拉萨河谷杨树人工林细根的生产力及其周转

通过土钻取样和分解袋法对拉萨河谷杨树人工林细根的生长和周转进行了测定.结果表明,在该地区杨树人工林生态系统中,约80%的细根集中分布在0～30cm土壤表层中;接近树木一侧的活(死)细根生物量均高于外侧,但二者未达到显著的差异;在生长季期间,活细根生物量平均为2.576 t · hm-2,死细根生物量平均为1.566 t · hm-2,生长高峰出现在生长季初期.经估算,拉萨河谷杨树人工林细根年生长量为3.030 t · hm-2,年周转率为1.18次;但受高原低温的影响,细根分解缓慢,分解系数k平均为0.0007～0.0008.细根的这种生长特征是杨树对高原地区短暂生长季节和雨热同季气候条件的一种适应性表现.     

杨树人工林细根数量和形态特征的季节动态及代际差异

采集欧美杨107Ⅰ代和Ⅱ代人工林细根样品,分析杨树不同根序细根数量特征(根长度、表面积和生物量)和形态特征(比根长、根长密度、根组织密度)对季节波动的响应及其代际差异.结果表明： 杨树各根序细根数量特征(根长度、表面积和生物量)均呈明显的季节变化,且具有明显的根序差异性.低级根序细根数量特征季节差异显著,细根生物量在生长季显著增加而生长季后显著下降.高级根序细根比根长季节波动显著,而根长密度和根组织密度等形态特征波动较小.连作导致人工林杨树1～2级细根长度、生物量、比根长和根长密度在生长季显著增大.1级细根数量特征与土壤温湿度呈显著正相关,与土壤有机质和速效氮含量呈显著负相关;而2级细根数量特征仅与土壤养分显著相关.杨树人工林细根特征的季节动态及代际差异体现了杨树对细根的碳投入变化,因连作引发的土壤养分匮乏可能引发植株对根系的碳投入增加,这种碳分配格局与人工林地上部分生产力形成密切相关.     

关帝山华北落叶松人工林细根生物量空间分布及季节变化

利用根钻法研究了山西关帝山华北落叶松（Larix principis—rupprechtii Mayr）人工林细根生物量的空间分布和季节变化特征。结果表明,华北落叶松不同径级细根生物量随土层深度的增加而逐渐减少,土壤表层（0—10cm）中各径级细根的生物量最高,Ⅰ级细根（根直径0～1mm）的生物量在不同土层深度间差异显著（P〈0．05）;距树干不同水平距离处各径级的细根生物量差异均未达到显著水平（P〉0．05）。在0～10cm土层中,各径级细根生物量的季节变化差异显著（P〈0．05）,均表现为单峰型,峰值出现在9月份;在10～20cm和20-30cm土层中,Ⅰ级和Ⅱ级（根直径1～2mm）细根生物量季节变化差异显著,Ⅲ级细根（根直径2～5mm）和Ⅰ级死根（根直径0～2mm）生物量季节变化差异不显著。     

距树干不同距离处华北落叶松人工林细根生物量分布特征及季节变化

 该文研究了华北落叶松(Larix principis-rupprechtii)人工林细根生物量水平分布和季节变化特征。采用钻土芯法(土钻内径7.0 cm), 在距树干20、50和100 cm处设取样点, 每个样点处分3层(0~10、11~20和21~30 cm)钻取土芯, 取样时间为5、7、9和10月。华北落叶松人工林细根(≤2 mm)生物量全年平均值为224.89 g•m^–2, 在水平分布上表现为100 cm处细根生物量最大(244.20 g•m^–2), 其次为20 cm处(221.03 g•m^–2), 50 cm处最少(209.45 g•m^–2)。在0~30 cm土层, 总细根(包括活跟和死根)生物量季节变化范围在169.67~263.09 g•m^–2之间, 9月细根生物量最大, 5月细根生物量最少。0~10 cm土层细根生物量季节变化差异显著(p＜0.05), 11~20和21~30 cm差异不显著(p＞0.05)。距树干100和20 cm处(0~10 cm土层), 细根生物量的季节变化差异明显(p＜0.05), 9月总细根生物量最大(172.82和185.68 g•m^–2), 5月总细根生物量最少(69.28和73.47 g•m^–2); 50 cm处季节变化差异不明显(p＞0.05)。细根生物量分布和季节变化不仅受土壤垂直格局影响同时也与距树干不同水平距离有很大的关系。     

格氏栲天然林与人工林根系呼吸季节动态及影响因素

通过用挖壕沟 静态碱吸收法对福建三明格氏栲天然林及33年生格氏栲和杉木人工林的根系呼吸进行为期2a定位研究。不同森林根系呼吸速率季节变化均呈单峰曲线,最大值出现在春末或夏初,最小值出现在冬季。1年中格氏栲天然林、格氏栲人工林和杉木人工林根系呼吸速率变化范围分别在157.76~480.40mgCO2/(m2·h)、53.03~339.45mgCO2/(m2·h)和16.66~228.02mgCO2/(m2·h)之间。在近似正常气候状况的2002年,不同森林根系呼吸主要受土壤温度影响(R2=0.52~0.72);而土壤温度和土壤湿度共同则可解释根系呼吸速率季节变化的81%~90%。在极端干旱的2003年,根系呼吸受土壤温度或湿度的影响较小,土壤温度和土壤湿度共同仅能解释根系呼吸变化的24%~60%,这与根系在持续干旱期间长期处于近休眠状态有关。根系呼吸对土壤温度和土壤湿度的敏感性大小顺序均为杉木人工林>格氏栲人工林>格氏栲天然林。格氏栲天然林根系呼吸占土壤呼吸比例(47.6%)均高于格氏栲和杉木人工林的(42.5%和40.2%),不同森林根系呼吸占土壤呼吸比例均以冬季最低,而以5月或6月最高。格氏栲天然林、格氏栲人工林和杉木人工林根系呼吸年通量分别为6.537、4.013和1.828tC/(m2·h)。     

杨树细根及草根的生产力与周转的研究

对北方杨树人工林0－40cm土层中杨树细根和草根（≤2mm）年生物量、分解量、死亡量、生长量和周转率进行观察研究。结果表明,杨树细根的年生物量为2．062t.hm^-2,死根生物量为0．746t.hm^-2,分解量为0．158t.hm^2,生长量为2．351t.hm^－2,周转率为每年1．14次,活草根的年生物量、死根生物量、分解量、生长量和周转率分别0．501、0．035、0．023、0．691t.hm^-2和1．38,同时给出了杨树细根干重损失随分解时间变化的方程：1nx/x0=0.9515e^-0.0014t。     

华西雨屏区香樟人工林土壤表层细根生物量和碳储量

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.     

格氏栲天然林与人工林根际土壤微生物及其生化特性的研究

通过对格氏栲天然林（约１２０年生）和人工林（２８年生）根际土壤和全土微生物、生化活性、土壤养分的研究,结果表明：格氏栲天然林根际和全土土壤养分、土壤微生物区系、生理类群数量、土壤酶活性和生化作用强度均比相应人工林的大,格氏栲天然林根际土壤速效性养分相对富集,而人工林的则存在亏缺现象。格氏栲人工林的根际效应（Ｒ／Ｓ值）比天然林的明显。     

不同树龄橡胶林土壤水分和细根生物量

采用根钻法,分析了橡胶幼树期(5 a)、初产期(9 a)和旺产期(16 a)林下土壤水分特征及橡胶树细根生物量.结果表明:橡胶树龄越大,土壤含水量越高,而橡胶树细根生物量越少;不同树龄橡胶林0～60 cm土壤含水量随着土层深度的增加而升高,年内变化则呈\"双峰\"型;不同树龄橡胶树细根生物量最大值均出现在10 cm土层,且随着土层深度的增加而减少,细根生物量年内变化同样呈\"双峰\"型,但不同树龄细根生物量峰值的出现时间不一致.土壤含水量和土层深度是橡胶树细根生物量的主要影响因子.     

柠条细根的空间分布特征及其季节动态

以晋西北黄土区30年生柠条(Caragana korshinskii Kom.)人工林为研究对象,2007年应用Minirhizotron技术,分别在距茎干水平距离0、50、100 cm处设点,对林地0-100 cm土层深度范围内的柠条细根空间分布及其生长季的动态进行了研究。结果表明:(1)生长季柠条细根根长密度(RLD)总平均值为1.3423 mm/cm²。在水平方向上,距茎干水平距离50 cm处分布最多(1.5369 mm/cm²),其次为0 cm处(1.3855 mm/cm²), 100cm处分布最少(1.1044 mm/cm²)。在垂直深度上,各土层RLD平均值大小顺序为40-60 cm>60-80 cm>20-40 cm>0-20 cm>80-100 cm;(2)在0-100 cm土层范围内,月平均RLD在生长季的波动范围为0.4405 2.1040 mm/cm²,其中9月份最多,4月份最少;RLD在5个土层深度3个水平距离处随季节变化均表现先增加后减少的趋势,且不同空间位置RLD峰值变化均在秋季(8 10月份)波动。细根的这种时空分布差异,可能主要受林下土壤资源空间异质性及其季节性变化的影响,但也不排除其它因素的影响(如真菌,植食性昆虫)。     

格氏栲天然林和人工林土壤呼吸对干湿交替的响应

通过室外定位观测前期连续干旱情况下天然降雨及室内模拟不同温度 (10℃、19℃和 2 8℃ )下测定格氏栲天然林、格氏栲人工林和杉木人工林土壤增湿后呼吸动态 ,探讨不同林型土壤呼吸对土壤干湿交替的响应。结果发现室外定位观测和室内模拟试验均出现了增湿后土壤呼吸骤升至最大值及随后逐渐衰减的现象 ,且这种变化可由时间过程模型 (R=ate- bt c)较好地进行拟合。温度升高提升了土壤呼吸对干湿交替的响应值 RV。格氏栲天然林土壤呼吸对干湿交替的响应对温度最为敏感 ,随温度升高其响应指数 RE增加 ;杉木林土壤呼吸对干湿交替的响应指数 RE最高 ,且对土壤水分变化最敏感 ,但随温度升高超过一定限度后其响应指数 RE反而降低     

格氏栲天然林与人工林土壤非保护性有机C含量及分配

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土壤非保护性有机 C含量及分配的研究 ,结果表明 ,格氏栲天然林 0～ 10 0 cm土层内土壤有机 C贮量分别是格氏栲人工林和杉木人工林的 1.17倍和1.35倍 ,轻组有机 C贮量分别是后两者的 1.6 4倍和 2 .16倍 ,而颗粒有机 C贮量则分别是后两者的 1.6 0倍和 3.4 3倍 ,其土壤轻组有机 C和颗粒有机 C的分配比例亦显著高于后两者。不同林分间差异均以 0～ 10 cm土层为最大 ,该层格氏栲天然林土壤有机 C含量分别是格氏栲和杉木人工林的 1.5 2倍和 1.6 3倍 ,轻组有机 C含量分别是后两者的 1.70倍和 2 .14倍 ,而颗粒有机C含量则分别是后两者的 2 .18倍和 4 .85倍。这种差异与经营人工林时进行皆伐、炼山、整地等对林地干扰强度较大、幼林郁闭前产生水土流失及凋落物、枯死细根归还量减少等有关。土壤轻组有机 C和颗粒有机 C可作为土壤有机 C库变化的较为敏感指标 ,同时亦可指示土壤肥力演变。     

关于氮有效性影响细根生产量和周转率的四个假说

在全球变化如氮沉降及温度升高等可能导致土壤氮有效性增加的背景下,细根动态如何变化一直是陆地生态学研究中的一个重要内容.本文综述了前人提出的细根动态响应土壤N有效性提高的4个代表性假说:1)细根生产量和周转率都提高;2)细根生产量和周转率都下降;3)细根生产量下降,周转率提高;4)细根生产量提高,周转率下降.根据2000年以来以微根管方法为主测得的根系动态数据,笔者认为假说1)和假说2)得到的支持最为充分.此外,还探讨了树种、细根异质性、菌根真菌、细根采样方法和施肥方法等对上述各假说检验的影响.     

Fine root dynamics in a loblolly pine forest are influenced by free-air-CO2-enrichment: a six-year-minirhizotron study

Efforts to characterize carbon (C) cycling among atmosphere, forest canopy, and soil C pools are hindered by poorly quantified fine root dynamics. We characterized the influence of free‐air‐CO₂‐enrichment (ambient +200 ppm) on fine roots for a period of 6 years (Autumn 1998 through Autumn 2004) in an 18‐year‐old loblolly pine (Pinus taeda) plantation near Durham, NC, USA using minirhizotrons. Root production and mortality were synchronous processes that peaked most years during spring and early summer. Seasonality of fine root production and mortality was not influenced by atmospheric CO₂ availability. Averaged over all 6 years of the study, CO₂ enrichment increased average fine root standing crop (+23%), annual root length production (+25%), and annual root length mortality (+36%). Larger increase in mortality compared with production with CO₂ enrichment is explained by shorter average fine root lifespans in elevated plots (500 days) compared with controls (574 days). The effects of CO₂‐enrichment on fine root proliferation tended to shift from shallow (0–15 cm) to deeper soil depths (15–30) with increasing duration of the study. Diameters of fine roots were initially increased by CO₂‐enrichment but this effect diminished over time. Averaged over 6 years, annual fine root NPP was estimated to be 163 g dw m^?2 yr^?1 in CO₂‐enriched plots and 130 g dw m^?2 yr^?1 in control plots (P= 0.13) corresponding to an average annual additional input of fine root biomass to soil of 33 g m^?2 yr^?1 in CO₂‐enriched plots. A lack of consistent CO₂× year effects suggest that the positive effects of CO₂ enrichment on fine root growth persisted 6 years following minirhizotron tube installation (8 years following initiation of the CO₂ fumigation). Although CO₂‐enrichment contributed to extra flow of C into soil in this experiment, the magnitude of the effect was small suggesting only modest potential for fine root processes to directly contribute to soil C storage in south‐eastern pine forests.     

Fine Root Production and Turnover in a Norway Spruce Stand in Northern Sweden: Effects of Nitrogen and Water Manipulation

Fine root length production, biomass production, and turnover in forest floor and mineral soil (0–30 cm) layers were studied in relation to irrigated (I) and irrigated-fertilized (IL) treatments in a Norway spruce stand in northern Sweden over a 2-year period. Fine roots (<1 mm) of both spruce and understory vegetation were studied. Minirhizotrons were used to estimate fine root length production and turnover, and soil cores were used to estimate standing biomass. Turnover was estimated as both the inverse of root longevity (RTL) and the ratio of annual root length production to observed root length (RTR). RTR values of spruce roots in the forest floor in I and IL plots were 0.6 and 0.5 y⁻¹, respectively, whereas the corresponding values for RTL were 0.8 and 0.9 y⁻¹. In mineral soil, corresponding values for I, IL, and control (C) plots were 1.2, 1.2, and 0.9 y⁻¹ (RTR) and 0.9, 1.1, and 1 y⁻¹ (RTL). RTR and RTL values of understory vegetation roots were 1 and 1.1 y⁻¹, respectively. Spruce root length production in both the forest floor and the mineral soil in I plots was higher than in IL plots. The IL-treated plots gave the highest estimates of spruce fine root biomass production in the forest floor, but, for the mineral soil, the estimates obtained for the I plots were the highest. The understory vegetation fine root production in the I and IL plots was similar for both the forest floor and the mineral soil and higher (for both layers) than in C plots. Nitrogen (N) turnover in the forest floor and mineral soil layers (summed) via spruce roots in IL, I, and C plots amounted to 2.4, 2.1, and 1.3 g N m⁻² y⁻¹, and the corresponding values for field vegetation roots were 0.6, 0.5, and 0.3 g N m⁻² y⁻¹. It was concluded that fertilization increases standing root biomass, root production, and N turnover of spruce roots in both the forest floor and mineral soil. Data on understory vegetation roots are required for estimating carbon budgets in model studies.     

树木细根生产与周转研究方法评述

树木细根在森林生态系统能量流动和物质循环中起重要的作用。树木细根研究及方法探讨也成为当今森林生态学的研究热点。在中国,对树木细根生产和周转的研究尚未引起充分重视。在此介绍了目前国外普遍采用的树木细根研究方法及其优缺点、适用性以及不同方法的研究比较,以期对我国开展树木细根方面的研究有所裨益。     

Ectomycorrhizal Colonization, Biomass, and Production in a Regenerating Scrub Oak Forest in Response to Elevated CO2

The effects of CO₂ elevation on the dynamics of fine root (FR) mass and ectomycorrhizal (EM) mass and colonization were studied in situ in a Florida scrub oak system over four years of postfire regeneration. Soil cores were taken at five dates and sorted to assess the standing crop of ectomycorrhizal and fine roots. We used ingrowth bags to estimate the effects of elevated CO₂ on production of EM roots and fine roots. Elevated CO₂ tended to increase EM colonization frequency but did not affect EM mass nor FR mass in soil cores (standing mass). However, elevated CO₂ strongly increased EM mass and FR mass in ingrowth bags (production), but it did not affect the EM colonization frequency therein. An increase in belowground production with unchanged biomass indicates that elevated CO₂ may stimulate root turnover. The CO₂-stimulated increase of belowground production was initially larger than that of aboveground production. The oaks may allocate a larger portion of resources to root/mycorrhizal production in this system in elevated rather than ambient CO₂.