物生长和光合特性的影响

采用盆栽试验方法,探讨了香樟(Cinnamomum camphora)凋落叶不同土壤添加水平(0 g/盆为CK、25 g/盆、50 g/盆,100 g/盆)对受体作物小白菜(Brassica chinensis)、莴笋(Lactuca sativa)幼苗生长和光合特性的影响。结果显示:(1)香樟凋落叶分解对两种作物的地径、株高、生物量、叶片数和叶面积均有明显的抑制作用,且抑制效应随凋落叶添加量的增加而增强,但随着分解时间的延长其抑制作用逐渐减弱甚至表现为促进作用。(2)香樟凋落叶分解对两种作物的光合色素含量均有明显的抑制效应,并随凋落叶添加量的增加抑制作用增强,且持续时间延长。(3)经凋落叶处理的两种作物叶片净光合速率(P_n)、气孔导度(G_s)、蒸腾速率(T_r)、水分利用率(WUE)总体上均低于CK,而胞间CO₂浓度(C_i)在各凋落叶处理下均高于CK。(4)随着土壤中凋落叶量的增加,两种作物在光饱和以及CO₂饱和状态下的最大净光合速率(P_{n max})、表观量子效率(AQY)、羧化速率(CE)、光呼吸速率(R_p)和暗呼吸速率(R_d)均不断下降,而光补偿点(LCP)、光饱和点(LSP)、CO₂饱和点(CSP)、CO₂补偿点(CCP)因受体作物的不同,表现出不同的变化趋势。研究表明,土壤中香樟凋落叶分解释放的化感物质,能通过降低受体作物的光合色素合成和光合能力,限制其营养生长,最终影响生物量积累;相对于莴笋,小白菜对香樟凋落叶分解产生的化感胁迫效应具有更强的耐受性,可能更适宜在香樟林间种植。     

模拟增温和不同凋落物基质质量对凋落物分解速率的影响

采用凋落物分解袋法,研究了在土壤、水分相当的条件下模拟增温对红松(Pinus koraiensis)、蒙古栎(Quercus mongolica)及其混合凋落物分解的影响,以及在不同温度水平下,不同凋落物质量(两种单一凋落物和混合凋落物)的分解特性。利用碱式吸收法测量了凋落物分解累积释放CO₂动态。将N浓度和C/N率作为凋落物质量参数,用呼吸产生CO₂的积累值和凋落物质量损失率确定凋落物分解率。结果表明温度升高对单一凋落物和混合凋落物分解均有促进作用,在不同温度水平上,不同质量凋落物的分解特性有所差别,25 ℃和29 ℃条件下混合凋落物分解速率>蒙古栎单一凋落物>红松单一凋落物分解速率。然而,在31 ℃条件下混合凋落物与蒙古栎单一凋落物分解速率相差不大,二者均大于红松单一凋落物分解速率。     

半干旱草地不同植物枯落物分解对放牧和封育的响应

为探究放牧和封育对半干旱草地植物枯落物分解的影响,选取赖草、牛枝子及其混合物为研究对象,调查了不同网孔分解袋中宁夏半干旱草地植物枯落物分解特征及对放牧和封育的响应规律。结果表明：（1）放牧样地250目网孔中,枯落物质量残留率表现为牛枝子显著高于赖草和混合物（P<0.05）,而在放牧样地30目网孔、封育样地2种网孔中,枯落物质量残留率均表现为3种枯落物间无显著差异。（2）250目网孔中,放牧和封育样地枯落物分解衰减常数均表现为混合物显著高于牛枝子,而赖草居中;并且,牛枝子枯落物分解衰减常数表现为封育样地显著高于放牧样地。30目网孔中,放牧和封育样地枯落物分解衰减常数均表现为赖草、混合物显著高于牛枝子（P<0.05）;并且,牛枝子枯落物分解衰减常数表现为封育样地显著高于放牧样地（P<0.05）。（3）在放牧样地,仅牛枝子枯落物R_m表现为30目显著低于250目网孔（P<0.05）,k表现为30目显著高于250目网孔（P<0.05）;土壤动物对枯落物分解的贡献率表现为混合物显著低于牛枝子,赖草居中（P<0.05）。而在封育样地,仅牛枝子枯落物k表现为30目显著高于250目网孔（P<0.05）;土壤动物对枯落物分解的贡献率表现为混合物和牛枝子均显著高于赖草,且混合枯落物的土壤动物贡献率表现为封育样地显著高于放牧样地（P<0.05）。（4）枯落物残留率与其初始N、P、木质素/N、C/P呈显著相关性（P<0.05）;枯落物分解衰减常数与其初始N、P、木质素、N/P、C/P和木质素/P间均呈显著相关性（P<0.05）。研究表明,植物种类组成显著影响枯落物的残留率和分解衰减常数。放牧与封育管理通过影响网孔中土壤动物分布来调控半干旱区草地植物枯落物的分解,而且封育管理更有利于促进土壤动物对低质量枯落物（牛枝子）的分解。     

云冷杉红松林掘根倒木及其微立地对凋落叶分解速率及养分释放的影响

采用凋落物分解袋埋藏法,将采集的红松（Pinus koraiensis）、紫椴（Tilia amurensis）和色木槭（Acer mono）凋落叶按自然比例混合装入袋中,于2019年7月将其埋入云冷杉红松林中不同腐烂等级（Ⅱ、Ⅲ、Ⅳ级）的掘根倒木（UT）及其形成的坑底（PB）与丘面（MF）以及对照（包括林隙（FG）和林分（IS））等11种微立地下。8-10月每月从每种微立地取回3袋,处理后测定凋落叶的质量、碳、氮、磷含量。采用相关分析和方差分析的统计分析方法,探究不同微立地下凋落叶的质量、分解速率与养分元素之间的相关性和差异显著性。结果表明：（1）微立地和分解时间对凋落叶质量具有极显著影响（P<0.01）。凋落叶分解90天后,各微立地的凋落叶质量残留率排列为：PB （85.64%） > MF （83.09%） > FG （81.33%） > IS （80.93%） > UT （80.27%）;（2）各微立地的凋落叶分解速率排列为：k_IS=k_UT>k_FG>k_MF>k_PB;Olson指数模型能够较好的模拟各微立地的凋落叶分解动态;年分解速率k为0.61-1.42,分解50%和95%所需时间分别为0.49-1.14 a和2.10-4.92 a。（3）各微立地的凋落叶C残留率总体呈下降趋势,表现为释放模式;UT和MF微立地的N、P残留率持续下降,表现为释放;PB微立地的N、P变化模式分别为释放-富集-释放、富集-释放模式,释放均大于富集,最终表现为释放模式。微立地对凋落叶P释放具有极显著影响（P<0.01）,对N释放具有显著影响（P<0.05）;微立地与掘根倒木腐烂等级的交互作用对C、N释放均具有极显著的影响（P<0.01）。（4）凋落叶质量残留率与P的残留率在所有微立地中均存在显著或极显著正相关关系,与N的残留率仅在Ⅱ级UT、PB微立地、Ⅲ级UT微立地、Ⅳ级UT、PB和MF微立地以及FG对照中呈显著或极显著的正相关关系,与C的残留率仅在Ⅱ级UT、PB微立地、Ⅳ级PB、MF微立地中存在极显著或显著正相关关系,与C/N在Ⅱ级UT微立地、Ⅲ级UT、MF微立地和FG对照中呈显著或极显著负相关关系。可见,与不同腐烂等级的掘根倒木相比,掘根倒木形成的微立地环境对凋落叶分解和养分释放的影响较大。     

凋落物和根系对沂蒙山区三种森林恢复方式土壤酸性磷酸酶动力学特征的影响

酸性磷酸酶动力学特征可反映不同底物供应下土壤磷转化状况。以人工恢复的引进种黑松人工林和本地种栓皮栎人工林以及自然恢复的天然次生林为研究对象,开展凋落物添加去除和根系去除对土壤酸性磷酸酶动力学特征的影响研究。结果表明:(1)三种森林恢复方式下土壤酸性磷酸酶活性和最大反应速度(V_max)均为双倍凋落物＞对照＞去除凋落物＞去除根系＞无输入;(2)改变凋落物和根系输入对酸性磷酸酶的半饱和常数(K_m)和催化效率(V_max/K_m)影响不大;(3)酸性磷酸酶活性受速效磷含量的反馈调节;土壤氮可利用性和含水量显著影响酸性磷酸酶活性。改变凋落物和根系输入对引进种黑松人工林土壤有机磷转化能力影响最大,天然次生林次之,本地种栓皮栎人工林最稳定。根系对土壤酸性磷酸酶动力学特征的影响大于凋落物。其结果可为暖温带森林恢复,应对气候变化和森林防火、收集凋落物等管理措施提供理论依据。     

不同水分条件下杨树-玉米复合系统凋落物分解特性

为探讨水分变化对农林复合生态系统凋落物分解特性的影响,以河西走廊杨树（Populus）-玉米（Zea mays）凋落物为研究对象,设置正常水分（9200 m³/hm²,对照）,轻度干旱胁迫（减少15%,7800 m³/hm²）,中度干旱胁迫（减少30%,6400 m³/hm²）3种不同水分处理条件,采用分解袋法研究了不同水分条件下杨树叶和玉米秸秆的质量残留率、分解速率和养分含量变化特征。结果表明：（1）随着干旱胁迫的加剧,两种凋落物的质量残留率均增加,而分解速率降低。经过164 d的分解后,杨树叶和玉米秸秆的质量残留率分别为70.43%-77.49%、63.55%-68.29%。分析表明：水分和时间对各类型凋落物的质量残留率均有极显著的影响（P<0.001）,但二者的交互作用不显著（P>0.05）;干旱胁迫显著降低了玉米秸秆的分解速率,但杨树叶的分解速率却只是在中度干旱胁迫下显著降低（P<0.05）。对于不同类型凋落物而言,分解速率表现为玉米秸秆>杨树叶。（2）两种类型凋落物的氮（N）残留率在分解过程中表现为降低的趋势,但随着干旱程度的加大,N的残留率增加,表明水分抑制了N的释放过程。分解164d后,同一类型凋落物不同水分条件下的N残留率均存在显著差异。对于同一水分条件下不同凋落物而言,玉米秸秆的N残留率最低,而杨树叶最高。总的来说,水分降低对干旱区农林复合系统内凋落物的分解和氮元素含量具有显著的抑制作用。     

西沙永兴岛抗风桐与海岸桐群落凋落叶分解及中型土壤动物的贡献

我国南海诸岛主要是珊瑚岛。植物凋落物分解是生态系统元素循环的关键环节,但目前关于南海珊瑚岛生态系统凋落物分解的研究还是空白。以我国西沙群岛的优势树种抗风桐（Pisonia grandis）和海岸桐（Guettarda speciosa）为研究对象,采用凋落物袋法,分别于分解期间的第3、6、9、13和15个月取样,探究中型土壤动物对两种植物群落中凋落物分解过程中质量损失和养分释放的影响。结果表明：与没有中型土壤动物存在的情况（0.1 mm凋落物袋）相比,分解开始后的6个月内,中型土壤动物存在（2 mm凋落物袋）使抗风桐和海岸桐凋落叶分解速率分别提高了12.3%和4.8%（P<0.05）;分解6-15个月期间,中型土壤动物存在使抗风桐和海岸桐凋落叶分解速率分别提高了33.0%和12.3%（P<0.05）。中型土壤动物排除显著影响了不同分解阶段凋落叶总碳（Total carbon,TC）、总氮（Total nitrogen,TN）、纤维素、木质素和半纤维素的残留率变化。中型土壤动物群落组成受土壤温度显著影响（P<0.05）,它们对凋落叶分解的贡献可能主要受优势类群如真螨目和寄螨目的影响。相较海岸桐,抗风桐凋落叶的分解周期更短,中型土壤动物对其的贡献更大;选用抗风桐作为南海珊瑚岛退化植被恢复或新建的先锋种对促进生态系统元素循环更有利。     

喀斯特11种典型生态恢复树种凋落叶分解及其对土壤碳排放的激发效应

旨在探究喀斯特地区退化生态系统植被恢复树种凋落叶分解过程及其对土壤碳排放的激发效应,为选择合适的树种进行植被恢复提供数据支持。以中国林科院热带林业实验中心大青山石山树木园11种适应性强、耐干旱贫瘠的优良石山树种为研究对象,利用¹³C自然丰度法区分凋落叶和土壤来源CO₂并量化土壤激发效应,比较不同生态恢复树种凋落叶分解及其激发效应的差异,探讨凋落物分解及其激发效应与凋落物性状之间的关联。结果表明:(1)11个生态恢复树种凋落叶在碳相关化学性质(水溶性碳、半纤维素和单宁含量等)、养分含量(磷和镁含量等)及化学计量特征(碳磷比和氮磷比)等方面均表现出较高程度变异。(2)不同生态恢复树种凋落叶分解及其诱导的土壤激发效应具有极显著差异(P<0.001);在整个培养实验期间,11个生态恢复树种凋落叶平均分解了35.3%,其中海南椴分解最快,达到50%,而青冈栎分解最慢,仅分解16.5%。(3)总体上看,凋落叶处理的土壤呼吸速率(5.1 mg C kg^-1 土壤 d^-1)是对照土壤呼吸速率(2.3 mg C kg^-1土壤d^-1)的2.2倍,凋落叶添加显著促进土壤有机碳分解,平均达到37.6%;其中海南椴、割舌树和任豆凋落叶输入则抑制土壤有机碳分解(抑制程度分别为-13.2%、-6.9%和-22.5%),产生负激发效应。(4)凋落叶分解与非结构性碳(r=0.63,P=0.04)和水溶性碳(r=0.91,P<0.001)呈显著正相关,与叶干物质含量(r=0.64,P=0.03)、纤维素(r=0.62,P=0.04)和锰含量(r=-0.63,P=0.04)呈显著负相关。多元回归分析结果表明,水溶性碳、钾和钙含量相结合可以解释生态恢复树种凋落叶分解变异的98%;然而,凋落叶性状与土壤激发效应强度之间并没有显著相关性。从土壤养分归还角度考虑,喀斯特退化生态系统恢复树种可以选择光皮梾木、海南椴、顶果木和降香黄檀等凋落叶分解较快的树种,以促进土壤养分循环和植被恢复;另一方面,从土壤碳固持角度来看,海南椴、任豆和割舌树等凋落叶输入会抑制土壤有机碳分解,从而有利于提高退化生态系统土壤碳封存能力。     

东北地区森林凋落叶分解速率与气候、林型、林分光照的关系

在东北长白山、张广才岭、小兴安岭、大兴安岭的主要森林类型中设置26块样地,进行为期3a(2004—2006年)凋落叶分解实验,以研究气候、林型、林冠透光率对凋落叶分解速率的相对影响大小。结果表明,不同林型凋落叶分解速率依次为:落叶阔叶林针阔叶混交林落叶针叶林常绿针叶林岳桦林。对分解速率影响因素的分析表明,气候因子(热量和水分)对分解速率有较强的解释力,分别解释了分解常数k和分解95%所需时间(t95%)的55.5%和65.0%的变异。但是,气候对分解速率的影响在很大程度上是通过与林型、林冠透光率的协同作用而实现的,其独立解释力并不大(9%)。气候的变化导致林型(物种组成)的变化、进而影响分解速率,这一因素解释了分解参数变异的46.8%(k)和56.8%(t95%)。与此同时,气候和林型的变化还导致林冠透光率的变化,随着热量水平的上升林冠透光率下降、间接提高分解速率。这一因素分别解释了k值和t95%变异的23.9%和22.3%。研究结果表明,气候对凋落叶分解的影响主要是通过对物种组成、林冠结构(影响透光率)等生物因素的间接作用实现的。忽视这些生物因素、简单研究气候和分解速率的关系可能难以正确预测未来气候变化对凋落物分解的影响。     

Effects of enhanced atmospheric CO2 and nutrient supply on the quality and subsequent decomposition of fine roots of Betula pendula Roth. and Picea sitchensis (Bong.) Carr.

Fine root litter derived from birch (Betula pendula Roth.) and Sitka spruce (Picea sitchensis (Bong.) Carr.) plants grown under two CO₂ atmospheric concentrations (350 ppm and 600 ppm) and two nutrient regimes was used for decomposition studies in laboratory microcosms. Although there were interactions between litter type, CO₂/fertiliser treatments and decomposition rates, in general, an increase in the C/N ratio of the root tissue was observed for roots of both species grown under elevated CO₂ in unfertilized soil. Both weight loss and respiration of decomposing birch roots were significantly reduced in materials derived from enriched CO₂, whilst the decomposition of spruce roots showed no such effect. A parallel experiment was performed using Betula pendula root litter grown under different N regimes, in order to test the relationship between C/N ratio of litter and root decomposition rate. A highly significant (p<0.001) negative correlation between C/N ratio and root litter respiration was found, with an r²=0.97. The results suggest that the increased C/N ratio of plant tissues induced by elevated CO₂ can result in a reduction of decomposition rate, with a resulting increase in forest soil C stores.     

Early needle senescence and thinning of the crown structure of Picea abies as induced by chronic SO2 pollution. II. Field data basis, model results and tolerance limits

Field data on the sulphur and cation budget of growing Norway spruce canopies (Picea abies [L.] Karst.) are summarized. They are used to test a spruce decline model capable of quantifying effects of chronic SO₂ pollution on spruce forests. At ambient SO₂ concentrations, acute SO₂ damage is rare, but exposure to polluted air produces reversible thinning of the canopy structure with a half-time of a few years. Canopy thinning in the spruce decline model is highest (i) at elevated SO₂ pollution, (ii) in the mountains, (iii) at unfertilized sites with poor K⁺, Mg²⁺ or Zn²⁺ supply, (iv) at low spruce litter decomposition rates, and (v) acidic, shallow soils at high annual precipitation rates in the field and vice versa. Model application using field data from Würzburg (moderate SO₂ pollution, alkaline soils, no spruce decline) and from the Erzgebirge (extreme SO₂ pollution, acidic soils in the mountains, massive spruce decline) predicts canopy thinning by 2–11% in Würzburg and by 45–70% in the Erzgebirge. The model also predicts different SO₂-tolerance limits for Norway spruce depending on the site elevation and on the nutritional status of the needles. If needle loss of more than 25% (damage class 2) is taken to indicate ‘real damage’ exceeding natural variances, then for optimum soil conditions SO₂ tolerance limits range from (27.3 ± 7.4) μg m^?3 to (62.6 ± 16.5) μg m^?3. For shallow and acidic soils, SO₂ tolerance limits range from (22.0 ± 5.5) μg m^?3 to (37.4 ± 7.5) μ m^?3. These tolerance limits, which are calculated on an ecophysiological data basis for Norway spruce are close to epidemiological SO₂-toIerance limits as recommended by the IUFRO, UN-ECE and WHO. The observed statistical regression slope of the plot (damaged spruce trees vs. SO₂-pollution) in west Germany is confirmed by modelling (6% error). Model application to other forest trees allows deduction of the observed sequence of SO₂-sensitivity: Abies > Picea > Pinus > Fagus > Quercus. Thus, acute phytotoxicity of SO₂ seems not to be involved in ‘forest decline’. Chronic SO₂-pollution induces massive canopy thinning of Abies alba and Picea abies only at unfavourable sites, where natural stress factors and secondary effects of SO₂pollution act together to produce tree decline.     

干旱与半干旱区灌丛微生境中红砂枯落物分解特征及中小型节肢动物的作用

在干旱区(内蒙古乌拉特后旗)和半干旱区(宁夏盐池)荒漠草原区,选择柠条灌丛内外微生境为研究样地,以红砂枯落物为研究对象,利用2种规格网孔分解袋(30目和250目网孔),探索中小型节肢动物在红砂枯落物分解过程中的作用规律,研究灌丛微生境中红砂枯落物质量损失变化特征及节肢动物群落的贡献。结果表明：(1)在干旱与半干旱区,红砂枯落物分解常数K均表现为灌丛内外微生境间无显著差异,且有无节肢动物参与对K的影响均较小。(2)分解至12个月时,无节肢动物参与的情况下,干旱与半干旱区红砂枯落物残留率均表现为裸地显著低于灌丛;但有节肢动物参与时,枯落物残留率则表现为灌丛内外微生境间无显著差异。分解至44个月时,无节肢动物参与的情况下,仅在干旱区枯落物残留率表现为裸地显著高于灌丛;而有节肢动物参与时,干旱与半干旱区枯落物残留率均表现为灌丛内外微生境间无显著差异。(3)节肢动物对红砂枯落物质量损失的贡献率呈现单峰值现象,且在分解至24个月时达到峰值。枯落物分解至12个月时,仅半干旱区节肢动物对红砂枯落物分解的贡献率表现为裸地显著低于灌丛;分解至44个月时,仅干旱区节肢动物对红砂枯落物分解的贡献率表现为裸地显...     

模拟氮沉降和降雨对华西雨屏区常绿阔叶林凋落物分解的影响

从2013年11月至2015年5月,采用凋落物分解袋法,设置了对照(CK)、氮沉降(N)、减雨(R)、增雨(A)、氮沉降+减雨(NR)、氮沉降+增雨(NA)6个处理水平,研究了模拟氮沉降和降雨对华西雨屏区常绿阔叶林凋落物分解的影响。结果表明:华西雨屏区常绿阔叶林凋落叶分解较快,凋落枝分解较慢;凋落物夏季分解较快,其他季节分解较慢。经过18个月的分解后,凋落叶和枝的质量残留率分别为45.86%和86.67%,凋落叶分解50%需要的时间为1.42 a,比枝短6.19 a。各处理凋落物叶分解系数表现为:k(A)k(CK)k(NA)k(N)k(R)k(NR),凋落枝质量残留率表现为:NNRRNACKA。模拟氮沉降、减雨和增雨处理凋落叶分解50%分别需要1.79、1.94a和1.36a,凋落枝分解50%分别需要8.84、8.63 a和6.47 a。各处理凋落叶分解95%需要5.37—11.33 a,凋落枝分解95%需要27.41—33.84 a。同一氮沉降条件下,增雨处理促进凋落叶分解,减雨处理抑制凋落叶分解;同一降雨条件下,氮沉降抑制凋落叶分解。氮沉降或降雨对凋落物的分解产生显著影响(P0.05),其交互作用影响不显著(P0.05)。可见,在氮沉降持续增加和降雨格局改变的背景下,增雨促进了华西雨屏区天然常绿阔叶林凋落物的分解,氮沉降和减雨抑制了凋落物的分解,模拟氮沉降和降雨对凋落物的分解交互作用表现不明显。     

Biological decomposition efficiency in different woodland soils

The decomposition (meaning disappearance) of different leaf types and artificial leaves made from cellulose hydrate foil was studied in three forests — an alluvial forest (Ulmetum), a beech forest on limestone soil (Melico-Fagetum), and a spruce forest in soil overlying limestone bedrock. Fine, medium, and coarse mesh litter bags of special design were used to investigate the roles of abiotic factors, microorganisms, and meso- and macrofauna in effecting decomposition in the three habitats. Additionally, the experimental design was carefully arranged so as to provide information about the effects on decomposition processes of the duration of exposure and the date or moment of exposure.

1. Exposure of litter samples oor 12 months showed:
2. Litter enclosed in fine mesh bags decomposed to some 40–44% of the initial amount placed in each of the three forests. Most of this decomposition can be attributed to abiotic factors and microoganisms.
3. Litter placed in medium mesh litter bags reduced by ca. 60% in alluvial forest, ca. 50% in beech forest and ca. 44% in spruce forest.
4. Litter enclosed in coarse mesh litter bags was reduced by 71% of the initial weights exposed in alluvial and beech forests; in the spruce forest decomposition was no greater than observed with fine and medium mesh litter bags. Clearly, in spruce forest the macrofauna has little or no part to play in effecting decomposition.
5. Sequential month by month exposure of hazel leaves and cellulose hydrate foil in coarse mesh litter bags in all three forests showed that one month of exposure led to only slight material losses, they did occur smallest between March and May, and largest between June and October/November.
6. Coarse mesh litter bags containing either hazel or artificial leaves of cellulose hydrate foil were exposed to natural decomposition processes in December 1977 and subsampled monthly over a period of one year, this series constituted the From-sequence of experiments. Each of the From-sequence samples removed was immediately replaced by a fresh litter bag which was left in place until December 1978, this series constituted the To-sequence of experiments. The results arising from the designated From- and To-sequences showed:
7. During the course of one year hazel leaves decomposed completely in alluvial forest, almost completely in beech forest but to only 50% of the initial value in spruce forest.
8. Duration of exposure and not the date of exposure is the major controlling influence on decomposition in alluvial forest, a characteristic reflected in the mirror-image courses of the From- and To-sequences curves with respect to the abscissa or time axis. Conversely the date of exposure and not the duration of exposure is the major controlling influence on decomposition in the spruce forest, a characteristic reflected in the mirror-image courses of the From-and To-sequences with respect to the ordinate or axis of percentage decomposition.
9. Leaf powder amendment increased the decomposition rate of the hazel and cellulose hydrate leaves in the spruce forest but had no significant effect on their decomposition rate in alluvial and beech forests. It is concluded from this, and other evidence, that litter amendment by leaf fragments of phytophage frass in sites of low biological decomposition activity (eg. spruce) enhances decomposition processes.
10. The time course of hazel leaf decomposition in both alluvial and beech forest is sigmoidal. Three s-phases are distinguished and correspond to the activity of microflora/microfauna, mesofauna/macrofauna, and then microflora/microfauna again. In general, the sigmoidal pattern of the curve can be considered valid for all decomposition processes occurring in terrestrial situations. It is contended that no decomposition (=disappearance) curve actually follows an e-type exponential function. A logarithmic linear regression can be constructed from the sigmoid curve data and although this facilitates inter-system comparisons it does not clearly express the dynamics of decomposition.
11. The course of the curve constructed from information about the standard deviations of means derived from the From- and To-sequence data does reflect the dynamics of litter decomposition. The three s-phases can be recognised and by comparing the actual From-sequence deviation curve with a mirror inversion representation of the To-sequence curve it is possible to determine whether decomposition is primarily controlled by the duration of exposure or the date of exposure. As is the case for hazel leaf decomposition in beech forest intermediate conditions can be readily recognised.

     

长白山阔叶红松林主要树种凋落叶分解速率及其与叶性状的关系

阔叶红松林是我国东北地区地带性顶级森林群落,对维持区域生态系统稳定性具有重要作用。对阔叶红松林内主要树种凋落叶分解过程及影响因素进行研究,有助于增加长白山阔叶红松林生态系统的基础数据,为明确阔叶红松林的养分循环和物质流动提供依据。选取了长白山阔叶红松林内30个常见乔灌树种和16个凋落叶性状,采用野外分解袋法和室内样品分析等方法研究了长白山阔叶红松林内主要树种凋落叶分解速率及其与凋落叶性状的关系。1年的野外分解实验表明,30个树种的凋落叶重量损失率表现出较大差异。不同树种凋落叶的重量损失率在20.56%—92.11%之间,以红松(Pinus koraiensis)质量损失率最低,东北山梅花(Philadelphus schrenkii)质量损失率最高。不同生活型树种的凋落叶在质量损失率上存在显著差异,以灌木树种凋落叶的质量损失率最高,小乔木次之,乔木树种质量损失率最低。Olson模型拟合结果表明,不同树种凋落叶的分解速率k以红松最低,瘤枝卫矛(Euonymus verrucosus)最高,分别为0.24和1.64。不同树种分解50%和95%所需的时间分别在0.43—2.86年,1.83—...