用mtDNA序列鉴定出上海海域 须鲸科物种大村鲸

测定了采自上海海域的一头死亡须鲸骨骼样本的线粒体DNA（mtDNA）细胞色素b基因（Cyt b）序列330 bp（登录号MK295815）、细胞色素C氧化酶Ⅰ基因（COⅠ）序列206 bp（登录号MK317953）和控制区（control region）序列231 bp（登录号MK317954）。通过GenBank中的BLAST分析,结果表明,样本的上述三部分序列与大村鲸（Balaenoptera omurai）对应序列的相似性均达到100%,基于最大似然法（ML）法构建的系统发育树与BLAST结果一致,故将标本鉴定为大村鲸,为上海海域首次记录。     

线粒体DNA序列分析在中国水域真海豚物种鉴定中的初步应用

真海豚包括长喙真海豚( Delphinus capensis) 和短喙真海豚( D. delphis) 2 种, 而中国水域的真海豚到底是哪一个种或是否同时有两个种的存在, 并不清楚。本研究测定了12 头中国水域真海豚mtDNA 控制区(control region) 366 bp 和细胞色素b (cytochrome b , cyt b) 基因336 bp 的序列, 并与已发表的其它真海豚的序列合并分析,初步鉴定中国水域真海豚的分类地位。结果表明, 中国水域的真海豚与东太平洋的长喙真海豚有相同的鉴别位点, 且两者之间的核苷酸歧异度(控制区: 1.93 ±0.22 % , cyt b 基因: 0.68 ±0.19 %) 显著低于与短喙真海豚之间的差异(控制区: 2.92 ±0.41 % , cyt b 基因: 0.95 ±0.27 %) 。通过MEGA (molecular evolutionary genetic analysis) 软件中的邻接法(neighbor joining) 进行的系统发生分析中, 中国水域的真海豚与长喙真海豚聚成一支, 有明显较近的亲缘关系。因此, 中国水域的真海豚在分类上应归属于长喙真海豚。     

利用Cyt b基因由未知鲸骨鉴定出大村鲸

作者于2005年2月从广东省湛江市硇洲岛一位渔民手中采集到一块鲸类的脊椎骨,据渔民对该搁浅鲸类的外形描述推断该骨骼属于一种大型须鲸.为了鉴定该脊椎骨所属的种类,本文利用分子生物学技术,从中提取基因组DNA,并以此为模板特异性扩增Cyt b基因的部分序列进行物种鉴定.     

板角山羊mtDNA Cyt b基因变异特点及系统进化研究

测定了板角山羊品种13个个体的细胞色素b基因全序列(1140 bp),比较分析了群体中细胞色素b基因的碱基组成和序列间碱基的变异情况,结果显示:在该品种(群体)中细胞色素b基因序列中6个变异位点上观察到11次T-C间和2次A-G间的碱基转换,除了有2次T-C间碱基转换发生在密码子第2位点为非同义突变以外,其余的11次碱基转换发生在密码子第3位点,均为同义突变;有1次T-G间碱基颠换发生在密码子第2位点,为非同义突变;观察到5种单倍型,单倍型多样度为0.8077.并以绵羊为外群,与山羊属其他种的同源区序列构建系统发生树.结果显示, 在系统地位上板角山羊与胃石山羊有较近的亲缘关系.     

大林姬鼠两亚种线粒体DNA 细胞色素b 基因和控制区的序列多样性

为了研究大林姬鼠两亚种(韩国的指名亚种及中国东北和内蒙古地区的东北亚种)线粒体DNA 的变异程度并确定朝鲜亚种的分类地位,我们分别将来自韩国和中国东北长白山地区的两亚种的线粒体DNA 的细胞色素b 基因和控制区进行了测序分析。我们将测序所得到细胞色素b 基因序列与来自基因库的大林姬鼠5 个亚种的相应的单倍型进行了分析,结果显示大林姬鼠可分为4 个类群[类群1:韩国大林姬鼠指名亚种;类群2:中国长白山和内蒙古地区的东北亚种、俄罗斯外加贝尔的majuculus 亚种;类群3:中国长春的东北亚种、俄罗斯Primorye(俄罗斯远东地区) rufulus 亚种、俄罗斯库页岛(俄罗斯远东地区)和日本北海道地区的giliacus 亚种;类群4:中国黑龙江海林地区的东北亚种]。线粒体的控制区序列分析显示韩国指名亚种也不同于中国东北地区的东北亚种。本研究的类群1,2 和3 与Serizawa et al. (2002)的研究的K、S 和R 的分支相对应。这表明韩国指名亚种(类群1 和分支K)的线粒体DNA 与其他类群不同。另外,我们还发现在细胞色素b 基因构建的系统树中,东北亚种可以与类群2 (分支S)及类群3 (分支R 的不同亚种聚合在一起。我们认为线粒体DNA 的母性遗传与两个相邻亚种的个体之间的种内杂交造成了基于细胞色素b 序列对东北亚种的聚类分析结果与基于形态学特征的分类结果的不一致。因此,我们提出对这些显示出核苷酸序列多样性的东北亚种不能只用细胞色素b的数据进行亚种分类,还应该结合形态学和核DNA 特征进行进一步分析。最后,我们还发现韩国的指名亚种的细胞色素b 序列在平均距离16. 93% 的基础上不同于来自基因库的A. speciosus。Jones and Johnson (1965)指出了韩国的大林姬鼠在形态上的区别,所以我们认为韩国的大林姬鼠指名亚种A. p. peninsulae 是一种具有形态和遗传特异性的地方亚种。     

基于mtDNA Cytb 的六种果实蝇的分子鉴定

本研究首次对果实蝇属的桔小实蝇Bactrocera dorsalis、瓜实蝇B. cucurbitae、南瓜实蝇B. tau、番石榴实蝇B. correcta、具条实蝇B. scutellata、黑漆实蝇B. scutellaris等6种实蝇mtDNA Cytb基因进行了测序。对这6种实蝇72个个体mtDNA Cytb基因中段420 bp的碱基序列进行分析,得到38种单倍型,发现了116个变异位点,其中30个位点较为稳定。对这6种实蝇与其各自鉴别位点的对应关系研究表明,mtDNA Cytb基因可以作为这6种实蝇种类鉴别的分子标记。     

基于线粒体DNA细胞色素b基因和控制区序列分析西藏雅鲁藏布江黄斑褶鮡种群遗传多样性

采用线粒体DNA（mtDNA）Cyt b基因和D-loop控制区为分子标记,对分布于西藏雅鲁藏布江大峡谷以上里龙段和以下墨脱段2个群体的黄斑褶 （Pseudecheneis sulcata）共60个样本进行遗传多样性研究。获得联合基因有效序列长度为1 893 bp,包括Cyt b基因1 060 bp和D-loop控制区833 bp。结果显示,里龙和墨脱2个群体的单倍型多样性值（Hd）均较高（0.701和0.761）,核苷酸多样性值（π）均较低（0.001 00和0.001 09）;高频率的单倍型Hap1和Hap2为2个群体所共享,推测为祖先单倍型;同时,里龙和墨脱群体分别存在5个和6个特有单倍型,且在2个群体中不共享;分子方差分析（AMOVA）显示遗传变异主要来源于种群内部,群体间呈中度遗传分化水平（Fst = 0.090 44,P < 0.05）;中性检验（Tajima''s D、Fu''s Fs）和核苷酸不配对（SSD、Hir）分析结果揭示,黄斑褶 种群曾经历过种群扩张现象。本研究推测,黄斑褶 2个群体间的基因流动存在障碍,雅鲁藏布大峡谷的海拔落差及水文情势等生态屏障可能是阻碍黄斑褶 迁徙和交流的主要原因。     

淮河野生鲇鱼线粒体Cyt b基因的序列变异与遗传结构分析

本研究利用线粒体DNA细胞色素b(Cyt b)基因序列分析淮河信阳段、淮滨段、蚌埠段、洪泽湖及其支流颍河、淠河和池河的野生鲇鱼(Silurus asotus)种群遗传结构及种群历史.结果表明,在841 bp的同源序列中,7个种群共检测到变异位点40个,占全部序列的4.76％,121个个体共检测到32种单倍型;7个种群的平均单倍型多样性(h)、核甘酸多样性(Pi)分别为0.884 8、0.003 8,表明淮河野生鲇鱼种群的遗传多样性水平较高.7个种群间的遗传分化指数Fst为0.115 0,仅12.92％的变异来自种群间(AMOVA分析),基因交流值为3.85,种群间K2-P遗传距离为0.002 ～0.009,显示鲇鱼种群间没有发生明显的地理分化.NJ树揭示7个种群的个体组成2个谱系,但这2个谱系与地理分布并不相关.中性检验、错配分析和Network网络亲缘关系分析皆表明鲇鱼种群有过种群扩张,扩张时间约在0.17～0.29百万年前的中更新世中期和末期.     

黑线姬鼠两亚种(中国东北地区及俄罗斯远东地区的东北亚种和朝鲜半岛的朝鲜亚种) 的线粒体DNA 序列缺少趋异性

为了检测黑线姬鼠两亚种(来自中国东北地区、俄罗斯远东地区的东北亚种和朝鲜半岛的朝鲜亚种)线
粒体DNA 的变异水平并确定朝鲜亚种的分类地位,我们测序分析了两亚种的线粒体DNA 细胞色素b 的部分序列
(1 054 bp)和控制区的部分序列(860 bp),并与基因库中黑线姬鼠相应的单倍型序列进行了比较。可以看出东
北亚种的序列显示出某些分异,可以被分为2 或3 个亚群,所以我们提出需要更多标本的DNA 分析来确定东北
亚种的分类地位。另外,来自韩国的朝鲜亚种的序列,与来自中国东北地区龙江和哈尔滨的东北亚种的两个亚
群相似(1 个亚群是细胞色素b 的两个单倍型,另1 个是控制区的两个单倍型),表明基于线粒体DNA 序列的遗
传多样性与现今基于形态特征对这些姬鼠的分类所得结果是不一致的。因此我们认为来自韩国的朝鲜亚种是一
个只在形态特异上不同于东北亚种的地方亚种,我们建议通过其他DNA 标记来进一步验证其亚种地位。我们还
认为朝鲜半岛不是最近的冰川期黑线姬鼠残遗种的保护区。     

Stejneger's beaked whale strandings in Alaska, 1995–2020

Presented here is the first comprehensive and updated compilation of history, distribution, and findings of Stejneger's beaked whales (Mesoplodon stejnegeri) in Alaska. Stejneger's beaked whales are a poorly understood, elusive, deep-diving cetacean species found in the North Pacific Ocean. Since Stejneger's beaked whale strandings data in Alaska through 1994 were last published, 35 additional strandings have been documented. Twenty-seven animals stranded in the Aleutian Islands, seven stranded in Southcentral Alaska, and one animal stranded on St. Lawrence Island. Twenty-two carcasses were necropsied, but only four were fresh. Seventeen of the 22 died during mass stranding events and cause of death could not be definitively determined. Barotrauma was suspected in three cases and infectious disease possibly complicated by barotrauma occurred in two cases. We documented an expansion of strandings into the northern Bering Sea, characterized a sex bias, examined stomach contents that included macroplastic, and identified parasites not previously associated with Stejneger's beaked whales. Also included are data on the largest known mass stranding of Stejneger's beaked whales, which occurred on Adak Island in 2018. The history, distribution, and findings presented here are central to further our understanding of this species.     

OBSERVATIONS OF AN UNIDENTIFIED BEAKED WHALE (MESOPLODON SP.) IN THE EASTERN TROPICAL PACIFIC

Multiple sightings of a distinctive but unidentified species of beaked whale have been made in the eastern tropical Pacific. The unidentified whale has two color morphs: a conspicuously marked black and white form (judged to be larger), and a uniformly gray-brown form. Maximum length estimates have been 5–5.5 m. Other features include a relatively flat head, with a small, distinct melon; a moderately long beak; and a low, wide-based, triangular dorsal fin. On most animals the trailing edge of the dorsal fin is only slightly falcate and often appears straight. On the black and white morph, a broad white or cream-colored swathe originates immediately posterior to the dorsal surface of the head and runs posterio-ventrally on either side of the animal. The prevalence of scarring on the black and white animals suggests sexual dimorphism and that these larger, more conspicuously marked animals are adult males, while the smaller, browner, unscarred animals are females and young. Possibilities for identification include: 1) a well-marked race of a known Mesoplodon sp., 2) Mesoplodon (Indopacetus) pacificus or 3) an undescribed species.     

Does a lack of observed beaked whale strandings in military exercise areas mean no impacts have occurred? A comparison of stranding and detection probabilities in the Canary and main Hawaiian Islands

Anthropogenic activities must be monitored to determine effects on marine mammal species, but the difficulty lies in how to measure impact. Mass strandings of beaked whales have occurred in association with naval exercises, with two species most affected, Cuvier's (Ziphius cavirostris) and Blainville's (Mesoplodon densirostris) beaked whales. Six such events have occurred in the Canary Islands but there have been no reported mass strandings in Hawai‘i. We assess the hypothesis that factors that influence the likelihood of strandings occurring and/or being detected differ between the Canary and main Hawaiian Islands, such that beaked whale stranding/detection probabilities will be lower in Hawai‘i. On an archipelago-wide basis, nearshore bathymetric comparisons indicate that the Canaries have a greater proportion and a total greater amount of appropriate beaked whale habitat closer to shore, with a steeper slope. Hawaiian shorelines are more dominated by steep cliffs, human population density is much lower, and human population per kilometer of shoreline is 53% lower than in the Canaries. All of these factors suggest that there is a higher probability of a carcass washing onshore and being detected in the Canary Islands. It cannot be concluded that the lack of mass strandings in Hawai‘i is evidence of no impact.