浙江天童常绿阔叶林藤本植物的适应生态学研究Ⅱ.攀援能力和单株攀援效率

选用节间长、节数和支持木大小作为攀援能力的指标,单株攀援的支持木种类、数量及水平扩展面积作为单株攀援效率的指标,对浙江天童常绿阔叶林中5类12种大中型木质藤本的攀援能力及生态适应性和其中2种藤本单株攀援效率进行了分析,结果发现:1)不同攀援类型的节间长和节数存在显著差异,对支持木大小要求不同,反映出攀援能力在类型间的差异;没有一类藤本兼具所有优势,攀援能力是节间长、节数和支持木大小不同组合的结果;卷须类的广东蛇葡萄(Ampelopsis cantoniensis)和暗色菝葜(Smilax lanceifolia var.opaca)节间最长、节数居中、要求较小支持木;枝卷类的香港黄檀(Dalbergia millettii)节数和支持木大小与卷须类接近,但节间较短;不定根类的中华常春藤(Hedera nepalensis var.sinensis)、扶芳藤(Euonymus fortunei)、薜荔(Ficus pumila)和络石(Trachlospermum jasminoides)以及吸盘类的异叶爬山虎(Parthnocissus heterophylla)节间最短、但节数最多,要求较大支持木;茎缠绕类的白花野木瓜(Stauntonia leucantha)、羊角藤(Morinda umbellata)、忍冬(Lonicera japonica)和薯莨(Dioscorea cirrhosa)节间长居中,节数最少,要求中等但幅度较宽的支持木.2)同类型不同藤本的节间长、节数和支持木大小的差异反映出由非亲缘关系植物演化形成的藤本具有自身特性的一面;同种藤本个体间差异反映出植物的可塑性特点,是个体对群落内异质生境响应的结果.3)广东蛇葡萄单株平均攀援支持木(乔木)种类、株数和水平扩展面积大于香港黄檀,反映出前者单株攀援效率大于后者;两种藤本的单株攀援效率不与年龄呈正相关,反映出影响因素的复杂性;单株攀援效率可用来指示它们在群落中作用大小.     

浙江天童常绿阔叶林藤本植物的适应生态学研究 II.攀援能力和单株攀援效率

选用节间长、节数和支持木大小作为攀援能力的指标,单株攀援的支持木种类、数量及水平扩展面积作为单株攀援效率的指标,对浙江天童常绿阔叶林中5类12种大中型木质藤本的攀援能力及生态适应性和其中2种藤本单株攀援效率进行了分析,结果发现:1)不同攀援类型的节间长和节数存在显著差异,对支持木大小要求不同,反映出攀援能力在类型间的差异;没有一类藤本兼具所有优势,攀援能力是节间长、节数和支持木大小不同组合的结果;卷须类的广东蛇葡萄(Ampelopsiscantoniensis)和暗色菝葜(Smilaxlanceifoliavar.opaca)节间最长、节数居中、要求较小支持木;枝卷类的香港黄檀(Dalbergiamillettii)节数和支持木大小与卷须类接近,但节间较短;不定根类的中华常春藤(Hederanepalensisvar.sinensis)、扶芳藤(Euonymusfortunei)、薜荔(Ficuspumila)和络石(Trachlospermumjasmi noides)以及吸盘类的异叶爬山虎(Parthnocissusheterophylla)节间最短、但节数最多,要求较大支持木;茎缠绕类的白花野木瓜(Stauntonialeucantha)、羊角藤(Morindaumbellata)、忍冬(Lonicerajaponica)和薯莨(Dioscoreacirrhosa)节间长居中,节数最少,要求中等但幅度较宽的支持木。2 )同类型不同藤本的节间长、节数和支持木大小的差异反映出由非亲缘关系植     

季风常绿阔叶林不同恢复阶段藤本植物的物种多样性比较

藤本植物是森林生态系统的重要组成部分,影响群落的恢复与演替。通过对云南普洱地区不同恢复阶段(恢复15a、恢复30a和原始林群落)季风常绿阔叶林群落的野外调查,分析了不同恢复阶段藤本植物的物种丰富度、密度、多度、径级分布、多样性指数及攀援方式,并探讨藤本植物与支持木的关系。结果表明:在0.81hm²的调查样地中,共发现DBH≥0.1cm的藤本植物1292株(分属34科51属64种)。原始林群落的藤本物种丰富度、密度(DBH＜1cm)、胸高断面积和平均胸高断面积都显著高于恢复阶段,原始林和恢复15a群落的密度(DBH≥1cm)、平均胸径和平均长度之间无显著差异,但都显著高于恢复30a。3种群落类型中藤本植物的物种组成和径级分布有显著差异,原始林中藤本植物物种更多,而且大径级(DBH≥10cm)的藤本植物仅出现在原始林及恢复30a的群落。单株藤本攀援的支持木在3种群落类型中均占多数,藤本植物与支持木的胸径存在显著的正相关(P＜0.001),原始林群落中DBH≥15cm的支持木更易被攀援,而恢复阶段则相反。茎缠绕藤本植物对原始林的负面影响要显著少于恢复15a及30a群落,而卷须类藤本植物也反映出原始林正处于一个动态变化的阶段,同时根攀缘和搭靠类藤本植物物种组成和多度变化可以反映出干扰后季风常绿阔叶林的恢复程度。森林砍伐是影响不同恢复阶段藤本植物的物种组成和分布的主要因素。     

广西弄岗五桠果叶木姜子群落木质藤本空间格局及其与树种间的关系

木质藤本是生物多样性的重要组成,木质藤本通过影响支持木进而影响群落的结构和功能,但在生物多样性丰富的北热带喀斯特森林中,木质藤本与支持木的关系鲜为人知。以喀斯特季节性雨林的五桠果叶木姜子（Litsea dilleniifolia）群落为研究对象,对木质藤本的密度、分布格局及其与主要树种的关系进行调查研究,分析木质藤本对树木的影响。结果显示：（1）五桠果叶木姜子群落内木质藤本平均密度为0.0913株/m²,木质藤本在0-20m空间尺度整体表现为聚集分布,且随着尺度增大,聚集强度逐渐减弱;不同径级木质藤本在不同尺度上的分布格局不同。（2）木质藤本对不同径级、不同种类、不同聚集强度的支持木选择表现以下体征：随着支持木径级增加,木质藤本攀附的比例和每木藤本数有增加趋势,且木质藤本胸径与支持木胸径呈极显著正相关;附藤率较高的支持木有紫葳科（Bignoniaceae）种类和东京桐（Deutzianthus tonkinensis）,单木附藤数量多的是南方紫金牛（Ardisia thyrsiflora）;物种的聚集强度与附藤率、附藤数量呈负相关。（3）木质藤本的密度与支持木死亡率关系不显著,而物种的附藤率与死亡率呈极显著负相关。以上结果表明,木质藤本密度在原生性喀斯特季节性雨林中并不高,且木质藤本对支持木具有选择性,但其对五桠果叶木姜子群落的死亡率并未产生显著影响。该研究可为喀斯特原生性季节性雨林的物种共存、极小植物种群保育提供理论依据,也可为石漠化区域的植被修复提供科学参考。     

天然更新檫木林的能量分析

在测定天然更新檫木林的檫木[Sassafras tsumu (Hemsl.) Hemsl.]各器官热值的基础上, 建立檫木能量回归模型, 进而计算了群落能量现存量. 结果表明: 檫木各器官热值具有一定差异, 其中叶的热值最大, 树干的热值最小; 檫木树干、枝、根及全树的能量与D和 D2H(D为胸径, H为株高)回归关系达到极显著水平, 而叶的能量与D和D2H回归关系不明显; 各径级檫木树干能量的70%以上聚集在树干下部; 不同径级檫木枝的能量分布不同, 大径级主要集中在枝的中上部, 中小径级主要集中在枝的下部; 天然更新檫木林檫木的能量现存量为1.23×106 kJ·hm-2,从大至小排序依次为树干(72.58%)、根(20.15%)、枝(7.08%)、叶(0.19%).     

元江干热河谷木质藤本的多样性及其与宿主树木的关系

木质藤本是森林生态系统的重要组分。本研究在元江干热河谷地区随机设置了30个20 m×20 m的样方,调查样方中胸径≥0.5 cm的木质藤本多样性及其与宿主树木之间的关系。结果显示:30个样方中记录到胸径≥0.5 cm的木质藤本植物共945株(隶属于22种20属11科),其中,豆科木质藤本的丰富度和多度最高;胸径≤2 cm的木质藤本占个体总数的63.7%;茎缠绕类木质藤本的个体数最多。样方中胸径≥5 cm的树木共有1060株(隶属于38种31属16科),36.0%的树木上至少附藤1株。不同径级和不同树皮粗糙度的树木被木质藤本侵扰的百分比之间存在极显著差异(P0.001)。随着宿主树木平均枝下高的增加,附藤率呈下降趋势。76.5%的木质藤本选择离其根生长点最近的树木进行攀援。表明元江干热河谷中的木质藤本以小径级占优势,树木胸径、枝下高、树皮粗糙度和木质藤本根生长点到树木的距离是影响木质藤本侵扰树木的重要因素,支持木质藤本对宿主树木的侵扰具有选择性的假说。研究结果对中国西南干热河谷退化植被的恢复与物种多样性保护具有重要意义。     

黄河三角洲刺槐人工林风害成因

在调查2010年6-7月大风对黄河三角洲地区人工刺槐林的影响基础上,测定了风倒木形态指标、根系特征及其所处林窗的大小和土壤紧实度,分析滨海盐碱地人工刺槐林风倒的成因.结果表明:风倒是刺槐林遭受风害的主要形式,以胸径15 ～20 cm的树木受害最严重.随着径级的增加,风倒木的树高、冠幅、冠高和尖削度显著增加,而枝下高、冠幅/冠高和枝下高/树高变化不显著;根系长度先迅速增加而后增加缓慢,根系质量逐渐增加.随林窗面积增加,倒木株数先增加后下降,100 ～ 150 m2林窗倒木株数最多.土壤紧实度随土壤深度增加而增加,而随样木径级增加变化不显著.随径级增加,树形因子增大、根系生长受抑是刺槐风倒的重要原因,而林窗起到了促进作用.     

杉木观光木混交林群落N、P养分循环的研究

 通过对福建三明27年生杉木(Cunninghamia lanceolata)-观光木(Tsoongiodendron odorum)混交林（混交比例2：1）及杉木纯林群落N、P养分循环进行为期2年的研究。结果表明,混交林中杉木和观光木地上各组分的N、P含量大小均为叶>活枝（或皮）>枯枝>干,而根系的则随径级的减小而增大,且观光木各组分的N含量均高于杉木的;混交林群落的N、P总积累量达585.223 kg·hm－2和128.784 kg·hm－2,分别是纯林群落的1.5倍和1.3倍。混交林群落N、P养分年归     

海南霸王岭山地原始林与伐后林中木质藤本对支持木的选择

通过对海南霸王岭热带山地原始林与伐后林中树木及其攀附木质藤本的调查,研究原始林与伐后林中木质藤本对支持木的选择性。结果表明:1)6科优势树木中附藤率最高的是野牡丹科(Melastomataceae),附藤率最低的科,原始林中是山矾科(Symplocaceae),伐后林中是茜草科(Rubiaceae)。2)原始林中,谷木(Memecylon ligustrifolium)与线枝蒲桃(Syzygiumaraiocladum)的附藤比率和每木藤本数均高于样地平均水平;三角瓣花(Prismatomeris tetrandra)和龟背灰木(Symplocosandenophylla)的附藤比率均低于样地平均水平,而每木藤本数与样地平均水平之间没有显著差异。伐后林中,谷木的附藤比率和每木藤本数高于样地平均水平;九节(Psychotria rubra)的附藤比率和每木藤本数低于样地平均水平。3)杜仲藤(Parabariummicranthum)的主要支持木是谷木,夜花藤(Hypserpa nitida)的主要支持木是线枝蒲桃。研究表明,木质藤本对支持木在科和种水平上都具有选择性,因此木质藤本会对树木造成不对称影响,进而影响森林的结构和动态。     

松嫩平原野古草种群构件结构动态

野古草是根茎型无性系禾草,在松嫩平原草甸经常形成单优种群落。采用单位面积挖掘取样、分株按营养繁殖世代划分龄级、根茎按实际生活年限划分龄级的方法,对松嫩平原单优群落和混生群落的野古草种群构件结构进行了调查与分析。结果表明,在生长季初期两群落野古草种群均以春性分株和根茎芽占优势,且分株及芽构件结构相对稳定,芽库的输出率单优群落为80.4%,混生群落为62.5%;整个生长季分株由2—3个龄级组成,1a分株数量是2a的2.9—10.2倍,其生物量各月份所占比例平均为93%,随着龄级的增加依次明显减少,呈增长型年龄结构;根茎由3—4个龄级组成,根茎累积长度及生物量均以2a占绝对优势,为稳定型年龄结构;分株生产力1a明显高于2a,对种群贡献最大;根茎贮藏力除个别月份以3a、4a最高外,两群落大部分以2a最高,在生长季后期,1a根茎物质积累的速率最快。     

标准切花菊杂交F1代群体侧枝侧蕾性状的杂种优势和遗传分析

以标准切花菊〔Dendranthema morifolium(Ramat.)Tzvel.〕品种'优香'('Yuuka')为母本、品种'神马'('Jinba')为父本进行杂交,对杂交F1代群体的单株侧枝平均长度、单株侧枝数、单株侧枝数与单株叶节数的比值(R1)、主蕾直径与侧蕾直径的比值(R2)、单株侧蕾数以及主蕾与侧蕾间距离6个性状进行杂种优势和相关性分析,并利用主基因+多基因混合遗传模型检测这些性状的主基因效应.结果显示:杂交F1代群体6个侧枝侧蕾性状的变异系数为2378%~5065%,且侧枝性状的变异系数总体上高于侧蕾性状;各性状的频次均呈现连续性的正态分布趋势,说明这些性状可能属于多基因控制的数量性状.杂交F1代群体的6个侧枝侧蕾性状均在001水平上表现出显著的中亲优势,表明各性状均存在显著的杂种优势.6个性状中,单株侧枝平均长度的中亲值最大(6230 mm),R1的中亲值最小(026);单株侧枝平均长度、R2和主蕾与侧蕾间距离的中亲优势均为正值,单株侧枝数、单株侧蕾数和R1的中亲优势均为负值.6个性状的中亲优势率为-5374%~3128%,其中,单株侧枝数的中亲优势率最小,而主蕾与侧蕾间距离的中亲优势率最大.相关性分析结果显示:单株侧枝平均长度和单株侧枝数均与R1呈极显著正相关,并与R2和单株侧蕾数呈极显著负相关;R2与侧蕾数也呈极显著正相关,且二者均与主蕾与侧蕾间距离呈极显著正相关.混合遗传分析结果显示:单株侧枝平均长度、R1、R2和单株侧蕾数均受2对主基因控制,符合B-1模型,主基因表现为"加性-显性-上位性",这4个性状的遗传率分别为7707%、9672%、6438%和5307%;单株侧枝数也受2对主基因控制,符合B-2模型,主基因表现为"加性-显性",该性状的遗传率为7438%,表明这5个性状的遗传存在主基因控制效应.而主蕾与侧蕾间距离符合A-0遗传模型,说明该性状无主基因控制,易受环境影响.     

越冬代梨木虱、梨二叉蚜产卵选择对子代种间竞争的影响

梨树萌芽期,越冬代梨木虱Cacopsylla chinensis和梨二叉蚜Schizaphis piricola子代共用同一食物资源,为了解其母代如何避免子代发生种间竞争,通过研究其产卵特点表明,梨二叉蚜和梨木虱在梨树枝条上的产卵位点不同。梨木虱主要在花芽枝上进行产卵,偏好于花芽芽鳞和枝条基部刻痕处产卵,以枝条基部产卵量最多,其次为顶花芽,产卵量随芽位次序依次下降,梨木虱还可在叶芽部位产卵,但数量较少;梨二叉蚜主要于叶芽枝上进行产卵,偏好在叶芽枝的第2、3芽位产卵,顶芽和枝条基部无产卵,未见梨二叉蚜在花芽部位产卵;在花芽枝上,梨木虱卵的空间生态位大于梨二叉蚜、叶芽枝上却相反,两者在梨树枝条上的产卵空间生态位呈分离状态;梨木虱和梨二叉蚜孵化的若虫数量及空间分布特点与卵一致;对梨木虱和梨二叉蚜产卵位点分析表明,其产卵位点的物理性状明显不同。本研究明确了梨木虱和梨二叉蚜母代通过不同产卵位点的选择,降低了子代种间的同位竞争。     

DEVELOPMENT AND PHYLLOTAXIS OF THE VEGETATIVE AXILLARY BUD OF MICHELIA FUSCATA

Tucker, Shirley C. (Northwestern U., Evanston, III.) Development and phyllotaxis of the vegetative axillary bud of Michelia fuscata . Amer. Jour. Bot. 50(7): 661–668. Illus. 1963.—The vegetative axillary buds of Michelia fuscala are dorsiventrally symmetrical with 2 ranks of alternately produced leaves. The direction of the ontogenetic spiral in each of these buds is related both to the symmetry of the supporting branch and to the position of the bud along the branch. On a radially symmetrical branch, all the axillary buds are alike—all clockwise, for example. But in a dorsiventrally organized branch the symmetry alternates from clockwise in 1 axillary bud to counterclockwise in the next bud along the axis. Leaf initiation and ontogeny of the axillary apical meristem conform with those of the terminal vegetative bud. The axillary bud arises as a shell zone in the second leaf axil from the terminal meristem. During this process the axillary apex develops a zonate appearance. The acropetally developing procambial supply of the axillary bud consists wholly of leaf traces. At the nodal level the bud traces diverge from the same gap as the median bundle trace of the subtending leaf. Only the basal 1–2 axillary buds which form immediately after the flowers elongate each year, while the majority remains dormant with 3 leaves or fewer.     

多效唑和缩节胺对现蕾前忍冬枝叶生长及花蕾性状和有效成分含量的影响

以忍冬品种‘九丰一号’(Lonicera japonica‘Jiufeng 1’)为实验材料,采用叶面喷施方法研究了不同质量浓度多效唑和缩节胺对现蕾前(抽枝生长初期)枝叶生长和叶片叶绿素含量以及花蕾性状和花蕾中绿原酸和总黄酮含量的影响。结果显示:分别喷施100、400、700和1 000 mg·L-1多效唑和50、100、150和200 mg·L-1缩节胺后,多数处理组的开花枝条数、着花节数和叶绿素含量较对照CK1(水)有不同程度提高,但叶面积差异不明显。随处理时间延长,各处理组枝条节间长度总体上呈逐渐增加的趋势,其中多数处理组枝条节间长度增长缓慢。各处理的花蕾长度、百蕾鲜质量和干质量总体上小于CK1,而花蕾折干率、总黄酮含量和绿原酸含量显著或不显著高于CK1。此外,在喷施多效唑和缩节胺的同时喷施质量体积分数1.0%尿素和质量体积分数0.1%硼砂,忍冬的叶面积、着花节数、花蕾长度、折干率、百蕾鲜质量和干质量总体上有所提高,而绿原酸含量降低,但各指标的差异总体较小。研究结果表明:喷施适量多效唑和缩节胺可调控忍冬枝条生长,并能提高花蕾中总黄酮和绿原酸含量。     

Liana cover in the canopies of rainforest trees is not predicted by local ground‐based measures

Lianas (woody climbers) are structural parasites of trees that compete with them for light and below‐ground resources. Most studies of liana–tree interactions are based on ground‐level observations of liana stem density and size, with these assessments generally assumed to reflect the amount of liana canopy cover and overall burden to the tree. We tested this assumption in a 1‐ha plot of lowland rainforest in tropical Australia. We recorded 1072 liana stems (≥1 cm diameter at breast height {dbh}) ha^?1 across all trees (≥10 cm dbh) on the plot and selected 58 trees for detailed study. We estimated liana canopy cover on selected trees that hosted 0–15 liana individuals, using a 47‐m‐tall canopy crane. Notably, we found no significant correlations between liana canopy cover and three commonly used ground‐based measurements of liana abundance as follows: liana stem counts per tree, liana above‐ground biomass per tree and liana basal area per tree. We also explored the role of tree size and liana infestation and found that larger trees (≥20 cm dbh) were more likely to support lianas and to host more liana stems than smaller trees (≤20 cm dbh). This pattern of liana stem density, however, did not correlate with greater liana coverage in the canopy. Tree family was also found to have a significant effect on likelihood of hosting lianas, with trees in some families 3–4 times more likely to host a liana than other families. We suggest that local ground‐based measures of liana–tree infestation may not accurately reflect liana canopy cover for individual trees because they were frequently observed spreading through neighbouring trees at our site. We believe that future liana research will benefit from new technologies such as high‐quality aerial photography taken from drones when the aim is to detect the relative burden of lianas on individual trees.     

补光对大棚火龙果冬季促花的影响

为探讨夜间补充光照对大棚火龙果冬季植株促花的效应,以2年生‘短芯’红肉(心)火龙果植株为试材,每天夜间补光6 h,以不补光为对照,观测火龙果枝条抽蕾状况。结果显示,在平均光强500 lx、每天补充光照6 h、连续补光45 d条件下,第一批次植株抽生花蕾率达83.3%,老枝(枝龄≥12个月)抽生花蕾率为15.2%,青枝(枝龄＜12个月)抽生花蕾率为28.0%,抽生花蕾枝条占植株总枝条数的21.4%;枝条花蕾数占枝条上芽点数的比率,老枝为2.7%、青枝为2.9%。而对照植株没有抽生花蕾,抽蕾率为0。表明夜间补充光照可有效地促进大棚火龙果冬季植株抽花。     

“Lateral Control”: Phytohormone Relations in the Conifer Treetop and the Short- and Long-Term Effects of Bud Excision in Abies nordmanniana

In a conifer tree, such as Nordmann fir, Abies nordmanniana Spach, the leader bud and its immediate surroundings play a decisive role in crown architecture. As subapical branch buds are segregated from the leader meristem, resource allocation between ortho- and plagiotropic growth is determined. The relationship between treetop buds in young trees was studied in the natural state and after surgical removal in early July of either the leader bud (decapitation) or the subapical whorl branch buds (destipitation). The two bud types showed consistent cytokinin profile differences but similar seasonal dynamics in cytokinins and auxin (IAA). After bud excision, ZRP increased dramatically in the subapical stem within 1 h, followed by ZR within 1 week. Supernormal levels of ZR were maintained through autumn and persisted in spring in the destipitated trees, but had returned to normal in the decapitated trees. The treetop buds remaining after bud excision experienced an immediate decrease in most cytokinins, followed, however, by a large surplus later in the season. The following spring this high level persisted in the leader bud of destipitated trees, but not in whorl buds of decapitated trees. Conspicuous growth pattern changes followed from destipitation, but few from decapitation. Growth reactions suggest that resource allocation to main branch buds inhibits leader growth in normal trees, a kind of “lateral control.” Auxin and ABA content in buds and stems was largely unaffected by treatments. Data suggest that subapical leader tissues beneath the apical bud group are a primary source of cytokinin regulation.     

Effect of light quality (red: far-red ratio) and defoliation treatments applied at a single phytomer on axillary bud outgrowth in Trifolium repens L.

We studied the effects of light quality and defoliation on the rate of phytomer appearance and axillary bud outgrowth in white clover. The treatments were applied to one phytomer, a phytomer being defined as the structural unit comprising a node, internode, axillary bud, subtending leaf and two nodal root primordia. Light of a low red:far-red (R:FR) ratio (0.27) was applied to a target phytomer either (i) within the apical bud and then to the axillary bud after emergence of the phytomer from the apical bud, or (ii) to the axillary bud only after emergence. The light conditions were directed to these specific parts of the plant by collimating light from small FR light-emitting diodes; with this technique we were able to change the light quality without any change in the level of photosynthetically active radiation. The subtending leaf of the target phytomer was retained or defoliated when it had emerged from the apical bud. FR light applied from the time the phytomer was within the apical bud caused a delay in branch appearance at the target phytomer. In contrast, direct treatment of the axillary bud with FR light after it had emerged from the apical bud did not result in any delay in branch appearance. As the light treatment of the apical bud may have changed the light environment of any of the organs contained in the bud we were unable to ascribe the delay in branch appearance to light perception by any particular organ. However, indirect evidence leads to the conclusion that the likely site of light perception was the developing leaf subtending the axillary bud while it was the outermost phytomer within the apical bud. These results do not support the hypothesis that the R:FR ratio of light incident at an axillary bud site is the environmental factor that controls bud development. Defoliation of the unfolding leaf reduced the rate of phytomer appearance on the main stolon but had no immediate effect on branch appearance. As a consequence there was a reduction in the number of phytomers between the stolon apical meristem and the first phytomer with a branch. This is frequently taken to indicate a relaxation of apical dominance, but in this case was found not to involve a direct effect on bud activity. A current model of white clover growth suggests that there is integration of activity between apical meristems but independence of activity and response to the local micro-environment by axillary buds. In contrast, we found that (i) defoliation reduced phytomer appearance only at the main stolon apical meristem and not at all the meristems in the plant and (ii) that a change in the local light environment of an axillary bud had no discernible effect on bud activity once the bud had emerged from the apical bud but could delay branching if applied before emergence. These results are at variance with the predictions of the model.     

浙江天童常绿阔叶林栲树爆芽物候格局研究

芽的活动和芽库动态反映了植物对环境的适应方式以及生活史对策。为了研究栲树（Castanopsis farge-sii）爆芽物候特征及其生活史对策,在2008年3～6月间对栲树自然种群的爆芽物候及芽变化进行了观察,定期记录了栲树的爆芽情况,包括被标记标准枝的芽数、芽所处阶段等参数,分析研究了栲树的爆芽物候特征。结果表明：栲树芽的发育集中在3～4月下旬,芽发育过程依其形态可分为：休眠期（第一阶段B0）、萌动期（第二阶段B1）、爆芽期（第三～第五阶段B2～B4）3个时期。爆芽各阶段种群、个体、小枝的物候参数基本相同。爆芽物候进程在第三阶段为双峰曲线,在第四阶段和第五阶段呈单峰曲线。在林下和林窗两种生境下第三阶段爆芽物候在时间上基本相同,而第四、第五阶段在时间上林下比林窗滞后。栲树在爆芽阶段并不存在早开始早结束的关系,虽然芽进入各阶段的时间不同,但最终出叶时间相对集中。作为亚热带常绿阔叶树种栲树,爆芽物候受气候等多方面因素的影响,其中春季温度为最重要的影响因素,长期适应的结果使得栲树爆芽物候与环境条件的变化相协调。