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1.
为探明高原草甸土壤微生物对短期氮沉降的响应,以纳帕海典型高寒草甸云雾薹草群落为对象,野外原位布设低氮(5 g N·m-2·a-1)、中氮(10 g N·m-2·a-1)和高氮(15 g N·m-2·a-1)3种施氮处理,研究氮沉降引起高寒草甸植物多样性及土壤性质变化对微生物生物量碳氮的影响。结果表明:氮添加显著增加土壤微生物生物量碳氮及其熵值,中氮处理下微生物生物量碳增量最高,达139.3%;微生物生物量碳氮的垂直变化表现为沿土层显著降低,降幅为24.1%~75.1%。氮添加显著提高群落地上生物量,降低Shannon和Simpson多样性,变幅达6.6%~65.4%;氮添加显著降低土壤pH,增加土壤有机质、全氮、铵态氮和硝态氮含量,且在中氮处理下变幅(7.0%~511.1%)最大;土壤pH随土层加深而增大,而其他理化指标则沿土层加深而显著减少,变幅达19.5%~91.2%。结构方程模型表明,土壤铵态氮、硝态氮和有机质对微生物生物量起促进作用,而土壤pH和植...  相似文献   

2.
为了探讨古田山地区5个树种—秃瓣杜英(Elaeocarpus glabripetalus)、枫香(Liquidambar formosana)、木荷(Schima superba)、青冈(Cyclobalanopsis glauca)和马尾松(Pinus massoniana)幼苗的生长和生物量及其分配对添加氮肥和减少降水的响应, 在野外设置了双因素氮肥(对照和施氮)和降水(自然降水(对照)和减少降水)控制试验, 氮肥的施入量为10 g·m-2·a-1 NH4NO3, 分别于每年5月初和7月初各施5 g·m-2·a-1, 减少降水处理是减少自然降水的30%。经过3个生长季的处理发现: 1)施氮显著促进了秃瓣杜英、枫香和木荷的苗高和基径的生长, 并且对秃瓣杜英和枫香的促进作用经过1个生长季的处理就表现出来, 而木荷在经过2个生长季后才表现出来; 2)施氮显著促进了秃瓣杜英、枫香和木荷的全株生物量以及各部分生物量的增长, 而只增加了马尾松的侧枝和叶片生物量以及青冈的侧枝生物量; 3) 2个生长季的施氮处理提高了秃瓣杜英和木荷的叶重比以及枫香和青冈的枝重比, 3个生长季的施氮处理促进了秃瓣杜英、枫香和木荷的茎重比以及青冈和马尾松的枝重比, 地上干物质分配比例的增加以地下干物质分配比例减小为代价, 施氮后显著降低了秃瓣杜英、枫香、木荷和青冈的根重比和根冠比; 4) 降水减少30%对各树种的生长均无显著影响。  相似文献   

3.
以黄土丘陵区草地植被群落3种优势种白羊草、长芒草和达乌里胡枝子为对象,采用裂区试验设计,设置0、50和100 kg N·hm-2·a-13个氮处理和0、40和80 kg P2O5·hm-2·a-1 3个磷处理,于生长旺盛期测定了各植物的叶长、叶宽、比叶面积、叶片干物质含量、叶片氮、磷含量和氮磷比等指标,分析不同优势种叶片功能性状对氮磷添加的响应差异.结果表明:与未施肥相比,50和100 kg N·hm-2·a-1处理下白羊草叶长和叶宽分别显著增加35.3%和64.4%,而长芒草仅有叶长显著增加58.8%,达乌里胡枝子仅有叶宽显著增加33.9%,但三者叶片干物质含量分别显著降低10.7%、15.3%和11.2%,白羊草和长芒草叶片氮含量分别显著增加23.0%和99.2%,氮磷比分别显著增加45.8%和96.9%;40和80 kg P2O5·hm-2·a-1处理下达乌里胡枝子叶长、叶宽和比叶面积分别显著增加56.9%、41.4%和19.6%,叶片干物质含量显著下降14.9%,三者叶片磷含量分别显著增加96.7%、110.9%和238.4%,氮磷比分别显著降低45.8%、42.8%和53.7%.50 kg N·hm-2·a-1处理下,与未施磷相比,40和80 kg P2O5·hm-2·a-1处理后仅达乌里胡枝子叶长和叶宽显著增大,3种植物叶片磷含量显著增加,白羊草和长芒草叶片氮含量显著降低;100 kg N·hm-2·a-1处理下,施磷后白羊草和长芒草叶长、达乌里胡枝子叶宽显著增大,三者叶片磷含量显著增加,白羊草叶片氮含量显著降低.综上表明,3个优势种植物叶片功能性状对短期氮磷添加的响应存在明显差异,这些差异与物种属性和施肥水平有关,不同优势种对氮磷添加响应的差异对维持草地群落多样性和稳定性具有重要作用.  相似文献   

4.
为理解模拟氮沉降对华西雨屏区天然常绿阔叶林土壤微生物生物量碳(MBC)和氮(MBN)的影响,通过一年野外模拟氮(NH4NO3)沉降试验,氮沉降水平分别为对照(CK, 0 g N·m-2·a-1)、低氮沉降(L, 5 g N·m-2·a-1)、中氮沉降(M, 15 g N·m-2·a-1)和高氮沉降(H, 30 g N·m-2·a-1),研究了氮沉降对天然常绿阔叶林土壤MBC和MBN的影响.结果表明: 氮沉降显著降低了0~10 cm土层MBC和MBN,且随氮沉降量的增加,下降幅度增大;L和M处理对10~20 cm土层MBC和MBN无显著影响,H处理显著降低了10~20 cm土层土壤MBC和MBN;氮沉降对MBC和MBN的影响随土壤深度的增加而减弱.MBC和MBN具有明显的季节变化,在0~10和10~20 cm土层均表现为秋季最高,夏季最低.0~10和10~20 cm土层土壤微生物生物量C/N分别介于10.58~11.19和9.62~12.20,表明在华西雨屏区天然常绿阔叶林土壤微生物群落中真菌占据优势.  相似文献   

5.
为探究氮沉降增加背景下高寒草甸土壤呼吸干湿季变化及其与环境因子的耦合关系,选择纳帕海典型退化草甸疏花早熟禾群落,设置对照(0 g·m-2·a-1)、低氮(5 g·m-2·a-1)、中氮(10 g·m-2·a-1)和高氮(15 g·m-2·a-1)4个水平的氮沉降模拟试验,分析氮沉降引起的地上生物量、植物多样性及土壤理化性质变化对土壤呼吸的影响。结果表明:不同氮沉降处理均显著促进草甸土壤呼吸,干季和湿季土壤呼吸速率相较于对照分别增加了21.9%~53.9%和27.3%~51.2%,且在中氮处理下增幅最大。氮沉降显著提升草甸地上生物量(增幅达52.2%~66.4%);植物多样性随氮添加总体呈降低趋势,湿季最大降幅(13.5%~24.2%)出现在高氮处理。氮沉降显著增加土壤铵态氮、有机质、微生物生物量碳氮、温度和含水率(增幅为14.3%~333.5%),氮沉降显著降低土壤pH(减幅达9.0%~34.6%)。结构方程表明...  相似文献   

6.
为阐明南亚热带4个主要树种——海南红豆(Ormosia pinnata)、马占相思(Acacia mangium)、木荷(Schima superba)和马尾松(Pinus massoniana)幼苗生长对不同氮添加量和添加方式的响应差异, 进行了幼苗模拟氮添加实验。实验设置3个氮添加水平(对照: 背景大气氮沉降量5.6 g N·m-2·a-1, 中氮: 15.6 g N·m-2·a-1, 高氮: 20.6 g N·m-2·a-1), 每个水平分两种添加方式(幼苗冠层施氮和土壤表层施氮), 共6个处理: (1)土壤对照(S-CK); (2)土壤中氮(S-MN); (3)土壤高氮(S-HN); (4)冠层对照(C-CK); (5)冠层中氮(C-MN); (6)冠层高氮(C-HN), 每个处理设置6个重复。研究结果表明: 不同氮添加量下, 土壤施氮和冠层施氮对植物幼苗生长的影响不同, 氮添加量、氮添加方式和物种3个因子之间存在显著的交互效应。与对照相比, S-MN增加了马占相思和木荷幼苗的生物量, 降低了马尾松的株高和生物量, 而C-MN仅增加了马占相思的生物量, 对其他3个树种没有影响; S-HN增加了马占相思的生物量, 显著降低了马尾松的基径、株高和生物量(p < 0.01), C-HN增加了马占相思、木荷和马尾松的基径、株高和生物量(p < 0.01)。不同氮添加量和氮添加方式对幼苗生长的影响因物种而异, 所有氮处理下海南红豆和马占相思的生长均明显快于木荷和马尾松; 木荷和马尾松幼苗的生长在两种氮添加方式间差异显著, 冠层施氮比土壤施氮对其幼苗生长的促进作用更大。由此可见: 在氮沉降背景下, 阔叶豆科植物(海南红豆、马占相思)比阔叶非豆科植物(木荷)生长快; 阔叶树种(海南红豆、马占相思和木荷)比针叶树种(马尾松)生长快。在长期氮沉降环境下, 不同物种生长的差异响应有可能导致亚热带森林物种组成发生变化。  相似文献   

7.
在目前全球氮沉降不断增加的背景下, 研究农田土壤呼吸对氮沉降的响应有助于理解未来生态系统碳循环对全球变暖的潜在影响。为探讨不同施氮浓度对华东地区冬小麦(Triticum aestivum)生长期土壤呼吸的影响, 该实验设计了对照组(不施加氮肥)和3种浓度施氮处理组(低浓度施氮15 g·m-2·a-1, 中等浓度施氮30 g·m-2·a-1, 高浓度施氮45 g·m-2·a-1)。使用便携式土壤CO2通量观测仪LI-8100测定不同施氮浓度处理下冬小麦生长期(2013年12月至2014年5月)的土壤呼吸速率, 并探讨土壤呼吸与土壤温度、湿度等环境因素的关系。结果表明: 低、中、高3种浓度施氮处理的土壤呼吸速率平均值分别为5.29、6.17和6.75 μmol·m-2 ·s-1, 与对照组(土壤呼吸速率平均值为4.90 μmol·m-2·s-1)相比, 分别增加了7.8%、23.6%和37.8%; 地上生物量分别增加39.9%、104.4%和200.2%, 并与冬小麦生长季的总土壤呼吸正相关。5 cm深度土壤的温度与土壤呼吸速率呈指数关系(p < 0.05), 土壤呼吸季节变化的65%-75%由土壤温度引起, 其温度敏感性为2.09-2.32。结果表明, 添加氮肥促进了植物的生长, 增加了生物量, 从而增加了冬小麦农田的土壤呼吸速率。  相似文献   

8.
为探究氮添加对濒危植物东北红豆杉幼苗生长-防御权衡的影响,为该物种的保护工作提供理论依据,本研究以东北红豆杉4年生幼苗为对象,进行了3种氮源(硫酸铵、硝酸铵和硝酸钾)和4个施氮量(30、60、90、120 kg N·hm-2·a-1)的氮添加实验。结果表明:(1)东北红豆杉幼苗的苗高增长量、地径增长量和总生物量随施氮量增加显著增加,施氮量超过90 kg N·hm-2·a-1后地径增长量和总生物量开始下降,施氮处理的幼苗根冠比显著低于对照组,但在不同施氮量下无显著差异;(2)净光合速率(Pn)和气孔导度在氮添加处理后显著提高,在施氮量为90 kg N·hm-2·a-1时达峰值,胞间CO2浓度与Pn的变化方向相反,说明氮添加可以缓解植物的非气孔限制;(3)黄酮类化合物含量在施氮后呈现先增高后降低的趋势,施氮量30 kg N·hm-2·a-1为转折点;(...  相似文献   

9.
华西雨屏区苦竹林土壤呼吸对模拟氮沉降的响应   总被引:15,自引:2,他引:13       下载免费PDF全文
2007年11月至2008年11月, 对华西雨屏区苦竹(Pleioblastus amarus)人工林进行了模拟氮沉降试验, 氮沉降水平分别为对照(CK, 0 g N·m-2·a-1)、低氮(5 g N·m-2·a-1)、中氮(15 g N·m-2·a-1)和高氮(30 g N·m-2·a-1)。每月下旬, 采用红外CO2分析法测定土壤呼吸速率, 并定量地对各处理施氮(NH4NO3)。结果表明: 2008年试验地氮沉降量为8.241 g·m-2, 超出该地区氮沉降临界负荷。在生长季节, 苦竹林根呼吸占总土壤呼吸的60%左右。模拟氮沉降促进了苦竹林土壤呼吸速率, 使苦竹林土壤每年向大气释放的CO2增加了9.4%~28.6%。在大时间尺度上(如1 a), 土壤呼吸主要受温度的影响。2008年6~10月, 土壤呼吸速率24 h平均值均表现为: 对照<低氮<中氮<高氮。氮沉降处理1 a后, 土壤微生物呼吸速率和土壤微生物生物量碳、氮增加, 并且均与氮沉降量具有相同趋势。各处理土壤呼吸速率与10 cm土壤温度、月平均气温呈极显著指数正相关关系, 利用温度单因素模型可以解释土壤呼吸速率的大部分。模拟氮沉降使得土壤呼吸Q10值增大, 表明氮沉降可能增强了土壤呼吸的温度敏感性。在氮沉降持续增加和全球气候变暖的背景下, 氮沉降和温度的共同作用可能使得苦竹林向大气中排放的CO2增加。  相似文献   

10.
在青藏高原高寒草甸区设置模拟增温和氮添加处理,研究长期增温与外源氮输入对高寒草甸群落生产及其分配的影响.结果表明:开顶箱增温装置造成小环境暖干化,即显著提高地表空气温度1.6℃,提高表层土壤温度1.4℃,降低土壤含水量4.7%.2012、2013和2014年不施氮处理下增温分别降低地上生物量61.5%、108.8%和77.1%,在高氮(40和80kg N·hm-2·a-1)处理下增温对群落地上生物量无显著影响,这说明增温的影响依赖于氮添加水平,且施氮补偿了增温导致的土壤氮损失.增温导致根冠比增加,2012、2013和2014年不施氮处理下增温分别增加根冠比98.6%、60.7%和97.8%.在不增温处理下,植物群落地上、地下生物量的变化率均表现出低氮(10、20 kg N·hm-2·a-1)促进、高氮抑制的趋势,达到饱和阈值时的氮添加剂量分别为56.0和55.5 kg N·hm-2·a-1;而在增温处理下,地上、地下生物量随施氮量增加呈线性增加趋势.这说明增温改变了高寒草甸生物量分配对外源氮输入的响应模式,增温导致的土壤无机氮含量变化是生物量分配模式改变的主要原因.由氮添加试验估算的高寒草甸氮饱和阈值表明,高寒草甸对氮输入的敏感性高于其他类型草地.  相似文献   

11.
《植物生态学报》2017,41(10):1041
Aims Fine roots are the principal parts for plant nutrients acquisition and play an important role in the underground ecosystem. Increased nitrogen (N) deposition has changed the soil environment and thus has a potential influence on fine roots. The purpose of this study is to reveal the effect of N deposition on biomass, lifespan and morphology of fine root.Methods A field N addition experiment was conducted in a secondary broad-leaved forest in subtropical China from May 2013 to September 2015. Three levels of N treatments: CK (no N added), LN (5 g·m-2·a-1), and HN (15 g·m-2·a-1) were applied monthly. Responses of fine root biomass, lifespan, and morphology of Castanopsis platyacantha to N addition were analyzed by using a minirhizotron image system from April 2014 to September 2015. Surface soil sample (0-10 cm) was collected in November 2014 and soil pH value, and concentrations of NH4+-N and NO3--N were measured.Important findings The biomass and average lifespan of the fine roots of C. platyacantha were 128.30 g·m-3 and 113-186 days, respectively, in 0-45 cm soil layer. Nitrogen addition had no significant effect on either fine root biomass or lifespan in 0-45 cm soil layer. However, LN treatment significantly decreased C. platyacantha root superficial area in 0-15 cm soil layer. HN treatment significantly decreased soil pH value. Our study indicated that short-term N addition influences soil inorganic N concentration and thus decreased pH value in surface soil, and thereafter affect fine root morphology. Short-term N addition, however, did not affect the fine root biomass, lifespan and morphology in subsoil.  相似文献   

12.
《植物生态学报》2016,40(10):980
Aims Irrational utilization and global climate change have caused degradation of grassland ecosystems in northern China with low soil fertility, decreased vegetation coverage and productivity. Nitrogen addition has been suggested an effective way to enhance restoration of those degraded grasslands. In this study, we selected a typical steppe with three different degrading levels, including lightly, moderately and heavily degraded communities, in East Ujimqin, Nei Mongol. Our objectives of this study are to examine if and how nitrogen (N) addition can enhance restoration of those degraded grasslands Methods Treatments with four levels of N addition (0, 5.0, 10.0 and 20.0 g N·m-2·a-1) were conducted to each of the three degraded communities from 2014 to 2015. Nitrogen was applied as urea in June of both years. Aboveground biomass was collected at the species level in 1 m × 1 m plot in August each year, all species biomass was summed as net primary production, and biomass of plant functional groups was calculated by perennial rhizome grasses, perennial bunchgrasses, perennial forbs, shrubs and semi-shrubs, annuals and biennials.Important findings Our results showed that the high (20.0 g N·m-2·a-1) and medium level N addition (10.0 g N·m-2·a-1) significantly increased the aboveground biomass of the slightly degraded community by 53.1% and 51.6% compared with no N addition. N addition had no significant effects on the moderately and heavily degraded communities. N addition with high and medium levels increased aboveground biomass of perennial rhizome grasses by 45.1% and 47.7%, but decreased that of perennial forbs by 37.4% and 42.1% at the slightly degraded community. Our results indicated that N addition could increase the growth of perennial rhizome grasses, and the growth of perennial forbs was suppressed consequently. Our results suggest that even the application of N fertilizers can only be helpful to restoration of those slightly degraded grasslands. Besides, N addition had no significant effects on species richness in different degraded communities indicating the fact that the study may not last long enough. For the purpose of increasing aboveground biomass of degraded grassland, we should not only consider the type and quantity of fertilization, but also the attribute of the degraded communities. In addition, the response of degraded community in biomass may strongly be impacted by degrading level of studied grassland.  相似文献   

13.
Aims As the second largest C flux between the atmosphere and terrestrial ecosystems, soil respiration plays a vital role in regulating atmosphere CO2 concentration. Therefore, understanding the response of soil respiration to the increasing nitrogen deposition is urgently needed for prediction of future climate change. However, it is still unclear how nitrogen deposition influences soil respiration of shrubland in subtropical China. Our objectives were to explore the effects of different levels of nitrogen fertilization on soil respiration, root biomass increment, and litter biomass, and to analyze the relationships between soil respiration and soil temperature and moisture.
Methods From January 2013 to September 2014, we conducted a short-term simulated nitrogen deposition experiment in the Rhododendron simsii shrubland of Dawei Mountain, located in Hunan Province, southern China. Four levels of nitrogen addition treatments (each level with three replicates) were established: control (CK, no nitrogen addition), low nitrogen addition (LN, 2 g·m-2·a-1), medium nitrogen addition (MN, 5 g·m-2·a-1) and high nitrogen addition (HN, 10 g·m-2·a-1). Soil respiration was measured by LI-8100 soil CO2 efflux system. At the same time, we measured root biomass increment and litter biomass in each plot.
Important findings Soil respiration exhibited a strong seasonal pattern, with the highest rates found in summer and the lowest rates in winter. Annual accumulative soil respiration rate in the CK, LN, MN and HN was (2.37 ± 0.39), (2.79 ± 0.42), (2.26 ± 0.38) and (2.30 ± 0.36) kg CO2·m-2, respectively. Annual mean soil respiration rate in the CK, LN, MN and HN was (1.71 ± 0.28), (2.01 ± 0.30), (1.63 ± 0.27) and (1.66 ± 0.26) μmol CO2·m-2·s-1, respectively, and it was 17.25% higher in the LN treatment compared with CK (p = 0.06). The root biomass increment was increased by LN, MN, and HN treatments by 18.36%, 36.49% and 61.63%, respectively, compared to CK. The litter biomass was increased by LN, MN, and HN treatments by 35.87%, 22.17% and 15.35%, respectively, compared with CK. Soil respiration exhibited a significant exponential relationship with soil temperature (p < 0.01, R2 is 0.77 to 0.82) and a significant linear relationship with soil moisture at the depth of 5 cm (p < 0.05, R2 is 0.10 to 0.15). The temperature sensitivity (Q10) value of CK, LN, MN and HN plots was 3.96, 3.60, 3.71 and 3.51, respectively. These results suggested that nitrogen addition promoted plant growth and decreased the temperature sensitivity of soil respiration. The increase of root biomass under N addition may be an important reason for the change of soil respiration in the study area.  相似文献   

14.
氮富集会影响到全球生态系统的植物生长繁殖和土壤理化性质.然而,目前关于氮富集对潮汐湿地生态系统植物生长和土壤理化性质的影响研究相对较少.通过氮添加野外控制实验,研究了4个氮添加水平(CK:0 g·m-2·a-1、N1:5 g·m-2·a-1、N2:20 g·m-2·a-1、N3:50 g·m-2·a-1)对黄河三角洲高...  相似文献   

15.
土壤养分异质性是竹林-阔叶林界面(bamboo and broad-leaved forest interface, 以下简称竹阔界面)的重要特征, 细根生长、周转和分解影响土壤养分供应能力, 但其在竹阔界面养分异质性形成中的贡献尚不清楚。该文选取竹阔界面两侧的毛竹(Phyllostachys pubescens)林和常绿阔叶林为研究对象, 开展土壤养分(C、N、P)含量、细根生物量及周转、细根分解及养分回归等指标的对比研究。结果表明: (1)竹阔界面两侧毛竹林和常绿阔叶林土壤养分差异明显, 毛竹林0-60 cm土壤有机碳(SOC)和土壤总氮(STN)含量分别为20.51和0.53 g·kg-1, 常绿阔叶林0-60 cm土壤有机碳(SOC)和土壤总氮(STN)含量分别为13.42和0.26 g·kg-1, 前者比后者分别高出34.53%和50.35%, 但毛竹林土壤全磷(STP)含量低于常绿阔叶林25.54%; (2)竹阔界面两侧细根生物量、养分密度及养分回归量差异明显, 毛竹林细根生物量高达1201.60 g·m-2, 是常绿阔叶林的5.86倍; 养分密度分别为591.42 g C·m-2、5.44 g N·m-2、0.25 g P·m-2, 分别是常绿阔叶林的6.12倍、3.77倍和3.11倍; 年均养分回归量分别为278.54 g C·m-2·a-1、2.36 g N·m-2·a-1、0.11 g P·m-2·a-1, 是常绿阔叶林的6.93倍、4.29倍和3.67倍; (3)细根对界面两侧土壤SOC、STN异质性形成的年均潜在贡献分别为76.79%和28.33%, 但对STP异质性形成起减缓作用, 贡献率为6.17%。这些结果说明毛竹扩张可以改变常绿阔叶林土壤的养分状况, 且细根对不同养分的异质性形成贡献不一致, 是土壤SOC、STN异质性形成的重要原因。  相似文献   

16.
植物叶片氮(N)、磷(P)养分特征受土壤可利用性N、P含量和N、P相对比例(N:P)的共同影响, 研究其作用机制有助于解释和评估土壤养分变化对植物养分利用策略的影响。该研究通过盆栽实验, 探讨芨芨草(Achnatherum splendens)养分化学计量学特征和叶片养分回收特征对不同剂量的养分添加(低、中、高3个N添加水平: 1.5、4.5、13.5 g·m-2·a-1)及不同土壤N:P (5、15、25)的响应。结果表明: 养分添加水平的提高显著增加了成熟叶片P含量和衰老叶片N、P含量, 显著降低了叶片N、P养分回收效率(NRE, PRE)。土壤N:P的升高显著降低了衰老叶片P含量和叶片NRE, 但增加了成熟和衰老叶片N:P和叶片PRE。相同养分添加水平条件下, 土壤N:P与叶片PRE显著正相关, 但与叶片NRE无显著相关性; 相同N:P条件下, 养分添加水平与NRE负相关, 但与PRE无显著相关性。植物NRE:PRE可以有效地反映环境变化所导致的植物对N、P需求的改变。土壤养分添加水平和N:P共同影响着芨芨草的叶片养分生态化学计量学特征和养分回收。  相似文献   

17.
Aims The shrublands of northern China have poor soil and nitrogen (N) deposition has greatly increased the local soil available N for decades. Shrub growth is one of important components of C sequestration in shrublands and litterfall acts as a vital link between plants and soil. Both are key factors in nutrient and energy cycling of terrestrial ecosystems, which greatly affected by nitrogen (N) addition (adding N fertilizer to the surface soil directly). However, the effects and significance of N addition on C sequestration and litterfall in shrublands remain unclear. Thus, a study was designed to investigate how N deposition and related treatments affected shrublands growth related to C sequestration and litterfall production of Vitex negundo var. heterophylla and Spiraea salicifolia in Mt. Dongling region of China.
Methods A N enrichment experiment has been conducted for V. negundo var. heterophylla and S. salicifolia shrublands in Mt. Dongling, Beijing, including four N addition treatment levels (control (N0, 0 kg N·hm-2·a-1), low N (N1, 20 kg N·hm-2·a-1), medium N (N2, 50 kg N·hm-2·a-1) and high N (N3, 100 kg N·hm-2·a-1)). Basal diameter and plant height of shrub were measured from 2012-2013 within all treatments, and allometric models for different species of shrub’s live branch, leaf and root biomass were developed based on independent variables of basal diameter and plant height, which will be used to calculate biomass increment of shrub layer. Litterfall (litterfall sometimes is named litter, referring to the collective name for all organic matter produced by the aboveground part of plants and returned to the surface, and mainly includes leaves, bark, dead twigs, flowers and fruits.) also was investigated from 2012-2013 within all treatments.
Important findings The results showed 1) mean basal diameter of shrubs in the V. negundo var. heterophylla and S. salicifolia shrublands were increased by 1.69%, 2.78%, 2.51%, 1.80% and 1.38%, 1.37%, 1.59%, 2.05% every year; 2) The height growth rate (the shrub height relative growth rate is defined with the percentage increase of plant height) of shrubs in the V. negundo var. heterophylla and S. salicifolia shrublands were 8.36%, 8.48%, 9.49%, 9.83% and 2.12%, 2.86%, 2.36%, 2.52% every year, respectively. Thee results indicated that N deposition stimulated growth of shrub layer both in V. negundo var. heterophylla and S. salicifolia shrublands, but did not reach statistical significance among all nitrogen treatments. The above-ground biomass increment of shrub layer in the V. negundo var. heterophylla and S. salicifolia shrublands were 0.19, 0.23, 0.14, 0.15 and 0.027, 0.025, 0.032, 0.041 t C·hm-2·a-1 respectively, which demonstrated that short-term N addition had no significant effects on the accumulation of C storage of the two shrublands. The litter production of the V. negundo var. heterophylla and S. salicifolia communities in 2013 were 135.7 and 129.6 g·m-2 under natural conditions, respectively. Nitrogen addition promoted annual production of total litterfall and different components of litterfall to a certain extent, but did not reach statistical significance among all nitrogen treatments. Above results indicated that short-term fertilization, together with extremely low soil moisture content and other related factors, lead to inefficient use of soil available nitrogen and slow response of shrublands to N addition treatments.  相似文献   

18.
采用分解网袋法,在古尔班通古特沙漠南缘设置对照N0(0 g N·m-2·a-1)、N5(5 g N·m-2·a-1)、N10(10 g N·m-2·a-1)和N20(20 g N·m-2·a-1)4个施N处理,研究外源N添加对多枝柽柳、盐角草及两者混合凋落物分解过程及养分释放的影响,分析氮沉降对荒漠生态系统凋落物分解的影响。结果表明: 各物种凋落物的分解速率存在显著差异,经过345 d的分解,多枝柽柳、盐角草及混合物在不同N处理间的分解速率分别为0.64~0.70、0.84~0.99和0.71~0.81 kg·kg-1·a-1。凋落物分解过程中,N、P均表现为养分的直接释放,试验结束时,N0、N5、N10和N20处理单种凋落物及其混合物N分别释放60.6%~67.4%、56.7%~62.6%、57.4%~62.3%、46.8%~63.0%,P分别释放51.9%~77.9%、59.9%~74.7%、53.0%~79.9%、52.3%~76.4%。N处理对单种凋落物及其混合物的分解影响不显著,但各种凋落物的养分动态对N添加的响应不同,N处理抑制了盐角草N、P释放及混合凋落物P释放,而对多枝柽柳无影响。在温带荒漠,适量的N输入对凋落物分解速率影响不大,但可能会延缓个别物种养分向土壤系统的归还。  相似文献   

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