人工红树林的生长与病虫害防治的研究

为了配合“十五”863项目研究红树林修复海水滩涂养殖水的营养污染,在深圳海上田园旅游区的科技试验区鱼塘构筑种植岛种植一年生红树植物海桑(Sonneratia caseolarisL.)、桐花树(Ageiceras corniculatum(L.)Blanco)、秋茄(Kandelia candelL.Druce)并监测了解其生长发育的情况及物候期;掌握危害红树林植物生长的主要病虫害.结果表明,海桑生长速度快,各生长形态指标都远大于秋茄和桐花树,并且具有良好的抗逆特性但怕冷冻.秋茄生长速度慢,对环境的适应能力差,怕水淹,成活率最低;桐花树抗逆性强,成活率最高.红树林植物幼龄时期容易受到病虫害严重威胁,要做好防治工作,保证红树林植物的健康生长.     

海南岛红树植物海桑遗传多样性的ISSR分析

海桑 (Sonneratia caseolaris)是海桑科红树植物 ,在我国仅天然分布于海南万宁、琼海、文昌等地。采用 ISSR分子标记技术对所有天然种群和海南东寨港红树林自然保护区引种的人工种群共 4个种群 86个个体进行了遗传变异分析。 11个引物共扩增出 2 39条带 ,其中 194条具多态性 ,多态位点百分率为 81.17%。在种群水平上多态位点百分率 4 0 .5 9%～ 5 0 .2 1% ,平均值为4 5 .71%。 Nei的基因多样性、Shannon信息指数在物种水平上分别为 0 .2 10 0和 0 .32 5 6 ,在种群水平上平均值分别为 0 .14 6 8和0 .2 2 10。 Nei的遗传分化系数 Gst和 AMOVA分析表明种群间已发生了较高的遗传分化。种群间的遗传一致度为 0 .90 11。估测的种群间的基因流为 0 .5 787。依据 Nei的遗传距离对不同种群进行 U PGMA聚类 ,聚类结果为横山种群 (HS)和东寨港种群(DZG)聚在一起 ,万宁种群 (WN)和琼海种群 (QH)聚为一类。Mantel检验表明遗传距离与地理距离之间有一定的正相关 ,但不显著。种群遗传多样性与环境因子间的相关性分析表明 :海桑种群遗传多样性水平与各环境因子间相关性均不显著。因东寨港引种种群的遗传多样性明显低于天然种群 ,为保护遗传多样性 ,应加强对琼海、万宁种群的就地保护和迁地保护工作。     

无瓣海桑、海桑、秋茄红树人工林群落动态及物种多样性研究

对红树植物无瓣海桑、海桑、秋茄3种人工林群落动态及物种多样性特征的系统研究结果表明,无瓣海桑群落和海桑群落的乔木层明显分为上层和中层两个亚层,上层木为无瓣海桑或海桑,中层木主要为秋茄和桐花树;秋茄群落的乔木层为单一层次,基本由秋茄组成．在无瓣海桑群落和海桑群落中,优势种群无瓣海桑或海桑仅有高龄级个体存在,未出现自然更新现象;秋茄和桐花树为旺盛增长种群,有可能成为优势种群,表明无瓣海桑和海桑为先锋造林树种,在裸滩种植可以促进其它红树植物的天然定居生长;在秋茄群落中,秋茄为旺盛增长种群,能够自然：更新演替,桐花树和海莲属初生增长种群．无瓣海桑群落和海桑群落的物种组成和物种多样性指标较接近,基本包含秋茄群落中的主要物种秋茄、桐花和海莲。表明无瓣海桑和海桑能与这些物种协调共生,同时种植无瓣海桑或海桑可以形成多样化的红树林群落;无瓣海桑群落和海桑群落在形成初期,种植密度较大时,物种多样性较高;密度相近时。形成初期随林龄的增加。其物种多样性略有提高．     

茅尾海无瓣海桑内生细菌多样性及其细胞毒活性北大核心CSCD

【目的】对无瓣海桑各组织器官内生细菌的分布特征、物种多样性及细胞毒活性进行分析。【方法】采用稀释涂布法分析无瓣海桑内生细菌的菌落形态及分布。利用16S r RNA基因序列进行系统发育分析,探讨无瓣海桑内生细菌的物种多样性。利用MTT法测试内生细菌培养液的乙酸乙酯提取物细胞毒活性。【结果】从各组织器官中分离出内生细菌38株,隶属12科21属(其中5属未定科),内生细菌数量和群落结构组成存在明显的组织特异性。在分离的菌株中,有5株菌与已有细菌物种典型菌株的全长16S r RNA基因相似性低于97%,代表着潜在新属或新种。5株内生细菌(R74、R71、S92、S85、S84)具有较强的细胞毒活性。【结论】无瓣海桑中可培养内生细菌的物种多样性丰富,潜藏较丰富的新物种资源,且含有较为丰富的活性菌株。     

红树植物人工湿地对生活污水的净化效果

研究了潜流型海桑（Sonneratia caseolaris）人工湿地、桐花树（Aegiceras corniculatum）人工湿地和木榄（Bruguiera gymnorrhiza）人工湿地对生活污水的净化效果。一年来,3种红树植物人工湿地对BOD5、CODCr、TP、TN、NH4^＋-N和NO2^--N的平均去除率分别达到83%、71%、41%、55%、50%和84%以上。人工湿地各处理周期之间,BOD5和CODCr去除率波动较小,而TP、TN、NH4^＋-N和NO2^--N去除率波动较大。3种红树植物人工湿地对各种污染物的净化效果存在一定的差异。海桑人工湿地和桐花树人工湿地对BOD5、CODCr、TP、TN和NH4^＋-N去除率明显高于木榄人工湿地,而海桑人工湿地和桐花树人工湿地相比较,除TP外,BOD5、CODCr、TN和NH4^＋-N去除率没有显著差异。人工湿地单一处理周期内,去除率随水力停留时间（HRT）的延长而增加。BOD5、CODCr、TN和NH4^＋-N在HRT为1d和2d的去除率分别为HRT为3d去除率的54%-65%和73%-84%,NO2^--N在HRT为1d和2d的去除率分别达到了HRT为3d的70%-81%和85%-94%,而TP在HRT为1d和2d的去除率分别只有HRT为3d的39%-50%和65%-74%。另外,红树植物人工湿地与风车草（Cyperus alternifoliu）人工湿地相比,前者的BOD5、CODCr、TP、TN和NH4^＋-N去除率明显小于后者（P〈0.05）。总体上看,3种红树植物人工湿地对生活污水的净化效果呈现海桑人工湿地≈桐花树人工湿地〉木榄人工湿地。     

Effects of Season, Rainfall, and Hydrogeomorphic Setting on Mangrove Tree Growth in Micronesia

Seasonal patterns of tree growth are often related to rainfall, temperature, and relative moisture regimes. We asked whether diameter growth of mangrove trees in Micronesia, where seasonal changes are minimal, is continuous throughout a year or conforms to an annual cycle. We installed dendrometer bands on Sonneratia alba and Bruguiera gymnorrhiza trees growing naturally within mangrove swamps on the islands of Kosrae, Federated States of Micronesia (FSM), Pohnpei, FSM, and Butaritari, Republic of Kiribati, in the eastern Caroline Islands of the western Pacific Ocean. Trees were remeasured monthly or quarterly for as long as 6 yr. Annual mean individual tree basal area increments ranged from 7.0 to 79.6 cm²/yr for all S. alba trees and from 4.8 to 27.4 cm²/yr for all B. gymnorrhiza trees from Micronesian high islands. Diameter increment for S. alba on Butaritari Atoll was lower at 7.8 cm²/yr for the one year measured. Growth rates differed significantly by hydrogeomorphic zone. Riverine and interior zones maintained up to seven times the annual diameter growth rate of fringe forests, though not on Pohnpei, where basal area increments for both S. alba and B. gymnorrhiza were approximately 1.5 times greater in the fringe zone than in the interior zone. Time-series modeling indicated that there were no consistent and statistically significant annual diameter growth patterns. Although rainfall has some seasonality in some years on Kosrae and Pohnpei and overall growth of mangroves was sometimes related positively to quarterly rainfall depths, seasonal diameter growth patterns were not distinctive. A reduced chance of moisture-related stress in high-rainfall, wetland environments may serve to buffer growth of Micronesian mangroves from climatic extremes.     

Re-establishment of epibiotic communities in reforested mangroves of Gazi Bay, Kenya

Recolonization of epibiotic flora and fauna in two fringing Sonneratia alba reforestation plots was investigated and compared to a natural mangrove stand and a denuded site in Gazi Bay, Kenya. The reforested sites differed with respect to land history and planting density. Habitat availability in the form of pneumatophore surface differed among forested sites (P<0.001), and between landward and seaward zones (P<0.05). Eighteen algal species were found in the natural area compared to 23 and 10 in replanted sites. Only one species was encountered in the denuded area. SIMPER analysis distinguished Enteromorpha ramulosa, Polysiphonia sp., Hypnea sp. and Caloglossa leprieuri as the main algal species responsible for differences between sites. Algal biomass was positively correlated to pneumatophores area (P<0.001). Total algal biomass differed markedly between forested sites: 1.4 (matrix replantation), 28.6 (natural stand) and 44.3 g m⁻² (integrated replantation) in the seaward zones. The matrix replantation showed strong differences in algal community assemblages compared to the other forested sites, and this site also had significantly lower biomass of sessile benthic fauna (P<0.001). Statistical differences in algal (P<0.01) and sponge (P<0.05) community composition between landward and seaward zones were observed in all sites and trunk fouling fauna was distinctly different between sites. Reasons for the above patterns are discussed and it is suggested that zonation patterns affecting pneumatophore surface and inundation time, in combination with proximity of sites to natural seeding areas, are the most likely explanations for observed patterns of epibiotic community distribution in this study.     

中国海桑属小志

本文描述中国海桑属一新种:拟海桑(Sonneratia paracaseolaris Ko, E. Y. Chen et W. Y.Chen).重新发表海桑属7种检索表,并将原隶属海桑组的海南海桑S.hainanensis Ko, E. Y.Chenet W.Y.Chen改隶无瓣海桑组,因其过去被认为是花瓣的部分实为退化雄蕊.     

3种海桑属濒危红树植物的种群结构与动态特征

以3种海桑属（Sonneratia）濒危红树植物——海南海桑（Sonneratia × hainanensis）、拟海桑（S. × gulngai）、卵叶海桑（S. ovata）为研究对象,通过编制静态生命表,绘制存活曲线、死亡率和消亡率等曲线分析其种群结构,并用生存分析与时间序列对其未来的数量动态进行预测,以阐述其种群结构特征和动态变化规律,为海桑属濒危植物种群的保护和恢复提供基础资料和科学依据。结果显示：（1）卵叶海桑种群结构为增长型;而由于缺乏幼龄个体,海南海桑和拟海桑均为衰退型。（2）三者的种群存活曲线都表现为Deevey-Ⅱ型,各种群的死亡率和消失率曲线的变化趋势一致,并随着龄级的增加呈波状上升趋势,其中海南海桑和拟海桑均在老龄阶段遇到了障碍,而卵叶海桑幼龄个体的发展遇到了瓶颈。（3）海南海桑和拟海桑种群自我更新能力较差,未来种群数量将逐渐衰退。卵叶海桑种群具有良好的恢复潜力,未来种群数量将逐步增加,但由于其种群个体数随龄级增加呈衰减趋势,若继续保持这种态势,将有可能导致龄级断层现象。（4）人类的养殖活动导致原有生境破碎化,产生了一系列不适宜种子萌发与幼苗生长的环境因子（光照、盐度、潮汐等）,这在很大程度上抑制了海桑属濒危植物种群的自然更新。建议在加大天然种群就地保护力度的基础上,优化迁地保护策略和科学实施野外回归,并积极开展人工辅助育种工作,突破育种难题,以保证其种群的正常更新。     

国产海桑属（Sonneratia Linn．f．）植物的形态解剖

本文描述我国海南岛产的卵叶海桑、海南海桑、杯萼海桑、拟海桑、海桑等５种海桑属植物的叶、花、果实、种子、木材等的形态结构;分析它们的主要特征在各种植物之间的异同．观察结果表明,海南海桑和拟海桑两新种的形态结构特征与其它各种植物有明显的不同,并讨论它们之间的分类关系。