大气N沉降的不断增加对森林生态系统的影响

若干年代以来,大气Ｎ沉降不断增加．在一些地区,大气Ｎ沉降超过了森林生态系统的Ｎ需求．Ｎ沉降的增加对植物生长的刺激作用和对菌根的危害、过剩的ＮＨ４＋在体内对其它阳离子的交换取代和在土壤中对其它阳离子在根的养分吸收方面的竞争抑制,都可造成植物体内其它养分缺乏,导致森林营养失调．Ｎ沉降的增加将提高硝化作用,加速ＮＯ３－和盐基阳离子的淋失,引起土壤酸化和Ａｌ、Ｍｎ活化．植物体内的高Ｎ水平将增加森林对寒冷、霜冻、真菌病害及可能的虫害等胁迫的敏感性．Ｎ沉降长期而持续的增加可通过干扰演替动力学,促使植物群落发生变化．     

湖北江汉平原农田生态系统Mn的循环及平衡分析

农田生态系统中 ,营养元素循环与平衡的研究已经受到许多学者的广泛关注 ,主要集中于Ｎ ,Ｐ ,Ｋ三要素的研究[1 ,2 ] 。微量元素养分循环的研究虽有一些报道[3 ,4] ,但主要集中于Ｂ和Ｚｎ元素 ,而对Ｍｎ的研究尚未见报道。微量元素Ｍｎ具有植物营养和污染危害双重作用。在我国 ,Ｍｎ肥的应用研究 ,包括肥效、施肥技术、丰缺诊断等已取得较大进展 ,Ｍｎ对环境污染及危害影响研究也取得了一些成果。随着Ｍｎ肥应用面积日益扩大 ,研究其在土壤 植物系统中循环与平衡 ,以维持Ｍｎ肥对作物适量供应 ,促进农田生态系统Ｍｎ肥的良性循环以及控制土…     

土壤有效氮及其相关因素对植物细根的影响

细根(直径≤2mm)作为植物吸收水分和养分的主要器官之一,在陆地生态系统养分循环和能量流动中起重要作用。开展土壤有效氮变化对植物细根影响研究对于了解全球气候变化条件下的陆地生态系统养分循环具有重要意义。本文就相关研究进行了综述:1)土壤有效氮变化对植物细根生长、发育、寿命及呼吸的直接影响;2)土壤质地、温度、大气CO2浓度和氮沉积等相关因素对植物细根的影响。由于研究方法及物种间差异等的影响,研究结果不尽相同。今后,应在不同空间尺度上深入研究土壤有效氮对植物细根的影响,而植物细根-土壤-微生物三者间相互关系变化对土壤氮变化的潜在响应将可能成为今后研究的热点问题之一。     

紫茎泽兰(Ageratina adenophora)入侵对土壤微生物群落和理化性质的影响

外来入侵植物与入侵地土壤微生物群落的互作关系是影响外来植物入侵力和生态系统可入侵性的一个重要领域。因此,研究外来植物入侵对入侵地土壤微生物群落及其理化性质的影响不仅可以全面地评估入侵植物对生态系统的影响,而且对于探索外来植物入侵的土壤微生物学机制尤为重要。采用磷脂脂肪酸(PLFAs)和传统培养相结合的方法研究了外来入侵植物紫茎泽兰对入侵地土壤微生物群落结构的影响;同时研究了紫茎泽兰入侵对11种土壤理化因子的影响。结果表明紫茎泽兰入侵改变了土壤微生物群落结构,提高了土壤自生固氮菌、氨氧化细菌和真菌的数量;同时,显著地提高了土壤的有效磷、速效钾、硝态氮、氨态氮和土壤有机碳含量,降低了土壤总钾含量和pH值。土壤微生物不同生理类群的变化与土壤中植物可直接吸收利用养分的变化显著相关。紫茎泽兰在入侵地成功定殖后,可能通过改变土壤微生物群落结构,特别是增加了与土壤养分循环相关的微生物功能类群数量,进而提高了土壤可利用的养分水平,创造对自身生长有利的土壤环境。紫茎泽兰改变土壤微生物群落是其入侵的一部分,这种改变进而加速了土壤养分循环,可能增强了紫茎泽兰的养分吸收,进而促进其生长、竞争和扩张。     

数种植物生物电流日周期变化观测初报

植物对养分吸收的方式分为:主动吸收、被动吸收和胞饮吸收三种^[1]。在植物体内,几乎可发现所有存在于土壤中的各种元素,这充分说明了被动吸收对植物矿质养分吸收的重要性。在矿质养分被动吸收过程中,溶于水中的离子对,以水为载体进入植物体内。土壤化学称这股荷电的离子为离子流;对植物而言,进入植物体内的这股离子流即营养流^[2]。荷电的离子流源源不断地通过根系,进入植物体内,并定向地运往地上部,这个过程表现为可检测出的植物生物电流。由此可见,植物矿质养分的被动吸收,不仅受到蒸腾作用、光合作用等耗水代谢的影响,而且还受到电磁场、太阳辐射能和月球引力作用--潮汐等大地物理诸因子的影响^[4]。因此,研究植物体生物电的变化规律,可在一定程度上较综合地反映植物对矿质养分的总体吸收情况。为此,本试验拟对数种植物生物电流日周期变化进行初步探讨。     

酸沉降影响下庐山森林生态系统土壤硫形态分布研究

近年来 ,因农业高产的养分平衡问题及因酸沉降污染问题硫的植物营养与生物地球化学研究日益活跃。至今已有较多研究者对农田和自然土壤中硫含量、形态分布及不同施肥条件和作物对它们的影响进行了研究[1,2 ,12～ 16 ] 。酸沉降影响下森林土壤硫及其去向倍受关注。研究表明 ,在高度风化的土壤上的森林生态系统中ＳＯ4 2 - 处于积累状态[17] ,而发育时间较短的土壤上的森林生态系统中ＳＯ4 2 - 则处于接近动态平衡的状态[18,19] 。Ｃａｒｌｓｓｏｎ等[2 0 ] 利用34Ｓ对挪威半岛森林土壤硫形态及其与酸沉降的关系进行了研究 ,认为有机硫和吸附…     

秸秆覆盖免耕土壤细菌和真菌生物量与活性的研究

土壤微生物生物量在土壤生态系统中具有非常重要的作用。大量的试验研究表明 ,土壤微生物生物量是植物营养元素的一个重要的源与库 ,生物量对土壤养分的调控作用 ,已经成为土壤培肥、耕作制度改革和作物栽培实践中的重要理论依据之一。自从Jenkinson提出了测定土壤微生物量的原理和概念以来 ,Jenkinson和 Powlson提出了测定微生物生物量的方法[16] ,Van De Werf和 Verstraete提出了土壤微生物生物量可以分为全微生物量和活动微生物量[10 ] ,Anderson和 Domsch提出了生物量与生物活性中细菌与真菌的比例为 2 2 /78% [8]。虽然生物量的研…     

长白松人工林生态系统营养元素的分配格局和积累规律

对长白松人工林生态系统营养元素的分配格局和积累规律研究表明,乔木层不同器官营养元素含量为叶＞枝＞根＞干皮＞干材;同化器官──针叶中养分含量为Ｎ＞Ｋ＞Ｃａ＞Ｐ＞Ｍｇ;吸收器官──根中养分含量为Ｃａ＞Ｎ＞Ｋ＞Ｐ＞Ｍｇ;人工林生态系统中的养分含量为土壤＞凋落层＞草本层＞灌木层＞乔木层,乔木层养分贮量和积累率分别为８８．７９％和７６．４３％;长白松林生态系统中植物对Ｎ、Ｐ的吸收较强烈．     

不同土壤水分状况下施硼对油菜硼吸收、利用的影响

1　引　　言我国是油菜生产大国 ,也是一个土壤缺Ｂ面积较大的国家 .由于油菜缺Ｂ问题突出 ,施用Ｂ肥已成为提高油菜产量、改善品质的重要措施[2 ,3 ,11] .但是 ,Ｂ肥的施用不但存在成本高、难度大、效率低的问题 ,而且也存在造成环境污染的可能性[9] .研究表明[8,10 ] ,不同油菜品种对缺Ｂ的反应存在基因型差异 ,因此 ,筛选、培育Ｂ营养高效基因型油菜以适应缺Ｂ土壤环境是解决油菜缺Ｂ问题的最有效途径之一 .植物对土壤中Ｂ的吸收、运输及利用因土壤水分状况而异[4 ,5] .研究不同水分条件下尤其是干旱情况下Ｂ素营养对油菜Ｂ营养效率的影…     

氮添加对森林植物磷含量的影响及其机制

氮沉降对森林生态系统磷循环产生了不可忽视的影响,尤其是加剧了植物生长的磷限制,从而使得氮沉降背景下植物磷含量变化备受关注。该文综述了氮添加对森林植物磷含量的影响,认为氮添加通过促进土壤磷酸酶活性进而提高土壤有效磷含量,有利于植物的磷吸收并增加植物磷含量。同时,森林植物磷含量对氮添加的响应还受物种、生活型以及施氮时间长短等因素的影响。基于森林植物磷含量对氮添加响应的差异性,该文进一步探讨氮富集背景下森林植物磷含量变化的可能机制:1)外源氮输入通过改变土壤中有效磷含量从而对植物磷的来源产生影响; 2)通过影响植物的根系分泌物、菌根共生和根系形态结构等进而影响植物的磷吸收能力;3)通过影响植物的磷养分再分配、磷养分重吸收对植物磷利用效率产生影响。综上所述,外源氮输入使植物磷含量发生改变,首要原因是土壤有效磷含量的改变,其次是植物磷吸收能力和磷利用效率的改变起调控作用。     

Nitrogen uptake and nitrogen use efficiency above and below ground along a topographic gradient of soil nitrogen availability

Nitrogen (N) uptake and nitrogen use efficiency (NUE) are closely related through feedback mechanisms to soil N availability and N cycling in forested ecosystems. We investigated N uptake and NUE not only at the leaf, litterfall, and aboveground levels but also belowground and whole stand levels along a topographic gradient of soil N availability in a cool temperate deciduous forest in Japan. In this study, we addressed how whole stand level N uptake and NUE affect C and N cycling in forested ecosystems. At the leaf, litterfall, and aboveground levels, N uptake decreased and NUE increased with decreasing soil N availability. This pattern resulted from decreasing leaf N concentrations and increasing N resorption efficiencies as soil N availability declined. Low N concentrations in litterfall may have resulted in little soil N being available to plants, due to microbial immobilization. In contrast, when belowground components were included, N uptake and NUE were not correlated with soil N availability. This was mainly due to higher levels of fine root production when soil N availability was low. Higher fine root allocation can result in a high input of detritus to decomposer systems and, thus, contribute to accumulation of soil organic matter and immobilization by microbes, which may result in further soil N availability decline. Our results suggest that allocation to the fine root rather than whole stand level NUE is important for C and N cycling in forested ecosystems, as is the feedback mechanism in which litterfall level NUE shifts with changes in the N concentration of litterfall.     

氮稳定同位素技术在陆地生态系统氮循环研究中的应用

在过去几十年中, 氮(N)稳定同位素技术的发展提高了人们对于陆地生态系统氮循环的认识。该文回顾了氮稳定同位素技术在研究生态系统氮循环中的历史, 综述了最近十多年来氮稳定同位素技术在陆地生态系统氮循环研究中的典型案例, 包括利用氮同位素自然丰度鉴定植物氮来源、指示生态系统氮状态和量化过程速率, 利用¹⁵N标记技术示踪氮的去向和再分布等。该文同时指出这些应用中存在的问题, 以及在陆地生态系统上氮稳定同位素技术今后研究的重点发展方向。     

采伐和火烧对森林氮动态的影响

森林是重要的陆地生态系统类型,它通过特有的养分循环机制维持其结构和功能.其中氮素对林木生长和发育十分重要,而且常是森林生产力的限制因素.另一方面,森林氮动态又常受到人类活动干扰的影响.根据国内外研究结果综述了采伐和火烧对森林氮动态的影响.结果表明采伐后环境因素的变化将影响森林N动态,其中最为关注的是采伐后一系列因素引起的N损失,如:N淋溶增加、伴随生物量的N迁移以及因径流或侵蚀增加造成的枯枝落叶层和土壤层N流失.这些N损失又将影响更新林分的生长和生产力.此外,采伐后N吸收速率一般下降,但随着植被快速生长N吸收速率将不断增加.采伐后氨化和硝化过程增强,但因短期内同化作用较弱,生态系统中大部分N将发生损失.火烧对森林N动态的短期影响主要包括:第一,火烧时N直接挥发损失;第二,火烧后N有效性增加,这主要由灰分沉积、根和微生物死亡及有机质N矿化增强等综合造成.随着时间延长,N有效性逐渐降低,这可能与火烧引起的有机质损失、植物N吸收增加、淋溶或侵蚀损失有关.然而,目前关于火烧造成的长期生态影响,如火烧后地上植被恢复与地下生物地球化学过程变化有何联系仍不太清楚.未来研究应着重于探讨氮素对森林采伐和火烧作出的短期响应将如何长期影响森林的结构和功能.此外,建议在实施营林方案时需考虑采伐和火烧对生态系统氮的影响.     

Nitrogen balance in forest soils: nutritional limitation of plants under climate change stresses

Forest ecosystems with low soil nitrogen (N) availability are characterized by direct competition for this growth-limiting resource between several players, i.e. various components of vegetation, such as old-growth trees, natural regeneration and understorey species, mycorrhizal fungi, free-living fungi and bacteria. With the increase in frequency and intensity of extreme climate events predicted in current climate change scenarios, also competition for N between plants and/or soil microorganisms will be affected. In this review, we summarize the present understanding of ecosystem N cycling in N-limited forests and its interaction with extreme climate events, such as heat, drought and flooding. More specifically, the impacts of environmental stresses on microbial release and consumption of bioavailable N, N uptake and competition between plants, as well as plant and microbial uptake are presented. Furthermore, the consequences of drying–wetting cycles on N cycling are discussed. Additionally, we highlight the current methodological difficulties that limit present understanding of N cycling in forest ecosystems and the need for interdisciplinary studies.     

Fire effects on ecosystem nitrogen cycling in a Californian bishop pine forest

Fire can cause severe nitrogen (N) losses from grassland, chaparral, and temperate and boreal forest ecosystems. Paradoxically, soil ammonium levels are markedly increased by fire, resulting in high rates of primary production in re-establishing plant communities. In a manipulative experiment, we examined the influence of wild-fire ash residues on soil, microbial and plant N pools in a recently burned Californian bishop pine (Pinus muricata D. Don) forest. Ash stimulated post-fire primary production and ecosystem N retention through direct N inputs from ash to soils, as well as indirect ash effects on soil N availability to plants. These results suggest that redistribution of surface ash after fire by wind or water may cause substantial heterogeneity in soil N availability to plants, and could be an important mechanism contributing to vegetation patchiness in fire-prone ecosystems. In addition, we investigated the impact of fire on ecosystem N cycling by comparing ¹⁵N natural abundance values from recently burned and nearby unburned P. muricata forest communities. At the burned site, ¹⁵N natural abundance in recolonising species was similar to that in bulk soil organic matter. By contrast, there was a marked ¹⁵N depletion in the same species relative to the total soil N pool at the unburned site. These results suggest that plant uptake of nitrate (which tends to be strongly depleted in ¹⁵N because of fractionation during nitrification) is low in recently burned forest communities but could be an important component of eco- system N cycling in mature conifer stands. Received: 29 June 1999 / Accepted: 24 October 1999     

Nitrogen Cycling Responses to Mountain Pine Beetle Disturbance in a High Elevation Whitebark Pine Ecosystem

Ecological disturbances can significantly affect biogeochemical cycles in terrestrial ecosystems, but the biogeochemical consequences of the extensive mountain pine beetle outbreak in high elevation whitebark pine (WbP) (Pinus albicaulis) ecosystems of western North America have not been previously investigated. Mountain pine beetle attack has driven widespread WbP mortality, which could drive shifts in both the pools and fluxes of nitrogen (N) within these ecosystems. Because N availability can limit forest regrowth, understanding how beetle-induced mortality affects N cycling in WbP stands may be critical to understanding the trajectory of ecosystem recovery. Thus, we measured above- and belowground N pools and fluxes for trees representing three different times since beetle attack, including unattacked trees. Litterfall N inputs were more than ten times higher under recently attacked trees compared to unattacked trees. Soil inorganic N concentrations also increased following beetle attack, potentially driven by a more than two-fold increase in ammonium (NH₄ ⁺) concentrations in the surface soil organic horizon. However, there were no significant differences in mineral soil inorganic N or soil microbial biomass N concentrations between attacked and unattacked trees, implying that short-term changes in N cycling in response to the initial stages of WbP attack were restricted to the organic horizon. Our results suggest that while mountain pine beetle attack drives a pulse of N from the canopy to the forest floor, changes in litterfall quality and quantity do not have profound effects on soil biogeochemical cycling, at least in the short-term. However, continuous observation of these important ecosystems will be crucial to determining the long-term biogeochemical effects of mountain pine beetle outbreaks.     

Nitrogen oligotrophication in northern hardwood forests

While much research over the past 30 years has focused on the deleterious effects of excess N on forests and associated aquatic ecosystems, recent declines in atmospheric N deposition and unexplained declines in N export from these ecosystems have raised new concerns about N oligotrophication, limitations of forest productivity, and the capacity for forests to respond dynamically to disturbance and environmental change. Here we show multiple data streams from long-term ecological research at the Hubbard Brook Experimental Forest in New Hampshire, USA suggesting that N oligotrophication in forest soils is driven by increased carbon flow from the atmosphere through soils that stimulates microbial immobilization of N and decreases available N for plants. Decreased available N in soils can result in increased N resorption by trees, which reduces litterfall N input to soils, further limiting available N supply and leading to further declines in soil N availability. Moreover, N oligotrophication has been likely exacerbated by changes in climate that increase the length of the growing season and decrease production of available N by mineralization during both winter and spring. These results suggest a need to re-evaluate the nature and extent of N cycling in temperate forests and assess how changing conditions will influence forest ecosystem response to multiple, dynamic stresses of global environmental change.     

氮磷添加对树木生长和森林生产力影响的研究进展

人为活动所导致的氮、磷输入和大气氮、磷沉降使生态系统中的氮、磷可利用性大幅提高, 对陆地生态系统的碳循环过程产生了显著影响。树木生长和森林生产力在全球碳循环中发挥着重要作用, 它决定着陆地碳固存的大小和方向。目前, 在全球范围内开展了很多氮、磷添加调控树木生长和森林生产力的野外控制实验, 但是研究结果并不一致, 受到多种生物、环境和实验处理条件等因素的影响。该文从野外氮添加和磷添加实验的文献数量、实验数量及其全球空间分布三个方面概述了氮、磷添加对树木生长和森林生产力影响的研究现状, 并总结了氮、磷添加实验中树木生长和森林生产力的评估方法, 包括相对生长速率和绝对增长量。基于相关的研究结果, 阐述了氮、磷添加影响树木生长和森林生产力的调控因素及其潜在影响机制, 包括气候、树木径级与林龄、植物功能性状(共生菌根类型、树木固氮属性和保守性与获得性性状)、植物和微生物相互作用关系、区域养分沉降速率和实验处理条件等。最后, 基于当前的研究进行了系统总结, 并指出今后需要加强的几个方面的研究, 以期为后续研究提供参考: 树木生长响应氮、磷添加的生理学机制, 树木各部分生长对氮、磷添加响应的权衡与分配, 植物功能性状在调节与预测树木生长响应氮、磷添加中的作用, 树木之间的竞争关系如何调控氮、磷添加对树木生长的影响, 以及开展长期的和联网的氮、磷添加对树木生长和森林生产力影响的野外控制实验。     

A review on the effects of nitrogen and phosphorus addition on tree growth and productivity in forest ecosystems

Nitrogen (N) and phosphorus (P) inputs induced by anthropogenic activities and atmospheric N and P deposition have largely increased the availability of soil N and P in terrestrial ecosystems, which have considerably affected terrestrial carbon cycling processes. Tree growth and productivity in forest ecosystems play an important role in global carbon cycling, and determine the magnitude and direction of terrestrial carbon sequestration. Currently, a large number of field manipulation experiments have been conducted to investigate the effects of N and/or P addition on tree growth and forest productivity, but the results from these studies were inconsistent. Such inconsistent results might be affected by multiple factors, including biological, environmental and experimental variables. Here, we reviewed the present research status of the effects of N and P addition on tree growth and forest productivity in forest ecosystems based on three aspects, including the number of publications and experiments with field N and P addition, and the global distributions of these experiments. Then, we summarized the methods for assessing tree growth and forest productivity at ecosystem level in forest ecosystems, including relative growth rate and absolute increment. According to the related results, we reviewed the regulating factors that affect tree growth and productivity, and the potential mechanisms for such factors, including climate, tree size and stand age, plant functional traits (including type of tree-associated mycorrhizal fungi, N-fixation property of trees, and conservative and acquisitive functional traits), plant-microbe interaction, ambient nutrient (i.e., N and P) deposition rate, and experimental variables. Finally, we summarized the current studies, and pointed out five aspects that are urgently needed to provide further insights in future studies, including the physiological mechanism of how tree growth responds to N and P addition, the tradeoff and allocation among growth of various parts of tree under N and P addition, the role of plant functional traits in regulating and predicting the responses of tree growth to N and P addition, how the competition among trees regulates the responses of tree growth to N and P addition, and conducting long-term and coordinated distributed field experiments investigating the effects of N and P addition on tree growth and forest productivity at the global scale.     

矿质养分输入对森林生物固氮的影响

生物固氮是森林生态系统重要的氮素来源,并且在全球氮循环中占有重要的地位。近代以来,因人类活动加剧而导致氮沉降的增加以及其它矿质养分元素(如磷、钼、铁等)输入的改变已成为影响森林生态系统生物固氮的重要因素之一,并引起了学术界的普遍关注。综述了国内外关于森林生物固氮对矿质养分输入的响应及机理。主要内容包括:(1)森林生物固氮的概念及主要的测定方法;(2)矿质养分输入对森林生物固氮的影响。整体上讲,氮素输入抑制了森林生物固氮,磷和其他营养元素输入则表现为促进作用。氮和磷、磷和微量元素同时添加均提高了森林的固氮量;(3)矿质养分改变森林生物固氮的机理。包括生物作用机制(如改变地表层固氮菌的数量或群落丰度、改变结瘤植物的根瘤生物量和附生植物的丰度或盖度)和环境作用机制(如引起土壤酸化、改变碳源物质的含量);(4)探讨了矿质养分输入对森林生物固氮影响研究中所存在的问题,并对未来该领域的研究提出建议。