三种兰科植物的保护遗传学研究

本研究在野外调查的基础上，采用随机扩增多态DNA (RAPD)分析和形态学方法，研究了我国三种珍稀濒危兰科植物硬叶兜兰（Paphiopedilummicranthum）、麻栗坡兜兰（P. malipoense）和独花兰（Changnienia amoena）的遗传多样性与群体遗传结构，主要结果如下： 1．采用1 2个引物对分布于我国云贵地区的4个硬叶兜兰群体共161个体进行RAPD扩增和分析，得出物种水平的多态条带百分率（PPB）为71.6%，Nci的基因多样度(h)为0.217，Shannon多样性指数（1)为0.3301;4个群体的平均多样性水平为PPB=45.2%，h=0.1457，1= 0.2204：低于远交兰花的平均水平。分子方差分析(AMOVA)表明，在总遗传变异中，群体间遗传变异占20.31%．群体内占79.69%;POPGENE给出的基因分化系数 （Gst）为0.2958;遗传分化略高于远交物种的平均水平。空间自相关分析表明，所检测的两个群体中存在明显的空间结构，基因型在群体中以不同的小斑块存在。遗传距离和空间距离不存在相关关系。 2．用于麻栗坡兜兰的RAPD引物同上，但取样范围只有贵州的2个群体共10个个体。就所研究的个体柬看，麻栗坡兜兰的遗传多样性明显低于远交兰花物种的平均水平。物种水平上，多态条带百分率(PPB)为49.5%。Nei的基因多样度（h）为0. 1174， Shannon多样性指数(I)为0.1764：在群体水平上，上述三个指标的平均值则分别为12. 75%、0.0486和0.0712，均大大低于硬叶兜兰。然而，尽管作了种种努力，麻栗坡兜兰的取样个体数量仍很少，因此所得结果可能会有误差。 3．用16个引物对分布于河南、湖北、湖南、江西4个省11个独花兰群体共216个体进行了RA PD扩增和分析，独花兰在物种水平PPB=80. 7%，h=0.197．1=0. 3116;在群体水平，上述三个指标的平均值则分别为40. 9%、0.1247和0. 1902，均低于远交兰花的平均水平。AMOVA分析表明，11个独花兰群体间的遗传变异占43.48%，群体内的占56.52%：在神农架和新宁地区内部，群体间的遗传变异分别占13.68%和49.3g%(AMOVA)。POPGENE给出的11个群体的基因分化系数(Gst)为0.3580．神农架和新宁地区内的Gst，值分别为0.1194和0.2597。可见，群体间的遗传分化明显高于远交物种的平均水平。空间自相关分析表明，独花兰的遗传变异在群体内不存在明显的空间结构。群体之间的遗传距离和空间距离不存在相关关系。 4．对独花兰7个群体形态性状的分析发现，12个形态性状在群体内均有较高的变异性，cv值变动于0.022-0.30O。庐山群体(LS)在所有性状上的平均值均为最高。营养性状和花部性状的变异性基本一致。除花葶长和花距直径与某些花部性状之间没有显著的相关关系外，各性状之间均有显著的相关性。对XN4群体的统计没有发现假磷茎数目与其他性状之间存在显著相关性。 根据以上对硬叶兜兰、麻粟坡兜兰和独花兰遗传多样性和群体遗传结构韵研究，结合其他方面的资料;对三种兰花的濒危机制进行了初步的分析。首先，人为采挖和破坏是导致这些兰花物种濒危的直接原因，尤其是麻栗坡兜兰。其次， 适宜兰花生存的生境正在只益萎缩、退化和片段化。这两方面因素的共同作用导致上述兰花群体的数目和规模日益下降，由此引发的遗传多样性降低和遗传结构的改变进一步加剧其濒危状况。对于独花兰而言，较低的繁殖能力又使其生存状态雪上加霜。针对三个物种不同的繁殖特性和遗传学状况，提出如下保护措施。(1)硬叶兜兰由于繁殖能力较强、现存个体尚多，遗传多样性损失不甚严重，因此以保护其所在的生境为基础、实施原位保护，是比较合适的保护策略。(2)麻粟坡兜兰目前受破坏程度非常严重;所剩个体很少，遗传多样性较低，已经很难进行有效的原位保护。因此;应利用迁地保护手段抢救目前尚存的个体。(3)独花兰的繁殖能力较弱，因此在保护生境和严禁采摘的基础上，可采用人工授粉等方式，提高结实率、增加繁殖效率，促使其复壮：在进行迁地保护时，则应注意不同群体间存在较大遗传变异而群体内多样性较低这一现实。

Shifts in the estuarine demersal fish community after a fishery closure in Puget Sound, Washington

Puget Sound is one of the largest and most ecologically significant estuaries in the United States, but the status and trends of many of its biological components are not well known. We analyzed a 21-year time series of data from standardized bottom trawl sampling at a single study area to provide the first assessment of population trends of Puget Sound groundfishes after the closure of bottom trawl fisheries. The expected increase in abundance was observed for only 3 of 14 species after this closure, and catch rates of most (10) of the abundant species declined through time. Many of these changes were stepwise (abrupt) rather than gradual, and many stocks exhibited changes in catch rate during the 3-year period from 1997 through 2000. No detectable change was recorded for either temperature or surface salinity over the entire sampling period. The abrupt density reductions that were observed likely do not reflect changes in demographic rates but may instead represent distributional shifts within Puget Sound.

芦笋抗氨基酸及氨基酸类似物突变体的筛选

由芦笋无菌苗诱导得到的愈伤组织，经甲基磺酸乙酯（EMS）诱变处理后，进行抗氧乙基半胱氨酸(AEC)和赖氨酸加苏氨酸(Lys十Thr)的突变体筛选工作，得到如下结果: ①AE C可抑制芦笋愈伤组织的生长，但此抑制作用可被赖氨酸或甲硫氨酸都分解除。利用AEC的抑制作用筛选得到抗0.5mMAEC的愈伤组织AR10并再生植株。AR10愈伤组织离开选择剂两代后仍保持对AE C的抗性。还发现抗性愈伤组织对2mM的半胱氨酸的抑制作用具有交叉抗性，对1mM的Lys+Thr的抑制作用有较弱的交叉抗性。AR10的再生植株一部分表出对A EC的抗性，另一部分则无抗性氨基酸分析表明，抗性愈伤组织内游离赖氨酸、苏氨酸、甲硫氨酸和异亮氨酸有所增加，而在开生植株中发现了半胱氨酸和赖氨酸的特异性增加（分别是对照的4•56和5 •39倍)。AR10的抗性机理目前尚不清楚。 ②2mM的Lys十Thr Lys+Thr对芦笋愈伤组织生长具有抑制作用。甲硫氨酸可部分解除.Ly s十Thr的抑制作用。用2mM的Lys+Thr筛选得到的抗性细胞系LTR2. LTR3，在离开选择压力一代，细胞增殖五倍的情况下仍保持对选择剂的稳定抗性。LTR2、L T R3愈价组织对A E C如仰制作用表现出部分的交叉抗性。另外还发现抗性系对苏氨酸(2mM )的生长抑制作用具有抗性，对赖氨酸(2mM)的生长抑制作用却无抗性，氨基酸分析表明。LTR2LTR3愈份组织内游离赖氨酸含量明显提高(分别是对照的2•18和2.67倍)，另发现一种峰值介于赖氨酸与游离氨之间的未知氨基酸增加更为显著(分别是对照的4•03和11•42倍)。这些结果表明抗性愈伤组织内氨基酸合成的某些关键酶可能发生了改变，对末端物的反馈抑制敏感性有所降低。

Seascape ecology of coastal biogenic habitats: advances, gaps, and challenges

We review the progress made in the emerging field of coastal seascape ecology, i.e. the application of landscape ecology concepts and techniques to the coastal marine environment. Since the early 1990s, the landscape ecology approach has been applied in several coastal subtidal and intertidal biogenic habitats across a range of spatial scales. Emerging evidence indicates that animals in these seascapes respond to the structure of patches and patch mosaics in different ways and at different spatial scales, yet we still know very little about the ecological significance of these relationships and the consequences of change in seascape patterning for ecosystem functioning and overall biodiversity. Ecological interactions that occur within patches and among different types of patches (or seascapes) are likely to be critically important in maintaining primary and secondary production, trophic transfer, biodiversity, coastal protection, and supporting a wealth of ecosystem goods and services. We review faunal responses to patch and seascape structure, including effects of fragmentation on 5 focal habitats: seagrass meadows, salt marshes, coral reefs, mangrove forests, and oyster reefs. Extrapolating and generalizing spatial relationships between ecological patterns and processes across scales remains a significant challenge, and we show that there are major gaps in our understanding of these relationships. Filling these gaps will be crucial for managing and responding to an inevitably changing coastal environment. We show that critical ecological thresholds exist in the structural patterning of biogenic ecosystems that, when exceeded, cause abrupt shifts in the distribution and abundance of organisms. A better understanding of faunal–seascape relationships, including the identifications of threshold effects, is urgently needed to support the development of more effective and holistic management actions in restoration, site prioritization, and forecasting the impacts of environmental change.