丹中槟榔市Sei Carang水域后铝土矿矿区红树林生态系统的更新速度

Moza Fani Maylani, F. Lestari, Susiana Susiana
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摘要

丹戎槟榔市塞加朗河口水域红树林生态系统是一个具有土地转换活动的红树林生态系统,为环境留下了开阔的土地。本研究的目的是从幼苗、树苗和乔木的角度来测定后铝土矿矿区红树林生态系统的密度和更新速度。这项研究于2022年7月至10月进行。本研究在丹中槟榔市Sei Carang河口水域存在一个红树林生态系统,其中有铝土矿后开口,基于有目的采样方法确定的四个站点进行。每个站点采集3块数据,苗木类样块大小为1x1m,采样样块大小为5x5m,树木样块大小为10x10m。数据分析采用物种密度公式,通过比较幼苗、树苗和乔木密度计算得到的数据,再用多样性指数公式计算更新率。研究结果发现了8种红树,即尖根红树(Rhizophora apiculata)、粗根红树(Rhizophora mucronata)、裸木红树(Bruguiera gymnorhiza)、白索纳(Soneratia alba)、海参红树(Avicennia lanata)、果木红树(Nypa fruticans)和柳杉(Lumnitzera litorea)。1站苗木密度为4万株/Ha,幼树密度为2667株/Ha,树木密度为1533株/Ha, 2站苗木密度为3万株/Ha,幼树密度为1467株/Ha,树木密度为500株/Ha, 3站苗木密度为36667株/Ha,幼树密度为5200株/Ha,树木密度为1600株/Ha, 4站苗木密度为53333株/Ha,幼树密度为3200株/Ha,树木密度为2133株/Ha。各观测站的红树林更新水平均较好。
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The rate of regeneration of mangrove ecosystems on post-bauxite mining areas in the waters of Sei Carang, Tanjungpinang City
The mangrove ecosystem in the Sei Carang estuary waters, Tanjungpinang city is a mangrove ecosystem that has land conversion activities and leaves the environment with open land. The purpose of this study was to determine the density and regeneration rate of mangrove ecosystems on post-bauxite mining areas as seen from seedling, sapling, and trees. This research was conducted in July-October 2022. This study was conducted at four stations determined by the purposive sampling method, based on the existence of a mangrove ecosystem in which there are post-bauxite mine openings in the Sei Carang estuary waters, Tanjungpinang City. For each station, 3 plots of data were collected, with a plot size of 1x1m for the seedling category, a plot of 5x5m for sampling and a plot of 10x10m for trees. Data analysis used the formula for species density, for the regeneration rate by comparing the data from the calculation of the density of seedling, sapling and trees and then the formula for the diversity index. The results of the study found eight types of mangroves, namely Rhizophora apiculata, Rhizophora mucronata, Bruguiera gymnorhiza, Soneratia alba, Avicennia lanata, Nypa fruticans, and Lumnitzera litorea. Density values at station 1 for seedling 40,000 individual/Ha, sapling 2,667 individual/Ha, and trees 1,533 individual/Ha, at station 2 for seedling 30,000 individual/Ha, sapling 1,467 individual/Ha, and trees 500 individual/Ha, at station 3 for seedling 36,667 individual/Ha, sapling 5,200 individual/Ha, and trees 1,600 individual/Ha then at station 4 for seedling 53,333 individual/Ha, sapling 3,200 individual/Ha, and trees 2,133 individual/Ha. The level of mangrove regeneration at all observation stations is quite good.
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