985 resultados para ddc: 384.533


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利用松科植物特殊的遗传体系(叶绿体基因组一父系遗传、线粒体基因组—母系遗传、核基因组一双亲遗传),我们对高山松及其两个亲本种进行了广泛的群体取样,通过线粒体基因nadl、叶绿体基因rbcL和trnL-F基因间区以及低拷贝核基因4CL的序列分析或PCR-RFLP分析,为高山松同倍体杂种起源假说提供了翔实的遗传学证据,同时在个体水平上探讨了高山松不同群体的遗传组成、群体遗传结构、基因交流方向、群体建立过程以及杂种基因组的进化。具体结果如下: 1.细胞质基因组分析 1)线粒体基因nudl分析 本研究对油松、高山松和云南松的19个群体、295个个体的线粒体基因nadl的一个内含子进行了序列分析或PCR-RFLP分析,共检测到3种线粒体DNA单倍型-A、B和C。油松所有的取样群体仅含单倍型A;除BX群体外,所有的云南松群体仅含单倍型B; 10个高山松群体中,5个群体固定单倍型A,4个群体固定单倍型B,1个群体(ZD)分布有A和B两种单倍型。2)叶绿体rbcL基因分析 对同一组群体的rbcL基因进行序列分析或PCR-RFLP分析,共检测到两个变异位点和三种叶绿体单倍型(TT、TC和GC)。TT和GC分别是油松和云南松种特异性叶绿体单倍型,而在高山松群体里则三种单倍型均有分布,而且TC单倍型广泛地分布在7个杂种群体中,该单倍型很可能来源于点突变或第三个已灭绝的亲本。rbcL基因检测到的高山松群体分化系数很高(Gst=0.533)。 3)叶绿体trn L-F区序列分析 叶绿体trnL-F分子标记检测到的不同单倍型的差异主要是由引物“e”下游120碱基处一个多聚T结构的长度变异所致(叶绿体SSR位点)。10个高山松群体中共检测到5种叶绿体单倍型,其中两种主要的单倍型(9T和11T)分别为油松和云南松的种特异性单倍型,其他单倍型均为非典型单倍型。群体遗传结构分析表明:杂种群体表现最高的遗传多样性,而且trnL-F分析得到的高山松群体的分化系数也很高( Gst=0.443)。 总之,对高山松、油松和云南松的同一组群体取样进行的细胞质基因组分析表明:高山松群体分布有油松和云南松种特异性的线粒体和叶绿体单倍型,该细胞质DNA单倍型的地理分布为假说“高山松为油松和云南松的的二倍体杂种”提供了翔实的遗传学证据。油松和云南松在不同的杂种群体中分别做父本和母本,即两亲本在杂交过程中发生了双向基因交流。群体遗传结构分析发现高山松群体表现最高的遗传多样性,而且群体间的分化系数很高。不同的杂种群体在遗传组成上的差异表明他们经历过不同的建立和进化历史。从线粒体和叶绿体单倍型的地理分布可以看出杂种群体的建立曾经历强烈的奠基者效应和回交。青藏高原的隆升对高山松的起源、杂种群体的适应辐射以及保持产生了重要的影响。川西南和滇西北作为青藏高原的东边边界,很可能是当初云南松和油松分布的重叠区及杂交地带,即高山松的起源地。 2.核基因4CL分析 对高山松、油松和云南松的19个群体、32个个体的低拷贝核基因4CL进行了克隆及序列分析,获得的78条序列可分为两种类型(类型A和类型B)。这两种类型明显的差别是类型A相对于类型B在内含子区有- 20bp的缺失。以华山松的3条序列为外类群,对得到的78条序列进行基因谱系分析,发现所有的序列分成明显的两支,分别对应于类型A和类型B,而且每一支均包含三个种的部分序列,表明4CL基因在这三个种分化之前就已发生重复。另一个明显的特点是某个种的一条序列与另一个种的序列比其与同种的其他序列关系更近,可能因基因交流(杂交和渐渗)、非共祖、致同进化和重组等进化事件所致。三种松树中共检测到4CL基因序列的两种类型和六个亚类型,高山松群体中没有发现杂种独特的类型或亚类型。高山松和云南松共享三种序列亚类型以及最多的序列多态性,表明这两个种之间曾存在广泛的基因交流。

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We measured growth and movements of individually marked free-ranging juvenile white shrimp (Litopenaeus setiferus) in tidal creek subsystems of the Duplin River, Sapelo Island, Georgia. Over a period of two years, 15,974 juvenile shrimp (40−80 mm TL) were marked internally with uniquely coded microwire tags and released in the shallow upper reaches of four salt marsh tidal creeks. Subsequent samples were taken every 3−6 days from channel segments arranged at 200-m intervals along transects extending from the upper to lower reach of each tidal creek. These collections included 201,384 juvenile shrimp, of which 184 were marked recaptures. Recaptured shrimp were at large an average of 3−4 weeks (range: 2−99 days) and were recovered a mean distance of <0.4 km from where they were initially marked. Mean residence times in the creek subsystems ranged from 15.2 to 25.5 days and were estimated from exponential decay functions describing the proportions of marked individuals recaptured with increasing days at large. Residence time was not significantly correlated with creek length (Pearson=−0.316, P=0.684 ), but there was suggestive evidence of positive associations with either intertidal (Pearson r=0.867, P=0.133) or subtidal (Pearson r=0.946, P=0.054) drainage area. Daily mean specific growth rates averaged 0.009 to 0.013 among creeks; mean absolute growth rates ranged from 0.56−0.84 mm/d, and were lower than those previously reported for juvenile penaeids in estuaries of the southeastern United States. Mean individual growth rates were not significantly different between years (t-test, P>0.30) but varied significantly during the season, tending to be greater in July than November. Growth rates were size-dependent, and temporal changes in size distributions rather than temporal variation in physical environmental factors may have accounted for seasonal differences in growth. Growth rates differed between creeks in 1999 (t-test, P<0.015), but not in 1998 (t-test, P>0.5). We suggest that spatial variation in landscape structure associated with access to intertidal resources may have accounted for this apparent interannual difference in growth response.

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We examined movement patterns of sportfish that were tagged in the northern Indian River Lagoon, Florida, between 1990 and 1999 to assess the degree of fish exchange between an estuarine no-take zone (NTZ) and surrounding waters. The tagged f ish were from seven species: red drum (Sciaenops ocellatus); black drum (Pogonias cromis); sheepshead (Archosargus probatocephalus); common snook (Centropomus undecimalis); spotted seatrout (Cynoscion nebulosus); bull shark (Carcharhinus leucas); and crevalle jack (Caranx hippos). A total of 403 tagged fish were recaptured during the study period, including 65 individuals that emigrated from the NTZ and 16 individuals that immigrated into the NTZ from surrounding waters of the lagoon. Migration distances between the original tagging location and the sites where emigrating fish were recaptured were from 0 to 150 km, and these migration distances appeared to be influenced by the proximity of the NTZ to spawning areas or other habitats that are important to specific life-history stages of individual species. Fish that immigrated into the NTZ moved distances ranging from approximately 10 to 75 km. Recapture rates for sportfish species that migrated across the NTZ boundary suggested that more individuals may move into the protected habitats than move out. These data demonstrated that although this estuarine no-take reserve can protect species from fishing, it may also serve to extract exploitable individuals from surrounding fisheries; therefore, if the no-take reserve does function to replenish surrounding fisheries, then increased egg production and larval export may be more important mechanisms of replenishment than the spillover of excess adults from the reserve into fishable areas.