{"title":"Molecular profiling of 18S rRNA reveals seasonal variation and diversity of diatoms community in the Han River, South Korea","authors":"B. Muhammad, Yeonjung Lee, Jang‐Seu Ki","doi":"10.12651/JSR.2021.10.1.046","DOIUrl":null,"url":null,"abstract":"Diatoms are groups of eukaryotic unicellular micro algae and are some of the most common organic matter in an aquatic ecosystem. They play an important role as the primary producers in freshwater and marine environ ments, and they contribute significantly to the photosyn thesis activity on Earth (Lee et al., 2019). In addition, dia toms are used widely across the world for environmental monitoring because different species of diatom typically have specific habitat preferences, and they react quickly to environmental changes (Dixit et al., 1992; Round et al., 2007). For example, species like Cyclotella meneghiniana and Thalassiosira pseudonana (Baek et al., 2011; Adenan et al., 2013) have distinct ranges of pH and salinity where they will grow (Spaulding et al., 2019). In addition, they have ranges and tolerance for other environmental factors, such as nutrient concentration, suspended sediment, flow regime, elevation, and for different types of human distur bances (Spaulding et al., 2019). Hence, they are consid ered susceptible indicators of water quality and environ mental change. For these reasons, diatoms have received considerable attention from past and ongoing research (Dixit et al., 1992; Adenan et al., 2013; Hilaluddin et al., 2020). In general, diatoms have been discriminated morphologi cally by using a light microscope (LM) and scanning elec tron microscope (SEM). However, some diatoms may have few discernible structural differences when viewed with a microscope. In addition, different lineages have often adapted in similar ways to analogous habitats. As a result, there are many examples of diatoms species that look very similar at the microscopic level, but are not closely related (Graham et al., 2009). Since the early 1980s, molecular techniques by using carbohydrates, toxins, proteins, and nucleic acids as markers have been developed to detect and discriminate phytoplankton (Ebenezer et al., 2012; Sun et al., 2012). Among DNA based methods such as terminal restriction fragment length polymorphism, micro array, realtime PCR, the highthroughput sequencing (HTS) of smallsubunit rRNA genes from environmental DNA techniques has already been widely applied for the assessment of microbial diversity and microplanktonic community structure (Eiler et al., 2012; Ghiglione and Murray, 2012). These methods allowed high resolution and rapid analysis of microbial and phytoplankton com Journal of Species Research 10(1):4656, 2021","PeriodicalId":426231,"journal":{"name":"Journal of species research","volume":"53 1","pages":"0"},"PeriodicalIF":0.0000,"publicationDate":"2021-02-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"2","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Journal of species research","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.12651/JSR.2021.10.1.046","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 2
Abstract
Diatoms are groups of eukaryotic unicellular micro algae and are some of the most common organic matter in an aquatic ecosystem. They play an important role as the primary producers in freshwater and marine environ ments, and they contribute significantly to the photosyn thesis activity on Earth (Lee et al., 2019). In addition, dia toms are used widely across the world for environmental monitoring because different species of diatom typically have specific habitat preferences, and they react quickly to environmental changes (Dixit et al., 1992; Round et al., 2007). For example, species like Cyclotella meneghiniana and Thalassiosira pseudonana (Baek et al., 2011; Adenan et al., 2013) have distinct ranges of pH and salinity where they will grow (Spaulding et al., 2019). In addition, they have ranges and tolerance for other environmental factors, such as nutrient concentration, suspended sediment, flow regime, elevation, and for different types of human distur bances (Spaulding et al., 2019). Hence, they are consid ered susceptible indicators of water quality and environ mental change. For these reasons, diatoms have received considerable attention from past and ongoing research (Dixit et al., 1992; Adenan et al., 2013; Hilaluddin et al., 2020). In general, diatoms have been discriminated morphologi cally by using a light microscope (LM) and scanning elec tron microscope (SEM). However, some diatoms may have few discernible structural differences when viewed with a microscope. In addition, different lineages have often adapted in similar ways to analogous habitats. As a result, there are many examples of diatoms species that look very similar at the microscopic level, but are not closely related (Graham et al., 2009). Since the early 1980s, molecular techniques by using carbohydrates, toxins, proteins, and nucleic acids as markers have been developed to detect and discriminate phytoplankton (Ebenezer et al., 2012; Sun et al., 2012). Among DNA based methods such as terminal restriction fragment length polymorphism, micro array, realtime PCR, the highthroughput sequencing (HTS) of smallsubunit rRNA genes from environmental DNA techniques has already been widely applied for the assessment of microbial diversity and microplanktonic community structure (Eiler et al., 2012; Ghiglione and Murray, 2012). These methods allowed high resolution and rapid analysis of microbial and phytoplankton com Journal of Species Research 10(1):4656, 2021
硅藻是一类真核单细胞微藻,是水生生态系统中最常见的有机物。它们作为淡水和海洋环境中的主要生产者发挥着重要作用,它们对地球上的光合作用活动做出了重大贡献(Lee et al., 2019)。此外,硅藻在世界范围内被广泛用于环境监测,因为不同种类的硅藻通常具有特定的栖息地偏好,并且它们对环境变化反应迅速(Dixit等人,1992;Round et al., 2007)。例如,meneghiniana Cyclotella和pseudonana thalassisira等物种(Baek et al., 2011;Adenan et al., 2013)在不同的pH和盐度范围内生长(Spaulding et al., 2019)。此外,它们对其他环境因素(如养分浓度、悬浮沉积物、水流状况、海拔)和不同类型的人为干扰也有一定的范围和耐受性(Spaulding et al., 2019)。因此,它们被认为是水质和环境变化的敏感指标。由于这些原因,硅藻在过去和正在进行的研究中受到了相当大的关注(Dixit等,1992;Adenan et al., 2013;Hilaluddin et al., 2020)。一般来说,硅藻是通过光镜和扫描电镜进行形态学区分的。然而,当用显微镜观察时,一些硅藻可能几乎没有可辨别的结构差异。此外,不同的谱系往往以相似的方式适应类似的栖息地。因此,有许多硅藻物种在微观层面上看起来非常相似,但并不密切相关(Graham et al., 2009)。自20世纪80年代初以来,利用碳水化合物、毒素、蛋白质和核酸作为标记的分子技术已经发展到检测和区分浮游植物(Ebenezer et al., 2012;Sun等人,2012)。在末端限制性片段长度多态性、微阵列、实时PCR等基于DNA的方法中,基于环境DNA技术的小亚基rRNA基因高通量测序(HTS)已经广泛应用于微生物多样性和微浮游生物群落结构的评估(Eiler et al., 2012;Ghiglione and Murray, 2012)。这些方法实现了微生物和浮游植物的高分辨率和快速分析[j] .物种研究,10(1):46-56,2021