Current status and restoration strategy of mangroves in Xincun Port,Lingshui,Hainan Island,China

ZHENG Fa; LIU Wei; LIU Jiahui; CHEN Zeheng; ZHAI Ruihao; WANG Ning; WEI Xiu

doi:10.15886/j.cnki.rdswxb.20230129

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Volume 15 Issue 6

Nov. 2024

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Article Navigation > Journal of Tropical Biology > 2024 > 15(6): 770-779

ZHENG Fa, LIU Wei, LIU Jiahui, CHEN Zeheng, ZHAI Ruihao, WANG Ning, WEI Xiu. Current status and restoration strategy of mangroves in Xincun Port,Lingshui,Hainan Island,China[J]. Journal of Tropical Biology, 2024, 15(6): 770-779. doi: 10.15886/j.cnki.rdswxb.20230129

Citation:

ZHENG Fa, LIU Wei, LIU Jiahui, CHEN Zeheng, ZHAI Ruihao, WANG Ning, WEI Xiu. Current status and restoration strategy of mangroves in Xincun Port,Lingshui,Hainan Island,China[J]. Journal of Tropical Biology, 2024, 15(6): 770-779. doi: 10.15886/j.cnki.rdswxb.20230129

Current status and restoration strategy of mangroves in Xincun Port,Lingshui,Hainan Island,China

doi: 10.15886/j.cnki.rdswxb.20230129

Haikou Marine Geological Survey Center, China Geological Survey, Haikou, Hainan 571127, China

Received Date: 2023-11-29
Rev Recd Date: 2024-04-24

Abstract

In recent years, the growth environment of mangroves has been seriously threatened and has become one of the most endangered ecosystems in the world. To clarify the current situation of mangroves and formulate more effective protection measures, digital orthophotos of Hainan Province were used to interpret the area and distribution areas of mangroves in Xincun Port, Lingshui, Hainan, and a survey was made of the species of mangroves in Xincun Port by using a sampling method. At the same time, the diversity of main biological indicators, and the distribution characteristics of natural and artificial populations of mangroves on the south and north bamks of Xincun Port were analyzed. The results indicate there are a total of 12 species of mangroves, including 8 species on the south shore,with the dominant species being Rhizophora apiculata; and 6 species on the north shore, with the dominant species being Laguncularia racemos. A national second-level protected plant（Lumnitzera littorea） has been transplanted and its growth condition is good. On both the north and south shores, natural forests have shown adaptability to high tide levels, but the growth status of mangroves on the south shore is better than that on the north shore. However, the trees in plantation forests on both shores are relatively short. In terms of species diversity, the biodiversity of natural forests is higher on the south shore than on the north shore. However, in terms of plantation forests, the biodiversity is slightly higher on the north shore than on the south shore. On the south shore mainly grows a natural forest, where it is more suitable to plant Sonneratia apetala or prune the trees to have loose canopy to increase species diversity,while the plantation forests on the north shore are mostly of native species. Planting multi-species at a two-layer pattern can increase species diversity more effectively. At the same time, taking into account the characteristics of biological invasion and different tide levels, a suggestion was made on planting Sonneratia apetala at high tide levels. This study clarified the species distribution and ecological characteristics of the mangroves in Xincun Port,Lingshui, which might provide valuable survey data for the mangrove protection and restoration projects in the area,facilitating optimization of the mangrove protection strategy, and hence the ecological protection and sustainable development of mangroves in Xincun Port.
- Xincun Port,
- mangrove forest,
- species distribution,
- species diversity,
- ecological restoration

References

[1]	李皓宇,彭逸生,刘嘉健,等.粤东沿海红树林物种组成与群落特征[J].生态学报, 2016, 36(1):252-260.
[2]	王丽荣,李贞,蒲杨婕,等.海南东寨港、三亚河和青梅港红树林群落健康评价[J].热带海洋学报, 2011, 30(2):81-86.
[3]
[4]	王震,陈卫军,管伟,等.珠海市淇澳岛主要红树林群落特征研究[J].中南林业科技大学学报, 2017, 37(4):86-91.
[5]	林鹏.中国红树林生态系[M].北京:科学出版社, 1997.
[6]
[7]	涂志刚,韩涛生,陈晓慧,等.海南陵水新村港与黎安港海草特别保护区大型底栖动物群落结构与多样性[J].海洋环境科学, 2016, 35(1):41-48.
[8]	史伟.海南陵水红树林湿地资源现状及保护对策[J].中南林业调查规划, 2021, 40(2):51-54.
[9]	陈彧,程成,王鑫,等.外来红树植物拉关木在陵水新村港的群落特征[J].热带林业, 2022, 50(2):25-29.
[10]	巩慧敏,刘永,肖雅元,等.近海海水和表层沉积物重金属污染与生态风险评价:以海南新村港为例[J].农业现代化研究, 2018, 39(4):700-708.
[11]	陈彧,杨克仁,方发之,等.海南陵水新村港退塘还林区域植被调查报告[J].林业科技通讯, 2019(12):27-30.
[12]	周立柱,杨顶田,尹小青.海南新村港和黎安港非点源污染负荷估算[J].生态科学, 2018, 37(3):11-20.
[13]	杨阳,高抒,周亮,等.海南新村港潟湖表层沉积物粒度特征及其沉积环境[J].海洋学报, 2016, 38(1):94-105.
[14]	谢春平,方彦,方炎明.乌冈栎群落垂直结构与重要值分析[J].安徽农业大学学报, 2011, 38(2):176-184.
[15]	杨星晨,雷少刚,徐军,等.生物多样性指数遥感制图方法研究[J].干旱区资源与环境, 2022, 36(6):105-113.
[16]
[17]	吴协保,曾晖,谢邦雄,等.海南陵水新村潟湖滩涂红树林生态修复关键技术研究[J].湿地科学与管理,2020, 16(1):60-63.
[18]	ASAEDA T, BARNUEVO A, SANJAYA K, et al. Mangrove plantation over a limestone reef-Good for the ecology?[J]. Estuarine, Coastal and Shelf Science, 2016,173:57-64.
[19]	BARNUEVO A, ASAEDA T, SANJAYA K, et al. Drawbacks of mangrove rehabilitation schemes:lessons learned from the large-scale mangrove plantations[J]. Estuarine,Coastal and Shelf Science, 2017, 198:432-437.
[20]	IIDA S, NAKASHIZUKA T. Forest fragmentation and its effect on species diversity in sub-urban coppice forests in Japan[J]. Forest Ecology and Management, 1995, 73(1/2/3):197-210.
[21]	HIGGINS S I, RICHARDSON D M, COWLING R M.Modeling invasive plant spread:the role of plantenvironment interactions and model structure[J]. Ecology, 1996, 77(7):2043-2054.
[22]	AN S Q, GU B H, ZHOU C F, et al. Spartina invasion in China:implications for invasive species management and future research[J]. Weed Research, 2007, 47(3):183-191.
[23]	唐国玲,沈禄恒,翁伟花,等.无瓣海桑对互花米草的生态控制效果[J].华南农业大学学报, 2007, 28(1):10-13.
[24]	李云,郑德璋,陈焕雄,等.红树植物无瓣海桑引种的初步研究[J].林业科学研究, 1998, 11(1):42-47.
[25]	张乔民,于红兵,陈欣树,等.红树林生长带与潮汐水位关系的研究[J].生态学报, 1997, 17(3):258-265.
[26]	CHEN L Z, WANG W Q, LIN P, et al. Influence of water logging time on the growth of Kandelia candel seedlings[J]. Acta Oceanologica Sinica, 2004, 23(1):149-157.

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通讯作者: 陈斌, bchen63@163.com

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沈阳化工大学材料科学与工程学院沈阳 110142

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Current status and restoration strategy of mangroves in Xincun Port,Lingshui,Hainan Island,China

Haikou Marine Geological Survey Center, China Geological Survey, Haikou, Hainan 571127, China

Received Date: 2023-11-29

Rev Recd Date: 2024-04-24

Key words:

Abstract: In recent years, the growth environment of mangroves has been seriously threatened and has become one of the most endangered ecosystems in the world. To clarify the current situation of mangroves and formulate more effective protection measures, digital orthophotos of Hainan Province were used to interpret the area and distribution areas of mangroves in Xincun Port, Lingshui, Hainan, and a survey was made of the species of mangroves in Xincun Port by using a sampling method. At the same time, the diversity of main biological indicators, and the distribution characteristics of natural and artificial populations of mangroves on the south and north bamks of Xincun Port were analyzed. The results indicate there are a total of 12 species of mangroves, including 8 species on the south shore,with the dominant species being Rhizophora apiculata; and 6 species on the north shore, with the dominant species being Laguncularia racemos. A national second-level protected plant（Lumnitzera littorea） has been transplanted and its growth condition is good. On both the north and south shores, natural forests have shown adaptability to high tide levels, but the growth status of mangroves on the south shore is better than that on the north shore. However, the trees in plantation forests on both shores are relatively short. In terms of species diversity, the biodiversity of natural forests is higher on the south shore than on the north shore. However, in terms of plantation forests, the biodiversity is slightly higher on the north shore than on the south shore. On the south shore mainly grows a natural forest, where it is more suitable to plant Sonneratia apetala or prune the trees to have loose canopy to increase species diversity,while the plantation forests on the north shore are mostly of native species. Planting multi-species at a two-layer pattern can increase species diversity more effectively. At the same time, taking into account the characteristics of biological invasion and different tide levels, a suggestion was made on planting Sonneratia apetala at high tide levels. This study clarified the species distribution and ecological characteristics of the mangroves in Xincun Port,Lingshui, which might provide valuable survey data for the mangrove protection and restoration projects in the area,facilitating optimization of the mangrove protection strategy, and hence the ecological protection and sustainable development of mangroves in Xincun Port.

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Reference (26)

[1]	李皓宇,彭逸生,刘嘉健,等.粤东沿海红树林物种组成与群落特征[J].生态学报, 2016, 36(1):252-260.
[2]	王丽荣,李贞,蒲杨婕,等.海南东寨港、三亚河和青梅港红树林群落健康评价[J].热带海洋学报, 2011, 30(2):81-86.
[3]
[4]	王震,陈卫军,管伟,等.珠海市淇澳岛主要红树林群落特征研究[J].中南林业科技大学学报, 2017, 37(4):86-91.
[5]	林鹏.中国红树林生态系[M].北京:科学出版社, 1997.
[6]
[7]	涂志刚,韩涛生,陈晓慧,等.海南陵水新村港与黎安港海草特别保护区大型底栖动物群落结构与多样性[J].海洋环境科学, 2016, 35(1):41-48.
[8]	史伟.海南陵水红树林湿地资源现状及保护对策[J].中南林业调查规划, 2021, 40(2):51-54.
[9]	陈彧,程成,王鑫,等.外来红树植物拉关木在陵水新村港的群落特征[J].热带林业, 2022, 50(2):25-29.
[10]	巩慧敏,刘永,肖雅元,等.近海海水和表层沉积物重金属污染与生态风险评价:以海南新村港为例[J].农业现代化研究, 2018, 39(4):700-708.
[11]	陈彧,杨克仁,方发之,等.海南陵水新村港退塘还林区域植被调查报告[J].林业科技通讯, 2019(12):27-30.
[12]	周立柱,杨顶田,尹小青.海南新村港和黎安港非点源污染负荷估算[J].生态科学, 2018, 37(3):11-20.
[13]	杨阳,高抒,周亮,等.海南新村港潟湖表层沉积物粒度特征及其沉积环境[J].海洋学报, 2016, 38(1):94-105.
[14]	谢春平,方彦,方炎明.乌冈栎群落垂直结构与重要值分析[J].安徽农业大学学报, 2011, 38(2):176-184.
[15]	杨星晨,雷少刚,徐军,等.生物多样性指数遥感制图方法研究[J].干旱区资源与环境, 2022, 36(6):105-113.
[16]
[17]	吴协保,曾晖,谢邦雄,等.海南陵水新村潟湖滩涂红树林生态修复关键技术研究[J].湿地科学与管理,2020, 16(1):60-63.
[18]	ASAEDA T, BARNUEVO A, SANJAYA K, et al. Mangrove plantation over a limestone reef-Good for the ecology?[J]. Estuarine, Coastal and Shelf Science, 2016,173:57-64.
[19]	BARNUEVO A, ASAEDA T, SANJAYA K, et al. Drawbacks of mangrove rehabilitation schemes:lessons learned from the large-scale mangrove plantations[J]. Estuarine,Coastal and Shelf Science, 2017, 198:432-437.
[20]	IIDA S, NAKASHIZUKA T. Forest fragmentation and its effect on species diversity in sub-urban coppice forests in Japan[J]. Forest Ecology and Management, 1995, 73(1/2/3):197-210.
[21]	HIGGINS S I, RICHARDSON D M, COWLING R M.Modeling invasive plant spread:the role of plantenvironment interactions and model structure[J]. Ecology, 1996, 77(7):2043-2054.
[22]	AN S Q, GU B H, ZHOU C F, et al. Spartina invasion in China:implications for invasive species management and future research[J]. Weed Research, 2007, 47(3):183-191.
[23]	唐国玲,沈禄恒,翁伟花,等.无瓣海桑对互花米草的生态控制效果[J].华南农业大学学报, 2007, 28(1):10-13.
[24]	李云,郑德璋,陈焕雄,等.红树植物无瓣海桑引种的初步研究[J].林业科学研究, 1998, 11(1):42-47.
[25]	张乔民,于红兵,陈欣树,等.红树林生长带与潮汐水位关系的研究[J].生态学报, 1997, 17(3):258-265.
[26]	CHEN L Z, WANG W Q, LIN P, et al. Influence of water logging time on the growth of Kandelia candel seedlings[J]. Acta Oceanologica Sinica, 2004, 23(1):149-157.

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Current status and restoration strategy of mangroves in Xincun Port,Lingshui,Hainan Island,China

doi: 10.15886/j.cnki.rdswxb.20230129

Abstract

References

Proportional views

通讯作者: 陈斌, bchen63@163.com

Proportional views

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