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1.
2004—2008年,采用微根管(minirhizotron)技术,对落叶松人工林细根生产和死亡进行连续动态观测,同时测定了温度(大气温度和土壤10 cm温度)和水分(降雨量和土壤10 cm深处含水量)的变化,研究细根生产、死亡的动态及其与温度和水分的关系.结果表明:落叶松细根年根长生产量在0.20~0.78 mm.cm-2,死亡量在0.26~0.72 mm.cm-2;2004—2006年细根年根长平均生产量(0.67 mm.cm-2)和死亡量(0.59 mm.cm-2)均高于2007—2008年细根年根长平均生产量和死亡量(0.37和0.39 mm.cm-2);在生长季内(5—10月),落叶松春末至夏季(6—7月)的细根生产量占全年产量的51%~68%,秋末(10月)仅占全年的1%~4%;而夏末(8月)和秋季(9—10月)细根死亡量占全年的59%~70%,早春(5月)占全年的1%~5%.相关分析表明,大气温度变化可以解释细根生产量66%的变异,而土壤10 cm深处温度解释24%,降雨量解释27%.细根的死亡量与土壤10 cm深处温度呈指数正相关.  相似文献   

2.
王娜  沈雅飞  程瑞梅  肖文发  杨邵  郭燕 《生态学杂志》2017,28(12):3827-3832
采用连续根钻法、分解袋法、分室通量模型法计算三峡库区马尾松细根的年生产量和周转率,分析细根生产量和周转率与各影响因子的关系.结果表明: 马尾松<0.5、0.5~1和1~2 mm细根年均生物量分别为0.29、0.59、0.76 t·hm-2,细根年生产量分别为0.13、0.49、0.37 t·hm-2,细根年周转率分别为1.49、1.01、0.40 a-1.各影响因子对不同径级细根生产与周转的影响不同.土壤温度、土壤钙含量显著影响<0.5 mm细根生产量与细根周转,且土壤温度解释生产量和周转率32.8%和25.0%的变异,土壤钙含量解释65.6%和73.1%的变异;细根生物量与细根生产量呈显著正相关,细根生物量分别解释<0.5、0.5~1和1~2 mm细根生产量41.0%、41.1%和54.5%的变异;细根P、K含量与<0.5 mm细根生产量具有显著相关性,分别解释<0.5 mm细根生产量32.2%、39.2%的变异.<0.5 mm细根与各影响因子的关系最为密切,土壤温度、土壤钙含量是细根生物量的主要影响因子.  相似文献   

3.
黄土高原4种植被类型的细根生物量和年生产量   总被引:1,自引:0,他引:1  
邓强  李婷  袁志友  焦峰 《生态学杂志》2014,25(11):3091-3098
细根(≤2 mm)在陆地生态系统净初级生产力的分配中占有重要地位,在碳循环和水土保持方面具有重要意义. 本文采用土钻法和内生长法,以黄土高原刺槐人工林、落叶灌木、退耕草地和沙蒿群落4种主要植被类型为对象,研究0~40 cm土层细根生物量、垂直分布和细根年生产量. 结果表明: 细根生物量与纬度呈线性负相关. 4种植被类型0~40 cm土层细根生物量的大小顺序为落叶灌木(220 g·m-2)>刺槐人工林(163 g·m-2)≈退耕草地(162 g·m-2)>沙蒿群落(79 g·m-2). 退耕草地直径≤1 mm细根生物量占直径≤2 mm总细根生物量的74.1%,在4种植被类型中最高;4种植被类型细根生物量随着土层深度的增加而减少,最大值均出现在0~10 cm土层. 退耕草地0~10 cm土层细根生物量占0~40 cm土层总细根生物量的44.1%,显著高于其他3种植被类型;细根年生产量与纬度呈线性负相关. 4种植被类型0~40 cm土层细根年生产量大小顺序为退耕草地(315 g·m-2·a-1)>落叶灌木(249 g·m-2·a-1)>刺槐人工林(219 g·m-2·a-1)>沙蒿群落(115 g·m-2·a-1),其中退耕草地显著高于其他3种植被类型. 退耕草地0~10 cm土层细根生产量占0~40 cm土层总细根生产量的40.4%,在4种植被类型中最高. 退耕草地细根周转时间为0.51 a,低于其他3种植被类型.  相似文献   

4.
落叶松和水曲柳人工林细根生长、死亡和周转   总被引:9,自引:3,他引:9       下载免费PDF全文
 细根周转是陆地生态系统碳分配格局与过程的核心环节,而细根周转估计的关键是了解细根的生长和死亡动态。该研究以18年生落叶松(Larix gmelinii)和水曲柳(Fraxi nus mandshurica)人工林为对象,采用微根管(Minirhizotron)技术对两树种0~40 cm深度的细根生长和死亡动态进行了为期1年的观测,研究了两树种细根在不同土层深度的生长与死亡动态、细根周转以及与土壤有效氮含量、土壤温度、大气温度和降水的关系。结果表明:1) 落叶松平均细根生长(Root length density production, RLDP)0.0045 mm•cm-2•d-1)明显低于水曲柳RLDP(0.0077 mm•cm-2•d-1)。两个树种细根平均RLDP在表层(0~10 cm)最大,而底层(30~40 cm)最小 ,两树种平均细根死亡(Root length density mortality, RLDM)也表现同样规律 。水曲柳春季生长的细根占41.7%,夏季占39.7%,而落叶松细根生长分别是24.0%和51.2%,水曲柳细根死亡主要发生在春季(34.3%) 和夏季(34.0%),而落叶松细根死亡主要发生在夏季和秋季(分别占28.5%和32.3%),两 树种细根生长与死亡在冬季均较小;2)落叶松细根年生长量(0.94 mm•cm-2•a-1)和年死亡量(0.72 mm•cm-2•a-1)明显低于水曲柳(1.52和1.21 mm•cm-2•a-1),两树种细根表层年生长量和年死亡量均最高,底层最低。落叶松细根年周转为3.1次•a-1(按年生长量计算)和2.4次•a-1(按年死亡量计算),相比较,水曲柳细根年周转分别为2.7次•a-1和2.2次•a-1;3)土壤有效氮含量、土壤温度、大气温度和降水综合作用影响细根生长和死亡动态,可以解释细根生长80%的变异和细根死亡95%以上的变异。  相似文献   

5.
幼龄柠条细根现存量与环境因子的关系   总被引:8,自引:1,他引:7       下载免费PDF全文
以晋西北黄土高原区柠条(Caragana korshinskii)幼龄人工林为研究对象, 应用微根管技术(Minirhizotron technique)对林地100 cm土层范围的柠条细根生长动态进行了观测。以2007年生长季(5~9月)的根长密度(RLD, mm·cm-3)数据为基础, 对柠条细根现存量(RLDst, mm·cm-3)及其与环境因子(≥10 ℃积温、同期土壤积温、积降雨量和土壤水分等)的关系作了研究。结果表明, 40~90 cm土层是柠条细根的主要分布区和生长活跃区, 其细根占细根总量的59.7%。柠条细根现存量的季节变化特征为: 5月至9月上旬RLDst持续增加, 9月下旬RLDst略有降低。柠条细根现存量季节变化与≥10 ℃积温、同期土壤积温和积降雨量均存在极显著正相关关系。  相似文献   

6.
对不同演替阶段的树种细根生产动态及其对环境因子响应的差异目前仍缺乏了解。为此, 在福建省三明市选择了中亚热带演替前期的马尾松(Pinus massoniana)和演替后期的米槠(Castanopsis carlesii)两种人工林为研究对象, 采用微根管法对两种人工林的细根根长生产量及其动态进行了为期2年的观测, 并分析了细根生产量的径级和土层分布, 及月生产量动态与气温、降水、土壤温度、土壤含水率等环境因子间的关系。结果表明: 1)两种林分的细根生产量有显著差异, 马尾松人工林细根年根长生产量约为米槠人工林细根年根长生产量的4倍; 两种林分的细根生产量呈现显著的月变化, 峰值均出现在夏季, 且2年内总细根生产量以夏季的细根生产量最大。2)两林分均是直径0-0.3 mm的细根所占细根生产量比例最大; 土层分布上, 马尾松人工林0-10 cm土层细根所占生产量的比例最大, 米槠人工林30-40 cm土层细根所占生产量比例最大。3)偏相关分析表明, 两林分细根月生产量均与气温、土壤温度极显著相关或显著正偏相关, 与降水、土壤含水率的偏相关均不显著; 一元线性回归分析表明, 演替早期马尾松人工林细根月生产量与气温、土壤温度的相关性明显高于米槠人工林。该研究表明, 与演替后期的米槠人工林相比, 中亚热带演替早期的马尾松人工林细根生产量大, 且与温度间的相关性更高。  相似文献   

7.
尽管干旱区生态系统的脆弱性受到了广泛的关注, 但目前关于干旱区植物细根有机碳与土壤碳循环关系的研究还比较少见。在2010年整个生长季节内, 采用土钻法和内生长法, 对新疆干旱区的琵琶柴(Reaumuria soongorica)群落土壤特性、细根的生物量月动态、生产量和周转进行了研究。结果表明: 琵琶柴群落表层土壤含水量最低, 土壤含水量表现出从浅层到深层逐渐增加的趋势; 而表层土壤的有机碳含量最高, 随着土壤深度的加深, 有机碳含量逐渐降低。细根生物量的月平均值为54.51 g·m-2, 群落细根生产量在82.76-136.21 g·m-2·a-1之间, 琵琶柴群落的细根周转率为2.08 times·a-1, 通过细根死亡进入土壤中的有机碳为17 g·m-2·a-1。这些结果表明: 由于灌丛细根高的周转速率, 细根是干旱区土壤有机碳输入的重要部分。  相似文献   

8.
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   

9.
2010年11月-2011年12月, 研究了华西雨屏区31年生香樟人工林土壤表层(0~30 cm)细根生物量及碳储量.结果表明: 香樟人工林土壤0~30 cm层细根总生物量(活根+死根)和碳储量的平均值分别为1592.29 kg·hm-2和660.68 kg C·hm-2,其中活细根贡献率分别为91.1%和91.8%.随着土壤深度的增加,香樟1~5级活细根和死细根的生物量及碳储量均显著减少;随着根序等级的升高,香樟活细根生物量及碳储量显著增加.香樟细根总生物量及碳储量均在秋季最高、冬季最低,死细根生物量及碳储量为冬季最高、夏季最低;1级根和2级根生物量及碳储量均在夏季最高、冬季最低,而3~5级根则为秋季最高、冬季最低.土壤养分和水分的空间异质性是导致细根生物量和碳储量变化的主要原因.  相似文献   

10.
格氏栲天然林与人工林细根生物量、季节动态及净生产力   总被引:59,自引:14,他引:59  
通过对福建三明格氏栲天然林及在其采伐迹地上营造的33年生格氏栲人工林和杉木人工林细根分布、季节动态与净生产力进行的为期3a(1999~2001)的研究,结果表明,格氏栲天然林、格氏栲和杉木人工林活细根生物量分别为4.944t/hm2、3.198t/hm2和1.485t/hm2,死细根生物量分别为3.563t/hm2、2.749t/hm2和1.287t/hm2;死细根生物量占总细根生物量的比例分别为41.9%、46.2%和46.4%;<0.5mm细根生物量占总细根生物量的比例分别为31.2%、29.4%和69.9%。3种林分活细根生物量和死细根生物量季节间差异显著(P<0.05),但年份间差异则不显著(P>0.05);活细根生物量最大值均出现在3月份,最小值一般出现在5~7月份或11~翌年1月份间。0~10cm表土层格氏栲天然林活细根生物量高达295.65g/m2,分别是格氏栲人工林和杉木人工林的2.4倍和8.1倍;该层格氏栲天然林活细根生物量占全部活细根生物量的59.8%,均高于格氏栲人工林(39.07%)和杉木人工林(24.51%)。格氏栲天然林、格氏栲人工林和杉木人工林细根分解1a后的干重损失率分别为68.34%~80.13%、63.51%~77.95%和47.69%~60.78%;年均分解量分别为8.747、5.143和2.503t/hm2;死亡量分别为8.632、5.148和2.492t/hm2;年均净生产量分别为8.797、5.425和2.513t/hm2,年周转速率分别为1.78、1  相似文献   

11.
樟子松人工林细根寿命估计及影响因子研究   总被引:2,自引:1,他引:1       下载免费PDF全文
细根寿命的估计是了解细根生产和死亡的关键, 对了解陆地生态系统碳分配格局和养分循环具有重要意义。该研究采用微根管(minirhizotron)技术, 以23年生樟子松(Pinus sylvestris var. mongolica)人工林为研究对象, 对细根生长和死亡过程进行了连续两年的观测。细根寿命的估计采用Kaplan-Meier方法, 计算细根的平均寿命(mean longevity)、中值寿命(median longevity)和累积存活率(cumulative survival rate), 用对数秩检验(log-rank test)比较单一因素, 包括细根直径、根序、出生季节和土层以及菌根侵染对细根寿命的影响。采用Cox比例风险回归分析方法, 同时分析上述因素对细根存活的影响程度。结果表明, 樟子松细根的生产和死亡具有明显的季节性, 春末和夏季(6月和7月)为生产高峰; 而死亡高峰出现在夏末至秋末, 以及冬季。樟子松细根的平均和中值寿命分别为(322 ± 10)天和(310 ± 15)天, 对数秩检验表明, 仅考虑单一因子时, 细根直径、根序、出生季节和土层以及菌根侵染均对细根寿命有显著影响。Cox回归分析表明, 菌根侵染、细根直径和土层是影响樟子松细根寿命的重要因子。细根直径每增加1 mm, 细根死亡危险率就降低99%, 即相当于寿命延长99%; 细根出生土层每增加1 cm, 其寿命延长5%; 而菌根侵染后, 会导致细根死亡危险率增加175%; 但根序和出生季节的影响不显著。这些发现证实: 林木细根寿命受到内在与外在因素的共同控制, 而多变量回归分析的方法有助于我们全面揭示细根寿命变异的潜在机制。  相似文献   

12.
《植物生态学报》2015,39(11):1071
AimsOur objectives were to determine differences in fine root production, its relationships with environmental factors, and its diameter- and depth-related distribution patterns between plantations of two subtropical tree species differing in successional stages. MethodsPlantation forests of an early-successional species, Pinus massoniana, and a late-successional species, Castanopsis carlesii, in Sanming, Fujian Province, were selected. Fine root production was monitored for two years using minirhizotrons methods. At the same time, environmental factors including monthly air temperature, monthly precipitation, soil temperature, and soil water content were determined.Important findings 1) During the two years, there was significant difference in annual fine root length production between these two forests, with annual production of P. massoniana plantation nearly four times that of C. carlesii plantation. Fine root length production under both forests showed significant monthly dynamics and maximized in summer, a season when most of fine roots were born. 2) Roots of 0-0.3 mm in diameter accounted for the largest proportion of total fine root length production. Fine roots were concentrated mostly at the 0-10 cm soil depth in P. massoniana plantation, but happened mostly at the 30-40 cm soil depth in the C. carlesii plantation. 3) Partial correlation analysis suggested that, monthly fine root production of both forests was significantly correlated with both air temperature and soil temperature, while it had no significant correlation with either rainfall or soil water content. Linear regression analysis illustrated that monthly fine root production was more correlated with air temperature and soil temperature in the P. massoniana plantation than in the C. carlesii plantation. It was concluded that fine root production in the early-successional P. massoniana plantation was not only much higher in amount, but also more sensitive to temperature, than that in the late-successional C. carlesii plantation.  相似文献   

13.
福建三明米槠次生林皆伐后形成人促更新幼林(AR)与米槠人工幼林(CC)、杉木人工幼林(CL),以保留的米槠次生林(CK)为对照,利用微根管法比较不同更新方式初期细根(直径≤2 mm)生物量和生产力的差异.结果表明: 1年内,AR、CC、CL和CK细根的年均生物量分别为422.5、253.1、197.2和162.8 g·m-2.4种林分细根总生产力大小为:AR (284.0 g·m-2·a-1)>CC (182.6 g·m-2·a-1)>CL (136.7 g·m-2·a-1)>CK (15.4 g·m-2·a-1).AR和CC春季生产力最大,CL秋季最大,CK冬季最大.CC表现为其他植物细根生产力多于目标树种,CL表现为目标树种细根生产力多于其他植物.AR和CC总细根的月生产力与各月降水量呈显著正相关,CL的其他植物细根月生产力与月均气温呈显著正相关.3种更新方式下幼林细根的年生产力和年均生物量都以20~40 cm土层最大,且以0~1 mm细根占主体.采用人促更新方式的幼林细根生物量和生产力大于人工更新方式的幼林,人促更新方式更有利于增加林地有机物归还、提高土壤肥力、维持较高生产力和降低更新初期林地碳源.  相似文献   

14.
《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   

15.
Fine root tumover is a major pathway for carbon and nutrient cycling in terrestrial ecosystems and is most likely sensitive to many global change factors.Despite the importance of fine root turnover in plant C allocation and nutrient cycling dynamics and the tremendous research efforts in the past,our understanding of it remains limited.This is because the dynamics processes associated with soil resources availability are still poorly understood.Soil moisture,temperature,and available nitrogen are the most important soil characteristics that impact fine root growth and mortality at both the individual root branch and at the ecosystem level.In temperate forest ecosystems,seasonal changes of soil resource availability will alter the pattern of carbon allocation to belowground.Therefore,fine root biomass,root length density(RLD)and specific root length(SRL)vary during the growing season.Studying seasonal changes of fine root biomass,RLD,and SRL associated with soil resource availability will help us understand the mechanistic controls of carbon to fine root longevity and turnover.The objective of this study was to understand whether seasonal variations of fine root biomass,RLD and SRL were associated with soil resource availability,such as moisture,temperature,and nitrogen,and to understand how these soil components impact fine root dynamics in Larix gmelinii plantation.We used a soil coring method to obtain fine root samples(≤2 mm in diameter)every month from Mav to October in 2002 from a 17-year-old L.gmelinii plantation in Maoershan Experiment Station,Northeast Forestry University,China.Seventy-two soil cores(inside diameter 60 mm;depth intervals:0-10 cm,10-20 cm,20-30 cm)were sampled randomly from three replicates 25 m×30 m plots to estimate fine root biomass(live and dead),and calculate RLD and SRL.Soil moisture,temperature,and nitrogen(ammonia and nitrates)at three depth intervals were also analyzed in these plots.Results showed that the average standing fine root biomass(live (32.2 g.m-2.a-1)in the middle(10-20 cm)and deep layer (20-30cm),respectively.Live and dead fine root biomass was the highest from May to July and in September,but lower in August and October.The live fine root biomass decreased and dead biomass increased during the growing soil layer.RLD and SRL in May were the highestthe other months,and RLD was the lowest in Septemberdynamics of fine root biomass,RLD,and SRL showed a close relationship with changes in soil moisture,temperature,and nitrogen availability.To a lesser extent,the temperature could be determined by regression analysis.Fine roots in the upper soil layer have a function of absorbing moisture and nutrients,while the main function of deeper soil may be moisture uptake rather than nutrient acquisition.Therefore,carbon allocation to roots in the upper soil layer and deeper soil layer was different.Multiple regression analysis showed that variation in soil resource availability could explain 71-73% of the seasonal variation of RLD and SRL and 58% of the variation in fine root biomass.These results suggested a greater metabolic activity of fine roots living in soil with higher resource availability,which resulted in an increased allocation of carbohydrate to these roots,but a lower allocation of carbohydrate to those in soil with lower resource availability.  相似文献   

16.
* Greater fine-root production under elevated [CO2] may increase the input of carbon (C) and nitrogen (N) to the soil profile because fine root populations turn over quickly in forested ecosystems. * Here, the effect of elevated [CO)] was assessed on root biomass and N inputs at several soil depths by combining a long-term minirhizotron dataset with continuous, root-specific measurements of root mass and [N]. The experiment was conducted in a CO(2)-enriched sweetgum (Liquidambar styraciflua) plantation. * CO2) enrichment had no effect on root tissue density or [N] within a given diameter class. Root biomass production and standing crop were doubled under elevated [CO2]. Though fine-root turnover declined under elevated [CO2], fine-root mortality was also nearly doubled under CO2 enrichment. Over 9 yr, root mortality resulted in 681 g m(-2) of extra C and 9 g m(-2) of extra N input to the soil system under elevated [CO2]. At least half of these inputs were below 30 cm soil depth. * Increased C and N input to the soil under CO2 enrichment, especially below 30 cm depth, might alter soil C storage and N mineralization. Future research should focus on quantifying root decomposition dynamics and C and N mineralization deeper in the soil.  相似文献   

17.
以喀斯特峰丛洼地不同植被恢复阶段的草丛、灌丛、次生林和原生林为研究对象,采用土芯法,分0~10、10~20、20~30 cm等3层获取群落活细根(直径≤2 mm),分析其生物量、形态特征及其与土壤性状的关系.结果表明:各恢复阶段细根生物量为194.63~255.19g·m-2,集中分布在0~10 cm表层土壤中,占0~30 cm土层总生物量60%以上,不同恢复阶段群落生物量的差异不显著;细根比根长和比表面积在不同恢复阶段差异显著,随着植被由草丛向原生林正向恢复而逐渐降低;超过66%的根长和64%的根面积分布在0~10 cm表层土壤中,多数细根根长和根面积均在0~0.5 mm和0.5~1 mm径级,这两级根长和根面积占其总量的87%和72%以上.冗余分析表明,喀斯特峰丛洼地植物群落细根特征与土壤性状之间存在着不同的相关性,其中土壤有机碳、速效钾和全氮对细根特征影响较大.这是植物长期适应生境条件形成的有效策略.  相似文献   

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