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Reproductive Ecology of Mangrove Flora: Conservation and Management

机译:红树林植物生殖生态学:保护与管理

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Mangroves are dynamic and unique inter-tidal ecosystems, common in tropical and subtropical coastal environments. They are among the world’s most productive ecosystems and are important in protecting coasts from erosion by fierce tides, in promoting the diversity of marine organisms and fisheries by contributing a quantity of food and providing favourable habitats for animals. These economic uses of mangroves indicate that they play an important role in the lives and economies in the coastal regions of different countries. Mangrove forests are under immense threat worldwide due to their multiple economic uses and alterations of freshwater inflows by various upstream activities in catchment areas. Mangrove plants with unique adaptations play a crucial role in sustaining life in mangrove forests. Their reproductive biology is central to understanding the structural and functional components of mangrove forests. The success of sexual reproduction and subsequent population expansion in mangrove plants is linked to flowering timings, pollinators and tidal currents. Viviparous and cryptoviviparous plants are true mangroves while non-viviparous ones are mangrove associates. The dispersal propagule is seedling in viviparous and non-viviparous plants while it is seed in nonviviparous plants. In this study, viviparous and crypto-viviparous species were included for study. These species are self-compatible, self-pollinating and also cross-pollinating; such a breeding system is a requirement for the success of sexual reproduction and subsequent build up and expansion of population. They are entomophilous in the study region. The viviparous plants include Ceriops tagal, C. decandra, Rhizophora apiculata, R. mucronata, Bruguiera gymnorrhiza and B. cylindrica. The non-viviparous plants include Avicennia alba, A. marina, A. officinalis, Aegiceras corniculatum and Aegialitis rotundifolia. Sexual reproduction and regeneration events are annual in these plants and are dependent on local insects, tidal currents and nutrient content in estuarine environment. In recent times, erratic and insufficient rainfall together with industrial pollutants released into rivers is causing negative effects on the growth, development and regeneration of mangrove flora. In effect, there is a gradual decrease in mangrove cover. Added to this is continuous exploitation of mangrove plants for fuel wood, creation of shelters for cattle and changes for industrial establishments and aquaculture development in estuarine regions. As a consequence, the existing mangrove cover is struggling to survive and also not in a position to support local needs and provide livelihood opportunities through fishery resources. Further, reduced mangrove cover is showing catastrophic effects on fishing communities who live along the shore line during the period of cyclonic surges and tsunami events.
机译:红树林是动态的,独特的潮间生态系统,常见于热带和亚热带沿海环境。它们是世界上生产力最高的生态系统之一,对于保护海岸免受猛烈潮汐侵蚀,通过提供大量食物和为动物提供有利的栖息地来促进海洋生物和渔业的多样性具有重要意义。红树林的这些经济用途表明它们在不同国家沿海地区的生活和经济中发挥着重要作用。由于红树林的多种经济用途和集水区上游各种活动改变的淡水流入量,它们在世界范围内受到了巨大的威胁。具有独特适应性的红树林植物在维持红树林的生命中起着至关重要的作用。他们的生殖生物学对于理解红树林的结构和功能组成至关重要。红树林植物中有性生殖的成功和随后种群的扩展与开花时间,传粉媒介和潮流有关。胎生和隐生植物是真正的红树林,而非活生植物是红树林的伴生。分散繁殖体在无胎和无胎的植物中是幼苗,而在无胎的植物中是种子。在这项研究中,包括了胎生和隐生的物种。这些物种是自相容的,自花授粉的和异花授粉的。这样的育种系统是成功进行有性生殖以及随后种群增加和扩大的必要条件。它们在研究区域是嗜虫的。胎生植物包括塔里木(Ceriops tagal),癸酸假丝酵母(C. decandra),尖头根瘤菌(Rhizophora apiculata),粘液芽胞杆菌(R. mucronata),裸枝布鲁吉拉氏菌(Bruguieragympnorrhiza)和圆柱状芽孢杆菌。非活体植物包括白僵菌,滨海曲霉,厚皮草,角顶伊蚊和轮叶伊蚊。这些植物每年都发生有性生殖和再生事件,并取决于河口环境中的当地昆虫,潮流和养分含量。近年来,降雨的不稳定和不足以及释放到河流中的工业污染物正在对红树林植物的生长,发育和再生造成负面影响。实际上,红树林覆盖率逐渐下降。此外,对红树林植物进行薪柴的持续开发,为牛群建立庇护所以及为河口地区的工业机构和水产养殖业发展进行变革。结果,现有的红树林正在努力生存,也无法通过渔业资源支持当地需求并提供生计机会。此外,减少的红树林覆盖率对旋风激增和海啸事件期间沿海岸线居住的捕鱼社区造成灾难性影响。

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