广东黑石顶森林群落黄果厚壳桂（Cryptocarya concinna）幼…

黄果厚壳桂幼苗未有准确对应于年龄的外部特征,通过相应样地中幼苗的解析,得出了以幼苗高度和基径对年龄的二元线性回归相对准确地划分幼苗年龄的方法,它优于单纯采用高工级或基径级划分年龄结构的方法,这种方法为非毁坏性的研究现存幼苗的结构提供了依据。     

广东黑石顶森林群落黄果厚壳桂幼苗出生和死亡特征

对黑石顶森林群落中黄果厚壳桂种群幼苗的出生和死亡的定位研究结果表明：黄果厚壳桂幼苗具有低出生率和低死亡率的特点,一年中以幼苗旺盛生长的季节死亡率最高,且死亡者主要是１年生和２年生的幼苗,３年以上幼苗很少死亡。幼苗出生和死亡与种群密度、林内光照及土壤水分的相关性因幼苗生长的群落环境不同而不同     

广东黑石顶森林群落黄果厚壳桂幼苗出生和死亡特特

对黑石顶森林群落中黄果厚壳桂种群幼苗的出生和死亡的定位研究结果表明：黄果厚壳桂幼苗具有低出生率和低死亡率的特点,一年中以幼苗旺盛生长的季节率最高,且死亡者主要是１年生和２年生的幼苗,３年以上幼苗很少死亡,幼苗出生和死亡与种群密度,林内光照及土壤水分的相关性因幼苗生长的群落环境不同而不同。     

黑石顶南亚热带常绿阔叶林优势种群黄果厚壳桂的AFLP分析

以扩增片段长度多态性（AFLP）分析了黑石顶南亚热带常绿阔叶林优势种群黄果厚壳桂（Cryptocarya concinna)在三个不同群落类型中的遗传多态性及遗传结构,并比较了该3个种群间的遗传分,以4对AFLP选择引物组合产生了大量扩增表型带,用AMOVA、PHYLIP等软件分析计算了种群的遗传结构。结果表明黑石顶黄果厚0壳桂种群具有高的种群内遗传多态性、低的种群间遗传分析。并讨论了种群遗传变化与生境的关系。     

广东黑石顶厚壳桂(Cryptocarya chinensis)不同年龄级遗传多样性

采用ISSR分子标记对广东省黑石顶地区厚壳桂(Cryptocarya chinensis)不同年龄级(成体、小树、幼苗)的遗传多样性进行研究.结果表明,和具有相同生活史特征的物种相比,黑石顶厚壳桂遗传多样性水平较低,总的基因多样性为0.0901;不同年龄级遗传多样性由成体-小树-幼苗逐渐降低,分别为0.0880、0.0793、0.0648.3个年龄级间的遗传分化为Gst=0.1410,st=0.0659(AMOVA).这一地区厚壳桂种群低的遗传多样性是由于这一地区森林片断化后,种群隔离导致不同地区种群间基因流的不畅通、个体数量缩小使得种群内遗传漂移作用加剧.但种群世代间遗传分化可能由取样误差导致的遗传漂变所产生.     

南亚热带森林片断化对厚壳桂种群遗传结构的影响

森林片断化是造成全球生物多样性丧失的主要原因,但从种群遗传学角度开展的研究还远远不够。因此,本文采用ISSR(inter-simplesequencerepeat)方法对广东省鼎湖山、黑石顶、大雾岭、古田、萝岗和饶平6个地点的南亚热带片断化森林中的厚壳桂(Cryptocaryachinensis)种群的遗传多样性进行了研究。每个种群分成体、小树和幼苗3个年龄级采样,共采集厚壳桂样品448个。7个ISSR引物共扩增出209条多态性带。研究结果表明,6个厚壳桂种群的总遗传多样性为0.1529,种群平均遗传多样性为0.0537。和保护较好的厚壳桂种群相比,萝岗和饶平的两个村边林种群的遗传多样性较低。6个厚壳桂种群间的遗传分化系数(GST)为0.6489。AMOVA分析结果表明,总的遗传变异中,67.97%(P<0.0002)的遗传变异存在于种群间,2.06%(P<0.01)的遗传变异存在于不同年龄级之间,29.96%(P<0.0002)的遗传变异存在于种群内。基于遗传距离的UPGMA分析结果表明,6个厚壳桂种群大致分成两支:一支包括大雾岭和黑石顶2个种群,另一支包括其他4个种群。鼎湖山、古田、大雾岭和黑石顶不同年龄级均各自聚合在一起。可以看出,森林的破碎化导致了南亚热带厚壳桂种群遗传多样性降低,种群间基因流受阻,提示我们对于同一地区的易危物种,这种威胁将很大,急需开展相关的保护研究。     

鼎湖山黄果厚壳桂粗死木质残体的分解

通过建立时间序列法、测定粗死木质残体的密度变化,研究鼎湖山黄果厚壳桂粗死木质残体三个直径(5~10cm、10~20cm和20~30cm)的分解过程,探讨粗死木分解过程中C、N元素及其C/N比值与分解速率的关系。结果表明粗死木质残体的分解常数K值随直径的增加从0.2225a-1呈指数降低到0.1257a-1,由粗死木质残体在分解过程中密度变化得出三个直径从小到大分解95%所需的时间分别为13a、19a和24a;黄果厚壳桂粗死木质残体在分解过程中不存在时滞效应,其树皮和心材的分解速度也相近,用单因素数指数方程能准确反映黄果厚壳桂的分解过程;与高纬度地区比较,鼎湖山黄果厚壳桂粗死木残体的分解速率常数K值显著高于前者。还就粗死木残体基质组成和性质、气候与环境条件、生物等因素对粗死木分解速率的影响进行了详细的讨论。     

模拟氮沉降对南亚热带两种乔木幼苗生物量及其分配的影响

探讨了南亚热带季风常绿阔叶林两种优势树种荷木(Schima superba)和黄果厚壳桂(Cryptocarya concinna)幼苗的生物量及其分配对氮沉降增加的响应。实验分为对照(CK)、T₅、T₁₀、T₁₅和T₃₀ 5个处理,每个处理设置3次重复。所施氮肥为NH₄NO₃,以溶液方式喷施,5个处理浓度分别为0、0.12、0.24、0.36、0.72 mol N·L^-1。每月喷施2次,5个样方1年喷施的总氮量分别相当于氮沉降率0、5、10、15、30 g N·m^-2·a^-1。经过11个月的施氮处理,两种幼苗对氮沉降的响应存在差异,其中黄果厚壳桂幼苗的基径、株高、全株生物量和相对生长速率除最高处理T₃₀外,均高于对照,但荷木幼苗的基径、全株生物量和相对生长速率除T₁₀外,均小于对照。氮处理也对生物量的分配产生了明显的影响,两种幼苗的叶重比以T₃₀最低,表明高氮处理不利于幼苗叶片的生长;枝重比均以T₃₀最高,反映了高氮处理的幼苗生物量分配到枝干的比例最高;根重比和根冠比均以对照样方幼苗的最高,表明氮处理抑制根的生长,分配到根部分的生物量下降。总的来看,经过11个月的处理,除最高处理T₃₀外,氮处理仍对黄果厚壳桂幼苗的生长有促进作用,而对荷木幼苗的生长则趋向于一定程度的抑制效应,表明黄果厚壳桂幼苗更能耐受高氮条件。     

新疆野核桃自然保护区不同坡向野核桃幼苗种群年龄结构及生长特征

为了解国家Ⅱ级渐危植物新疆野核桃不同年龄幼苗的数量组成及生长特性,在野核桃自然保护区不同坡向上设置4个2-hm²样地,应用相邻格子样方法对野核桃幼苗进行逐株调查,分析了野核桃幼苗种群的数量组成、基径和株高的生长特征及各性状间的生长关系.结果表明: 阳坡、半阳坡、阴坡和半阴坡野核桃1龄幼苗均较丰富,1～3龄幼苗数量均占绝对优势,不同坡向野核桃幼苗种群均呈增长型年龄结构.各坡向野核桃1龄幼苗平均5.7%可存活到4龄,平均1.7%可以存活到7龄.3龄是野核桃幼苗数量的一个转折点,幼苗种群在生活史中采用的是r对策.野核桃幼苗的基径和株高在3龄前生长缓慢,3龄后加快生长;基径平均生长速率为3.6 mm·a^-1,按阴坡、阳坡、半阴坡、半阳坡顺序减小;株高平均生长速率为9.0 cm·a^-1,按阳坡、半阳坡、半阴坡、阴坡顺序减小.不同坡向野核桃幼苗的基径与株高均随年龄的增加呈指数函数生长,株高与基径呈幂函数异速生长,幼苗各性状间的生长快慢可通过函数的性质和参数反映出来.     

光强对四种亚热带树苗生长特征影响的比较

鼎湖山亚热带森林优势树种藜蒴、荷木、黄果厚壳桂和马尾松2－3年生树苗,盆栽于16％、40％和100％的自然光下生长16个月．3种阔叶树无论在全自然光还是在弱光下均能较好地存活,遮光下的马尾松则出现不同程度的死亡．全光下的马尾松、黄果厚壳桂树苗的基径和树高生长大于遮光下的树苗．4个树种的侧枝数均随光照的减弱而下降．在不考虑新老叶更新的情况下,全光下的藜蒴、黄果厚壳桂单株叶片数大于弱光下的树苗,而荷木则相反．如果以全光下单株树苗干物质量为100％,那么在相对光照为40％和16％下生长的马尾松、黄果厚壳桂、荷木和藜蒴单株树苗的干物质量分别为57．4％和32．7％、73．8％和62．1％、78．0％和78．6％、93．9％和76．2％．不同光强下的藜蒴、荷木地上部分干物质量的变化不大,地下部分则随光照的减弱而下降,马尾松、黄果厚壳桂无论地上还是地下部分干物质量均随光强的减弱而明显减少．遮光下生长的3个阔叶树种树苗的冠根比（CRR）、叶重比（LWR）、叶面积比（LAR）和比叶面积（SLA）均高于全光下的树苗．马尾松为喜光树种,对阴生环境的适应能力极为有限;黄果厚壳桂为耐阴树种,在全光下仍然比遮光条件下生长较快．     

Distribution ofAcer palmatum seedlings under the crown of the maternal tree

To investigate the relationship between crown width of a parent plant and seedling distribution, seedling ages and sizes, and their distances from the maternal tree were surveyed under a maple (Acer palmatum) crown at Chungdam Park, Chungdam-dong, Kangnam-gu, Seoul, in 1998. Maple crown width increased 33.0 cm per year during the eight-year study. Seedlings ranged from 1 to 10 years old; their density was highest the third year, and decreased with age. Seedling-distribution ranges from the parent plant were 43 cm to 487 cm, and seedling density was highest at the border of the parent plant canopy. One-year-old seedlings were distributed broadly, but the main distribution areas became more distant from the maternal plant with seedling age. Seedling heights increased with age; differences between two consecutive ages were significant at the 0.1% level for ages less than 5 years, but not for over 6 years. For seedlings of the same age, heights were similar, but short under the tree crown, but were varied and taller outside the crown. The variation in seedling height increased with age and distance from the parent plant In particular, seedlings older than 5 years that were distributed outside the crown showed conspicuous variations among distance classes. Therefore, maple seedlings were distributed to an appropriate distance at which their growth could be supported by the understory-light environment. This study demonstrated that newA. palmatum trees are not recruited from the seedlings growing beneath the crown but from those that grow vigorously outside the crown.     

林窗对热带雨林冠层树种绒毛番龙眼幼苗生长的影响

在林窗中央、林窗边缘和林冠下3种不同光照梯度的森林生境中,研究了西双版纳季节雨林冠层树种绒毛番龙眼幼苗的早期 (种子萌发后10周内) 生长和定居后 (实生苗生长3个月以上) 的生长特点.结果表明: 绒毛番龙眼幼苗在早期生长阶段,林窗中央的株高、基径、总干质量、单株叶面积和相对生长率最大,分别为24.45 cm、3.17 mm、0.79 g、122.45 cm²和14.78×10^-3 g·d^-1.林冠下根冠比 (0.87) 高于林窗中央 (0.20) ,可能是光照和水分共同作用的结果.林窗中央较强的光照有利于定居后幼苗的生长,株高、基径、总干质量、单株叶面积、相对生长率和净同化率均在林窗中央最大,实验结束时分别达到31.48 cm、3.80 mm、2.22 g、174.52 cm²、2.29×10^-3 g·d^-1和2.54×10^-5 g·cm^-2·d^-1.幼苗死亡可能与水分胁迫密切相关,由水分胁迫引起的幼苗死亡率在林冠下最高 (26.88%),但林冠下由脊椎动物捕食引起的幼苗死亡率较低(2.93%),从而使林冠下幼苗的最终存活率最高 (70.19%).光照是影响绒毛番龙眼幼苗形态学调节的重要因素, 林窗中央不同生长阶段幼苗的比叶面积最低,但相对生长率和净同化率最大.水分胁迫和光照在幼苗定居后仍是影响幼苗生物量分配的重要因素, 林窗边缘幼苗的根冠比最高 (0.33).     

长白山不同演替阶段温带森林林下草本植物对乔木幼苗的影响

为了解次生针阔混交林和阔叶红松林林下草本植物对幼苗生长和存活的影响,基于长白山次生针阔混交林样地(Ⅰ)和阔叶红松林样地(Ⅱ),以246个1 m×1 m幼苗样方中乔木幼苗为研究对象,通过去除草本植物的对照试验探究草本植物对乔木幼苗高度生长和存活率的影响。结果表明,(1)群落水平上,草本植物去除有助于林下乔木幼苗的高度生长。次生针阔混交林和阔叶红松林中幼苗高度生长量在除草后较对照组均有显著提高,且阔叶红松林中幼苗高度增长在对照组和处理组中均高于次生针阔混交林。(2)去除草本植物对不同年龄级水平乔木幼苗高度生长影响不同。次生针阔混交林中,去除草本显著促进四年生及以上幼苗高度生长,对一至三年生幼苗影响不显著;阔叶红松中去除草本显著促进一至三年生幼苗高度生长,对四年生及以上幼苗影响不显著。(3)除草处理后,水曲柳幼苗高度生长量在两处样地均显著增加,假色槭幼苗高度增长量只在次生针阔混交林中显著增加,而其他幼苗高度增长量只在阔叶红松林中显著增加。(4)次生针阔混交林中,幼苗存活率与草本多度和物种数呈正相关关系,与草本盖度无相关关系;阔叶红松林中幼苗存活率与草本物种数呈正相关关系,与草本多度和盖度无相关关系。结果表明,草本植物会抑制乔木幼苗高度生长;虽可能在一定程度上有助于改善微生境,但未显著提高幼苗存活率。     

广东松幼苗存活率和生长特征的初步研究

2006年5月至2008年7月,在南岭国家级自然保护区测定了不同年龄、不同种植方式的广东松(Pinus kwangtungensis)幼苗的存活率、株高和基径等指标,以期为国家保护植物广东松的保育提供资料。结果表明,实验期间袋栽苗存活率下降明显,从开始时的100%下降到结束时的50%;裸植苗与移植苗的存活率从100%下降到80%左右。总月均株高、基径的增量,袋栽苗、裸植苗、移植苗依次为1.01、1.39、2.76cm;0.17、0.20、0.64mm。年均株高、基径增值,移植苗、裸植苗、移植苗依次为32.91、17.22、12.77cm;7.64、2.31、2.0mm。随着年龄的增长,各组幼苗的株高和基径增长均加快,株高与基径之间存在着极显著的线性相关关系,广东松幼苗至10a生仍属快速生长期。     

Effects of burial in sand and water supply regime on seedling emergence of six species

BACKGROUND AND AIMS: Air seeding has long been regarded as a quick and successful measure for vegetation rehabilitation in China. However, seedling emergence of often-used species including Agriophyllum squarrosum, Artemisia sphaerocephala, Artemisia ordosica, Hedysarum fruticosum, Caragana korshinskii and Medicago sativa is low. Experiments were conducted under controlled conditions to study the effects of sowing depth and water supply on seedling emergence, in order to understand the requirements for increasing seedling emergence. METHODS: Seeds were exposed to different environments of burial and water supply regimes in PVC pots (7 cm in diameter and 11 cm in height) under the same light intensity and alternating temperature regimes in a growth chamber. KEY RESULTS: Seedlings of three species (Agriophyllum squarrosum, Artemisia sphaerocephala, Artemisia ordosica) with relatively light seeds emerged well at a 0.5 cm sowing depth under a 7.5 and 10 mm water supply regime. However, few seedlings of these species emerged when the sowing depth was over 1 cm or when water supply was 5 mm. Seedlings of Caragana korshinskii, Hedysarum fruticosum and Medicago sativa emerged from sowing depths of 0.5-4 cm, 0.5-3 cm, and 0.5-4 cm, respectively, under both 7.5 and 10 mm water supply regimes. Under a 5 mm water supply regime, seedlings of these species also emerged at over 1 cm sowing depth. Seeds of all six species sown on the surface of sand did not germinate, and seedlings did not emerge when they were sown at depths greater than 6 cm. CONCLUSIONS: Based on these experiments, a 0.5 cm sowing depth resulted in the highest seedling emergence and it is concluded that this is the optimal sowing depth for seedling emergence of all six species.     

疏花水柏枝幼苗生物量与构件对模拟土壤地下水位变化的响应

通过模拟不同地下水位的方法,对疏花水柏枝（Myricaria laxiflora（Franch.）P.Y.Zhang et Y.J.Zhang）一年生幼苗在不同条件下地上与地下部生物量及构件的变化进行测定,分析幼苗生长对地下水位变化的响应。结果显示：随着地下水位的降低,疏花水柏枝幼苗的生长特征指标均呈先增加后减少的趋势,其中地上、地下部分生物量的最高值分别为0.0438、0.0100 g,最低值分别为0.0177、0.0026 g。幼苗地上部生物量在-10 cm处理水平最高;地下部生物量在-15 cm处理水平最高。幼苗直径、根表面积、株高、主根长度、根体积、一级枝数、二级枝数等指标也分别在-10 cm或-15 cm处理水平达到最高值。疏花水柏枝幼苗主要构件的生长与地下水位的变化存在显著相关性。主成分分析结果表明,幼苗的地下部分更容易受到土壤地下水位变化的影响,幼苗性状症候群随地下水位的变化而发生移动,说明该物种幼苗在不同地下水位时的生长投资策略具有较大差异。     

Drivers of seedling survival in a temperate forest and their relative importance at three stages of succession

Negative density dependence (NDD) and niche partitioning have been perceived as important mechanisms for the maintenance of species diversity. However, little is known about their relative contributions to seedling survival. We examined the effects of biotic and abiotic neighborhoods and the variations of biotic neighborhoods among species using survival data for 7503 seedlings belonging to 22 woody species over a period of 2 years in three different forest types, a half‐mature forest (HF), a mature forest (MF), and an old‐growth forest (OGF), each of these representing a specific successional stage in a temperate forest ecosystem in northeastern China. We found a convincing evidence for the existence of NDD in temperate forest ecosystems. The biotic and abiotic variables affecting seedlings survival change with successional stage, seedling size, and age. The strength of NDD for the smaller (<20 cm in height) and younger seedlings (1–2 years) as well as all seedlings combined varies significantly among species. We found no evidence that a community compensatory trend (CCT) existed in our study area. The results of this study demonstrate that the relative importance of NDD and habitat niche partitioning in driving seedling survival varies with seedling size and age and that the biotic and abiotic factors affecting seedlings survival change with successional stage.     

Relationships of weight and height with age in hybrid Holstein-Friesian/Guzera females

Serial data on live weights, height at withers and the weight/height ratio of 263 cows (3 to 9 years old) and 196 heifers (2 to 5 years old) were studied. The animals were of six red and white Holstein-Friesian (HF)/Guzera crosses (1/4, 1/2, 5/8, 3/4, 7/8 and > or = 31/32 HF-expected gene fraction). Separate analyses were performed for cows and heifers using the Proc Mixed of the SAS package. Models included the fixed effects of farm, season, reproductive and lactation status, two-factor interactions, quadratic regressions on age and age x crossbred group interaction, as continuous co-variables and regressions on the HF gene fraction and on breed heterozygosity, plus the animal random effect. Only heifer growth in height and weight/height was linear with age. In all three traits in both categories the individual additive-dominance model explained the variation between crossbred groups. The breed additive difference was not significant (P > 0.05) for cow and heifer live weight and for heifer weight/age ratio. Heterosis was significant for all traits except height of cows. Linear and quadratic regression coefficients for cows, were, respectively, for live weight, 35.20 +/- 5.23 kg/year and -1.54 +/- 0.43 kg/year2, for withers height, 2.49 +/- 0.29 cm/year and -0.15 +/- 0.02 cm/year2 and for weight/height, 0.22 +/- 0.04 kg/cm/year and -0.01 +/- 0.003 kg/cm/year2. Corresponding values for heifers were, for live weight, 153.46 +/- 37.06 kg/year and -15.69 +/- 4.91 kg/year2, while only linear coefficients applied to withers height (1.63 +/- 0.43 cm/year) and weight/height (0.16 +/- 0.03 kg/cm/year).