21 resultados para Genetics of osteoporosis

em Chinese Academy of Sciences Institutional Repositories Grid Portal


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As the only remainder type of phycobiliproteins in Prochlorococcus, the actual role of phycoerythrin still remains unknown. Previous studies revealed that two different forms of phycoerythrin gene were found in two ecotypes of Prochlorococcus that are specifically adapted to either high light (HL) or low light (LL) conditions. Here we analyze patterns of phycoerythrin nucleotide variation in the HL- and LL-Prochlorococcus populations. Our analyses reveal a significantly greater number of non-synonymous fixed substitutions in peB and peA than expected based on interspecific comparisons. This pattern of excess non-synonymous fixed substitutions is not seen in other five phycoerythrin-related genes (peZ/V/Y/T/S). Several neutrality statistical tests indicate an excess of rare frequency polymorphisms in the LL-Prochlorococcus data, but an excess of intermediate frequency polymorphisms in the HL-Prochlorococcus data. Distributions of the positively selected sites identified using the likelihood ratio test, when mapped onto the phycoerythrin tertiary structure, reveal that HL- and LL-phycoerythrin should be under different selective patterns. These findings may provide insights into the likely role of selection at the phycoerythrin locus and motivate further research to unveil the function of phycoerythrin in Prochlorococcus.

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Crassostrea ariakensis is an important aquacultured oyster species in Asia, its native region. During the past decade, consideration was given to introducing C. ariakensis into Chesapeake Bay, in the United States, to help revive the declining native oyster industry and bolster the local ecosystem. Little is known about the ecology and biology of this species in Asia due to confusion with nomenclature and difficulty in accurately identifying the species of wild populations in their natural environment. Even less research has been done on the population genetics of native populations of C. ariakensis in Asia. We examined the magnitude and pattern of genetic differentiation among 10 wild populations of C. ariakensis from its confirmed distribution range using eight polymorphic microsatellite markers. Results showed a small but significant global theta (ST) (0.018), indicating genetic heterogeneity among populations. Eight genetically distinct populations were further distinguished based on population pairwise theta (ST) comparisons, including one in Japan, four in China, and three populations along the coast of South Korea. A significant positive association was detected between genetic and geographic distances among populations, suggesting a genetic pattern of isolation by distance. This research represents a novel observation on wild genetic population structuring in a coastal bivalve species along the coast of the northwest Pacific.

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Premise of the study: Microsatellite markers were developed for Pinus koraiensis to characterize its genetic diversity and understand its population structure. Methods and Results: Using the Fast Isolation by AFLP of Sequences COntaining (FIASCO) Repeats protocol, 20 primer sets were developed in Chinese populations of P. koraiensis. Three of the markers showed polymorphism with two alleles per locus when assessed in a sample of two populations of P. koraiensis from the Changbai Mountain in the Jilin Province of China. Five and three loci were successfully amplified in P. taiwanensis and P. massoniana, respectively. The amplification size of these loci matches those in P. koraiensis. Conclusions: These markers may be useful for further investigation of population genetics of P. koraiensis.

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Wuchang bream (Megalobrama amblycephala) is an economically important fish in China. From a (GT)(13)-enriched genomic library, 20 microsatellites were developed. Nine of these 20 loci were polymorphic in a test population with allele numbers ranging from two to four, and the observed and expected heterozygosities ranging from 0.2609 to 0.7826 and from 0.3739 to 0.7546, respectively. In the cross-species amplifications, six of these nine loci were also polymorphic in white amur bream (Parabramis pekinensis). These polymorphic microsatellite loci are potentially useful for population genetics of Wuchang bream and its closely related species.

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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。

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种间杂交在自然界中普遍存在。杂交可以为群体带来多方面的遗传改变,具有重要的进化生物学意义。越来越多的证据表明,同倍性杂交物种形成是一种重要物种形成途径,在动、植物物种进化中扮演着重要的角色。同倍性杂交物种形成意味着一个稳定的、可育的、与亲本种间形成生殖隔离的杂种群体建立起来,但不改变染色体的数目。这种生殖隔离被认为是通过快速的染色体重组、生态分化、或空间分离形成的。对于现存杂交种的对比分析和对同倍性杂交物种形成的理论模拟都表明,适应性分化和生态转变在同倍性杂交物种形成中起着至关重要的作用。来自于生态成种的研究也表明生态选择自身就可以导致生殖隔离的形成和新物种的形成。尽管如此,我们对同倍性杂交物种形成过程的研究仍然较多地关注于染色体重组及相应的遗传效应;对于自然选择,特别是生态选择在同倍性杂交成种过程中的作用模式缺乏全面地了解。 本研究以同倍性杂交种-高山松为研究对象,利用地理信息学技术、基于天然群体取样的性状对比分析和人工杂交手段,全面地定量描述了高山松及其亲本种间的生态分化、生态转变下的天然群体生殖适应性、以及生态选择下的形态变异和种间杂交可配性。以此探讨了高山松的杂交成种过程,生态转变和自然选择的重要性以及它们与杂交种适应性、形态变异和生殖隔离之间的关系。利用地理信息学手段,对高山松及其亲本种间的生态分化对比分析表明:高山松与其亲本种间形成了明显的生态转变;在自然选择的作用下,高山松已经具备了对于青藏高原东南缘横断山区高山地带独特的生态适应性;相对于亲本种,它的适应性特征体现为混合型,在某些性状上它高出亲本种的适应性,在另一些性状上,它体现出居中、较低或者类似于亲本种适应性;高山松适生区由于地形地貌的复杂性,往往不连续,呈间断状。基于四个反映结实效率的性状、小孢子母细胞减数分裂异常现象及花粉萌发率在种间的对比分析表明,这些反映生殖状态的指标,在三个种及群体间并没有显著差异;相对于亲本种的天然群体,居于青藏高原的高山松群体,表现出了正常的授粉效率和生殖适应性。高山松天然群体正常的生殖效率表明,它经历了生态转变过程中的选择作用,已经具备了在新生境下,繁殖发展下去的生殖适应性。 在大规模群体取样的基础上,通过对反映植物个体发育和营养状态的球果和针叶形态性状的对比分析,我们发现,高山松及其亲本种间的形态变异存在以下特征:第一,绝大多数性状,在种间和种内群体间都存在着显著的差异,并且大部分性状的差异主要体现在种间;第二,高山松在大部分形态性状上介于两个亲本种之间,少数性状表现为超亲分离、类似于某个亲本或无种间差别;第三,在多数性状上,和亲本种相比,高山松群体都拥有较大的变异幅度。第四,在临近亲本种的群体中,高山松的形态特征更类似于所临近的亲本种。上述形态变异特征及其与气象、土壤、经纬度、海拔等因子间普遍的相关性,意味着生态选择在高山松成种过程中起了重要作用。总的来说,形态性状变异的总体模式揭示出:高山松在选择作用下的遗传和表型的精炼过程中已经形成了自身适应于高原环境的、稳定而有效的形态发育模式和资源利用方式,甚至是恰当的防御机制。 本研究通过云南松×油松的单交实验和油松×高山松部分双列杂交实验,检验了高山松及其亲本种间的杂交可配性。结果表明,就平均水平而言,高山松及其亲本种间的种间杂交结实可配性低于种内杂交,但个别种间杂交组合的结实可配性可能高于种间杂交;高山松及其亲本种间正在或已经形成了部分的合子后生殖障碍;现存的高山松群体及其亲本种间的生态地理隔离可能是很有效的生殖隔离形式,一方面做为合子前生殖隔离,它能避免种间相互传粉、阻碍种间杂交的发生,另一方面做为合子后生殖隔离,它能清除掉可能存在的劣势回交产物。 综合已有的证据,我们提出了高山松同倍性杂交物种形成模型:高山松的同倍性杂交成种是与青藏高原隆升过程以及隆升过程中所产生的全新生态空间紧密相关的;青藏高原隆升导致了生态环境的剧变,创造了全新的生态位,在选择的作用下,拥有综合了双亲遗传基础的杂种基因型开始占领这个全新的生态位;在分化的生态选择的持续作用下,杂种基因型在新的生境下稳定下来,形成了独立于亲本种的资源利用方式、形态特征和繁育系统,具备了完善的生殖和生态适应性;此时,一个与亲本种间以生态隔离存在的同倍性杂交种-高山松形成了;随着分化的生态选择的持续进行,高山松与亲本种间的内在生殖隔离不断加强。

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滇金丝猴(Rhinopithecus bieti)是我国著名的濒危保护动物.迄今为止,关于滇金丝猴并基于DNA序列的群体遗传学研究还没有报道.文章测定了来自于云南省维西县滇金丝猴群体样本的线粒体控制区全序列以及部分个体的细胞色素b全序列.在排除了核线粒体假基因存在的可能性之后,滇金丝猴维西群体内部被确认存在着两个序列分歧较大的分枝.即使如此,如果考虑到群体结构和迁移的影响,维西群体的遗传多样性水平可能并不高.

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Although new empirical evidence shows that sympatric speciation has occurred in some species, there are few indisputable model organisms for this process of speciation. The two subspecies (Gymnocypris eckloni eckloni and G. e. scoliostomus) of the schizothoracine Gymnocypris fish species complex from a small glacier lake in the Tibetan Plateau, Lake Sunmcuo, fit several of the key characteristics of the sympatric speciation model. We used combined mitochondrial control region sequences and the cytochrome b gene (1894 bp) to address the phylogenetics and population genetics of 232 specimens of G. e. eckloni and G. e. scoliostomus, as well as all of its closely related sister species. We found that: (i) a total of four old lineages were uncovered in the widespread G. e. eckloni, of which only one was shown to be shared with all G. e. scoliostomus individuals and (ii) the new subspecies (G. e. scoliostomus) evolved in Lake Sunmcuo from the ancestral G. e. eckloni population within approximately 0.057 Ma. These two taxa of the species complex are morphologically distinct, and reproductive isolation is further suggested. Ecological disruptive selection based on morphological traits (e.g. mouth cleft characters) and food utilization may be a mechanism of incipient speciation of two sympatric populations within Lake Sunmcuo. This study provides the first genetic evidence for sympatric speciation in the schizothoracine fish.

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川金丝猴(RhinoPithecusroxellana)是我国著名的珍稀濒危保护动物,但是,现有的群体遗传学研究成果并不能满足科学合理的制定其遗传保护策略的要求。这主要是因为前人研究的遗传标记均是相对比较保守的功能基因,因此无法检测到足够的变异,进而也无法进行精细的分析。有鉴于此,我们选取了进化速率较快的线粒体控制区作为遗传标记,并对来自于三个主要栖息地的川金丝猴样本进行了群体遗传学研究。我们在线粒体控制区中观察到了大量的变异,这和前人的工作结果形成了强烈的反差。通过基于溯祖理论的最大似然法估算,我们得到现存川金丝猴群体的总的有效群体大小在700一2,300只以内,同时其最近共同祖先的年代在19,000-62,700年前左右。线粒体控制区的结果表明现存川金丝猴群体可能起源于眠山群体,我们称之为单起源假说,但是由于样本限制,多起源的可能性仍然存在。整个川金丝猴群体表现出显著的内部分化的信号,甚至氓山群体内部还存在一个序列分歧非常大的分枝,这可能是由其特殊的社群结构以及较弱的基因交流造成的,并且由于群体结构和分化信息的拮抗作用,我们并没有直接检测到瓶颈效应。通过和相关濒危与非濒危物种的比较,我们认为川金丝猴群体的遗传多样性水平并不低,提示其濒危的状态主要是由随机因素造成的而非遗传因素的结果。虽然我们在线粒体控制区中发现了大量的变异,但是前人在蛋白质电泳的研究中并未检出多态,同时,川金丝猴特殊的社群结构是否会影响其在核基因水平上的群体遗传结构也是十分有趣的问题,因此,为了从核基因组的角度进一步研究川金丝猴的遗传多样性,并实现对核基因和核外基因的比较,我们对样本的14个微卫星座位做了检测。我们发现这些微卫星座位均存在多态,所有地方群体的平均杂合度均大于0.5;地方群体间存在着显著的分化;地方群体间有效群体大小比率的估计值和群体大小比率的野外观测值非常接近。通过对比线粒体数据,我们认为川金丝猴的社群结构对其群体的遗传结构有着重要的影响,首先表现在核基因有更大的基因流水平,其次还表现在我们可以检测到眠山群体和秦岭群体在近期均经历了瓶颈效应,说明在核基因水平上群体结构信号的影响要弱于线粒体基因。但是,通过和其它物种比较,微卫星的数据却表明川金丝猴的遗传多样性水平并不高于其它的濒危动物,这和线粒体控制区的结果相反。这主要是当以微卫星为标记时,群体的历史动态对于当前群体的多态程度的影响力有限所致。微卫星的结果表明了保护川金丝猴群体的紧迫性。我们还通过细胞色素b基因证明了线粒体控制区中的巨大分歧不是由核假基因的造成的。巧合的是前人也在川金丝猴群体中对该基因进行过研究,但是结果却相反,即我们发现的变异水平远远高于他们的结果。为此,我们比较了两项工作的数据,我们推测在前人的工作中可能存在着潜在的测序错误。不过,如果没有出现污染的话,这两项工作的综合结果可以直接支持我们前面提到的单起源假说。此外,通过细胞色素b基因的分析,我们还估算出川金丝猴和滇金丝猴(R.bieti)的分歧时间大致在0.7-2.3百万年之间。镇金丝猴(R.biti)也是我国著名的濒危保护动物,它是川金丝猴的近缘种,其濒危等级甚至还要高于川金丝猴。迄今为止,关于滇金丝猴并基于DNA序列的的群体遗传学研究还没有见诸于报道。我们测定了来自于云南省维西县镇金丝猴群体样本的线粒体控制区全序列以及部分个体的细胞色素b全序列。在排除了核线粒体假基因存在的可能性之后,我们确认滇金丝猴维西群体内部也存在着两个序列分歧较大的分枝,但是,这可能是邻近群体迁移而来的产物。因此,如果考虑到群体结构和迁移的影响,我们认为维西群体的遗传多样性水平可能并不高。在以上的研究中,我们使用了大量的群体遗传学方法,但遗憾的是,目前还没有一套令人满意的侧重于群体遗传学分析的程序工具库。为了简化今后工作的复杂度和难度,我使用OCAAML语言编制了一套程序工具集(Pan'sToolKit,PTK)。OCAML是一门优秀的计算机语言,它既支持快速开发,又支持高速运行,是理想的算法实现语言。基于OCAML的PTK库集成了许多实用工具以及群体遗传学算法,尤其是溯祖理论的算法。PTK库不仅可以用于处理常规的实验数据,而且还可以用于辅助理论和算法的研究。

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近十年,植物群体遗传学的研究飞速发展,然而与海拔相关的植物群体遗传结构和遗传变异研究却相对较少。到目前为止,还不清楚遗传变异与海拔之间是否有一个通用的格局。在山区,各种生态因子,如温度、降水、降雪、紫外线辐射强度以及土壤成分都随海拔梯度急剧变化,造成了即使在一个小的空间区域,植被类型变化显著,这种高山环境的异质性和复杂性为我们研究植物群体遗传结构和分化提供了方便。沙棘(Hippophea)属于胡颓子科(Elaeagnaceae)为多年生落叶灌木或乔木,雌雄异株,天然种群分布极为广泛。中国沙棘(H. rhamnoides subsp. sinensis)是沙棘属植物中分布较广的一个亚种,种内形态变异非常丰富,加之其具有独特的繁育系统和广泛的生态地理分布,是研究沙棘属植物遗传变异和系统分化的理想材料。本文从1,800 m 到3,400 m 分5 个海拔梯度进行取样,用RAPD 和cpSSR 分子标记研究了卧龙自然保护区中国沙棘天然群体的遗传结构和遗传变异。5 个取样群体依次标记为A、B、C、D 和E,它们分别代表分布在海拔1,800,2,200,2,600,3,000 和3,400 m 的5 个天然群体。RAPD实验用11 条寡核苷酸引物,扩增得到151 个重复性好的位点,其中143 个多态位点,多态率达94.7%。在5 个沙棘群体中,总遗传多样性值(HT)为0.289,B群体内的遗传多样性值为0.315,这完全符合沙棘这种多年生、远交的木本植物具有高遗传变异的特性。5 个群体内遗传多样性随海拔升高呈低-高-低变异趋势,在2,200 m海拔处的B群体遗传多样性达最大值0.315,3,400 m海拔处的E群体则表现最小仅0.098。5 个群体间的遗传分化值GST=0.406,也即是说有40.6%的遗传变异存在于群体间,1,800 m海拔处的A群体与其它群体的明显分离是造成群体间遗传分化大的原因。UPGMA聚类图和PCoA散点图进一步确证了5 个群体间的关系和所有个体间的关系。最后,经过Mantel检测,遗传距离与海拔表现了明显的相关性(r = 0.646, P = 0.011)。cpSSR 实验中,经过对24 对cpSSR 通用引物筛选,11 对引物能扩增出特异性条带,只有2 对引物(ccmp2 和ARCP4)呈现多态性。4 个等位基因共组合出4 种单倍型,单倍型Ⅰ出现在A 群体的所有个体和B 群体的8 个个体中,C、D、E 三个群体均不含有,而单倍型Ⅱ出现在C、D、E 三个群体的所有个体及B 群体的18 个个体中,A 群体不含有。另外两种单倍型Ⅲ和Ⅳ为稀有类型,仅B 群体中的4 个个体拥有。这种单倍型分布模式和TFPGA 群体聚类图揭示了,C、D、E 群体可能来源于同一祖先种,而A 群体却是由另一祖先种发展起来的,B 群体则兼具了这两种起源种的信息,这可能是因为在历史上的某一时期,在中国沙棘群体高山分化的过程中,B 群体处某个或者某些个体发生了基因突变,具备了适应高海拔环境的能力,产生了高海拔沙棘群体的祖先种。 In recent ten years, studies about population genetics of plants developed rapidly,whereas their genetic structure and genetic variation along altitudinal gradients have beenstudied relatively little. So far, it is uncleared whether there is a common pattern betweengenetic variation and altitudinal gradients. In the mountain environments, importantecological factors, e.g., temperature, rainfall, snowfall, ultraviolet radiation and soil substratesetc., change rapidly with altitudes, which cause the vegetation distribution varying typically,even on a small spatial scale. The mountain environments, which are heterogeneous andcomplex, facilitate and offer a good opportunity to characterize population genetic structureand population differentiation.The species of the genus Hippophae L. (Elaeagnaceae) are perennial deciduous shrubs ortrees, which are dioecious, wind-pollinated pioneer plants. The natural genus has a widedistribution extending from Northern Europe through Central Europe and Central Asia toChina. According to the latest taxonomy, the genus Hippophae is divided into six species and12 subspecies. The subspecies H. rhamnoides ssp. sinensis shows significant morphologicalvariations, large geographic range and dominantly outcrossing mating system. Thesecharacteristics of the subspecies are favourable to elucidate genetic variation and systemevolution. To estimate genetic variation and genetic structure of H. rhamnoides ssp. sinensisat different altitudes, we surveyed five natural populations in the Wolong Natural Reserve at altitudes ranging from 1,800 to 3,400 m above sea level (a.s.l.) using random amplifiedpolymorphic DNA markers (RAPDs) and cpSSR molecular methods. The five populations A,B, C, D, and E correspond to the altitudes 1,800, 2,200, 2,600, 3,000 and 3,400 m,respectively.Based on 11 decamer primers, a total of 151 reproducible DNA loci were yielded, ofwhich 143 were polymorphic and the percentage of polymorphic loci equaled 94.7%. Amongthe five populations investigated, the total gene diversity (HT) and gene diversity within population B equaled 0.289 and 0.315, respectively, which are modest for a subspecies of H.rhamnoides, which is an outcrossing, long-lived, woody plant. The amount of geneticvariation within populations varied from 0.098 within population E (3,400 m a.s.l.) to 0.315within population B (2,200 m a.s.l.). The coefficient of gene differentiation (GST) amongpopulations equaled 0.406 and revealed that 40.6% of the genetic variance existed amongpopulations and 59.4% within populations. The population A (1,800 m a.s.l.) differed greatlyfrom the other four populations, which contributes to high genetic differentiation. A UPGMAcluster analysis and principal coordinate analyses based on Nei's genetic distances furthercorroborated the relationships among the five populations and all the sampling individuals,respectively. Mantel tests detected a significant correlation between genetic distances andaltitudinal gradients (r = 0.646, P = 0.011).Eleven of the original 24 cpSSR primer pairs tested produced good PCR products, onlytwo (ccmp2 and ARCP4) of which were polymorphic. Four total length variants (alleles) werecombined resulting in 4 haplotypes. The haplotype was present in all individuals of Ⅰpopulation A and 8 individuals of populations B, the other three populations (C, D and Epopulations) did not share. The haplotype was present in all individuals of populations C, D Ⅱand E and 18 individuals of populations B, population A did not share. The other twohaplotypes and were rare haplotypes, which were only shared in 4 individuals of Ⅲ Ⅳpopulation B. The distribution of haplotypes and TFPGA population clustering map showedthat the populations C, D and E might be origined from one ancestor seed and population Amight be from another, whereas population B owned information of the two ancestor seeds. Itwas because that gene mutation within some individual or seed in the location of population Bwas likely to happen in the history of H. rhamnoides, which was the original ancestor of thehigh-altitude populations.

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依据线粒体上ND2和CO1两个变异较大的基因序列分析了香港地区香港湍蛙7种群、华南湍蛙1种群,以及大陆其他地区华南湍蛙7种群,戴云湍蛙1种群,武夷湍蛙1种群的系统发育关系,进而探讨香港湍蛙的遗传多样性、香港湍蛙特有性、如何确定香港湍蛙最佳保护单元以及这四种湍蛙的物种分类地位。 1. 香港湍蛙保护遗传学研究 香港湍蛙核苷酸传多样性较低,从其遗传多样性信息、单倍型网络分析、中性检验值以及岐点分布结果一致显示香港湍蛙很可能经历了瓶颈后的扩张,种群正在由一个较小的有效种群大小迅速增长, 有足够的时间通过变异用于积累单倍型的多态性, 而对于提高核苷酸多样化而言, 时间尚短(Nei M et al,1975,Avise J C,2000;李明等,2003)。 分子变异分析结果显示香港湍蛙种群间存在较多的基因交流,且系统发育树上各种群间交叉在一起,没有形成与地理单元相关的分支,而从其单倍型网络看,他们源于共同的祖先,是一个单系群,与地理单元间没有形成显著的遗传分化。因此应作为一个进化显著单元(ESU)。结合其与其他湍蛙发育关系及遗传距离以及野外采集信息认为香港湍蛙只在香港地区有分布,属于香港特有种。该物种内遗传多样性较低,又属于世界自然保护联盟红皮书中的近危种,同时也是《野生动物保护条例》中的受保护野生动物,且由于香港城市建设等使得其栖息环境受到威胁,因此在香港特别行政区应该受到重点保护。 从单倍型分布和核苷酸多样性可以看出大榄涌种群和城门种群具有较高的单倍型多样性和核苷酸多样性,应该作为保护的重点区域。 2. 华南湍蛙东、南沿海种群间系统关系 华南湍蛙分布广,各种群存在着丰富的遗传多样性信息且中部种群广西龙胜和湖南张家界种群核苷酸多样性明显高于其他边缘种群华南湍蛙。种群间几乎没有基因交流,且各种群间无共享单倍型,可见已形成了显著的遗传分化。各种群间遗传距离都较远,其中广东南昆山种群以及福建三港种群与其他种群距离最远,因此可以推测其他种群(广东深圳、香港大屿山、广西龙胜和防城以及湖南张家界种群)可能为独立进化的种群。但是否是一新种或一隐存种,还需要结合形态学进行更深入的研究。 本研究中无论从系统关系看还是从遗传距离看,大屿山种群与深圳种群最近,支持陈坚峰等将其定为华南湍蛙,即华南湍蛙新增一个分布点:香港大屿山。 系统树上广西防城种群(支B)与龙胜和湖南种群(支A)形成姐妹群。香港大屿山种群与深圳种群先形成姐妹群(支C),但却没有与其距离很近的广东南岭及南昆山种群(支D)形成姐妹群,可能粤北和粤中的环境及气候较复杂因此与粤南其他种群形成了明显的隔离。同时可以看出华南湍蛙种群遗传分化与地理距离没有显著的相关性。 3. 四种湍蛙间的系统关系 根据线粒体CO1基因建立四种湍蛙间的系统关系及其遗传距离,很清楚地看到,香港湍蛙与戴云湍蛙关系很近,而华南湍蛙则与武夷湍蛙较近。然而,戴云湍蛙同一个种群内部共有两个单倍型DY1和DY2,且两个单倍型间遗传距离大于DY1与香港湍蛙间遗传距离,更远远大于香港湍蛙种群内部的距离,即戴云湍蛙内部两个单倍型间遗传距离达到了种级水平,同样在系统发育树上这两个单倍型与香港湍蛙形成并系。但是,戴云湍蛙种内在形态上差异不显著。因此,其是否属于萌芽物种分化形成(budding speciation)或已经完全分化为两个不同的种值得进一步研究? 与戴云湍蛙香港湍蛙关系类似,从系统树上看华南湍蛙不形成单系,而是分成两个大支,与武夷湍蛙形成并系,且福建和南昆山的华南湍蛙与武夷湍蛙遗传距离远大于武夷湍蛙种内福建种群与浙江种群的遗传距离,达到了种级分化水平。由此,可以推断武夷湍蛙是有效种。系统树上广东深圳、香港大屿山、广西防城和龙胜以及湖南张家界种群与华南湍蛙福建及南昆山各种群间遗传距离已超出了种内各种群间的遗传距离,但是至于这一支是否应为另外一个种,有必要扩大采样,并结合核基因及形态信息进行进一步研究。 MtDNA of ND2 and CO1 gene were used to investigate genetic diversity of Amolops in Hongkong .We collected seven populations of A. hongkongensis,,one population of A.ricketti from Hong Kong and other seven populations of A.ricketti from East and South of Chinese mainland. As well as one population of A. daiyunensis and one population of A.wuyiensis Phylogenetic relationship were analyzed of four species. Discussed whether A.hongkongensis is an endemic species and how can we make the conservation and management decisions. 1. Conservation Genetics of A. hongkongensis A. hongkongensis has a low nucleotide diversity, the results of genetic diversity, haplotype network, neutrality test and the mismatch distributions indicate that A. hongkongensis experienced a recent expansion after a bottle neck. They had enough time to accumulated haplotype diversity, but it’s too short to have a high nucleotide diversity(Nei M et al,1975,Avise J C,2000;Li et al,2003). The result of AMOVA reveals that it has much gene exchange among the populations of A. hongkongensis. The clades of the phylogenetic tree were mixed together, no significant genetic differentiation among 8 populations and they share the same ancestor from the network analysis, these indicate that they are monophyly and should be protected as one ESU. Combined with the information of relationships of interspecies, genetic distance and distribution investigate, We conclude that A. hongkongensis is an endemic species of Hong Kong. Considering on the status of low genetic diversity in A.hongkongensis, and this species was listed in the IUCN red list as near threatened, as well as listed in the . Furthermore, it’s habitat loss and degradation more rapidly as the human activity got higher and higher. So it’s urgent to protect them in Hong Kong. Our results suggest that Tai Lam Wu and TAI MO Shan -Shing Mun populations have the higher priority to be protected because their higher genetic diversity. 2.Phylogenetic relationships among populations of Amolops ricketti from the Southern and eastern China A. ricketti has the considerable genetic diversity of mitochondrial haplotypes within and among populations, and Mitochondrial DNA diversity was higher in populations at the central area of the present distribution range of the frog,i. e. the Longsheng population and Zhangjiajie population, than at the edges of their distribution range. They have no share haplotype among populations, and have a significant genetic differentiation. Genetic distance is high among the populations, especially the distance of Nankun and Sangang group with others, which suggested that they evolved independently. May be there is a cryptic species or a new species, a further study is needed. The results of gene tree and the genetic distance clearly demonstrate that the population from LanTau island is A. ricketti, so we agree with Chen et al(2005) . That means A.ricketti have a new distribution site: LanTau island, HongKong. Phylogenetic relationships were analyzed through NJ and Mrbayes methods and got a consistent topological structure, the structure indicated that the ingroup were comprised four groups. Populations Longsheng and Zhangjiajie were first clustered as clade A; Populations Fangcheng was clustered together (clade B) as a sister group to clade A;Populations Shenzhen and Lantau island were sister groups and clustered as clade C;Then the clade D included populations Nankunshan and Nanling in Guangdong province and Sangang in Fujian province. 3. Phylogenetic Relationships among these four specises Phylogenetic relationships based on 1503bp CO1 gene and the genetic distance show that A. hongkongensis close to A. daiyunensis whereas A.ricketti near to A.wuyiensis. Nevertheless, there are two haplotypes in A.daiyunensis and the genetic distance between them higher than the distance between DY1 with A. hongkongensis. A. hongkongensis is nested in the paraphyletic ancestral species A. daiyunensis. Without significant difference in the morphological characters, So, we considered both A.daiyunensis and A.hongkongensis are valid species, may be this represents a case of ‘budding speciation’ like Batrachuperus pinchonii(Fu and Zeng,2008) in the population of A. daiyunensis. Just like two species above A. wuyiensis and A. ricketti are not monophyly, instead, A.wuyiensis is nested in the paraphyletic ancestral species A.ricketti. We need do more research to make sure whether they are new species.