珠江河口凤鲚的栖息地适宜性评价

谢雨芳; 吴鹏; 刘永; 肖雅元; 唐广隆; 王腾; 林琳; 李纯厚

doi:10.12131/20220029

珠江河口凤鲚的栖息地适宜性评价

doi: 10.12131/20220029

谢雨芳^{1, 2,},
吴鹏¹,
刘永^{1, 3},
肖雅元¹,
唐广隆^{1, 2, 3},
王腾^{1, 3},
林琳¹,
李纯厚^{1, 3, ,}

1.
中国水产科学研究院南海水产研究所/农业农村部南海渔业资源开发利用重点实验室/广东珠江口生态系统野外科学观测研究站/广东省渔业生态环境重点实验室，广东广州 510300
2.
上海海洋大学水产与生命学院，上海 201306
3.
南方海洋科学与工程广东省实验室 (广州)，广东广州 5114582

基金项目: 国家重点研发计划项目 (2019YFD0901204, 2019YFD0901201)；广东省基础与应用基础研究基金项目 (2019B1515120065)；广东省科技计划项目 (2019B121201001)；南方海洋科学与工程广东省实验室 (广州) 人才团队引进重大专项 (GML2019ZD0605)；广州市科技计划项目 (202102080509)；广东省基础与应用基础研究重大项目(2019B030302004-05)；中国水产科学研究院南海水产研究所中央级公益性科研院所基本科研业务费专项资金资助 (2021SD04)；中国水产科学研究院中央级公益性科研院所基本科研业务费专项资金资助 (2020TD16)

详细信息

作者简介:
谢雨芳 (1995—)，女，硕士研究生，研究方向为海洋渔业环境保护。E-mail: xie_yufang2022@163.com

通讯作者:
李纯厚 (1963—)，男，研究员，研究方向为海洋渔业环境保护。E-mail: scslch@vip.163.com

中图分类号: S 931.3
计量
- 文章访问数: 226
- HTML全文浏览量: 59
- PDF下载量: 28
- 被引次数: 0
出版历程
- 收稿日期: 2022-01-25
- 修回日期: 2022-05-02
- 录用日期: 2022-06-20
- 网络出版日期: 2022-07-02
- 刊出日期: 2023-02-03

Study on habitat suitability of Coilia mystus in Pearl River Estuary, China

XIE Yufang^{1, 2
,},
WU Peng¹,
LIU Yong^{1, 3},
XIAO Yayuan¹,
TANG Guanglong^{1, 2, 3},
WANG Teng^{1, 3},
LIN Lin¹,
LI Chunhou^{1, 3
, ,}

1.
South China Sea Fisheries Research Institute, Chinese Academy of Fishery Sciences/Key Laboratory of South China Sea Fishery Resources Exploitation & Utilization, Ministry of Agriculture and Rural Affairs/Observation and Research Field Station of Pearl River Estuary Ecosystem, Guangdong Province/Guangdong Provincial Key Laboratory of Fishery Ecology and Environment, Guangzhou 510300, China
2.
College of Fisheries and Life, Shanghai Ocean University, Shanghai, 201306, China
3.
Southern Marine Science and Engineering Guangdong Laboratory (Guangzhou), Guangzhou 511458, China

摘要

摘要: 探究珠江河口洄游性鱼类凤鲚 (Coilia mystus) 的生境适宜度，可为其渔业资源保护和利用提供科学依据。根据2019年冬季和2020年夏季在珠江河口进行的底拖网调查数据，选取水深、底层盐度、底层水温、底层溶解氧等作为指示因子，利用层次分析法 (Analytic hierarchy process, AHP) 计算各指示因子的权重，采用算数平均法 (Arithmetic Mean Model, AMM) 和几何平均法 (Geometric Mean Model, GMM) 计算栖息地适宜度指数 (Habitat Suitability Index, HSI)，验证发现基于GMM且赋予权重的HSI模型精确度较高，能较好地反映珠江河口凤鲚的栖息地分布。最优模型结果显示，珠江河口冬季和夏季凤鲚适宜的底层盐度分别为21.03‰~30.55‰和20.25‰~25.82‰，溶解氧质量浓度分别为6.79~7.28和3.85~4.01 mg·L⁻¹，水深分别为11.69~20.10和7.80~9.23 m，底层水温分别为19.84~19.95和28.36~29.44 ℃。珠江河口凤鲚HSI大于0.5的站点仅占总调查站点的17.39%，表明其栖息地适宜性较低，目前珠江河口适宜凤鲚的栖息地主要位于内伶仃海域的中华白海豚自然保护区。
- 凤鲚 /
- 栖息地适宜性指数 /
- 环境因子 /
- 珠江河口
Abstract: Exploring the habitat suitability of Coilia mystus, a migratory fish in the Pearl River estuary, can provide a scientific basis for the protection and utilization of fishery resources of C. mystus. Based on the date collected by the bottom-trawl in the Pearl River Estuary during winter in 2019 and summer in 2020, we constructed the habitat suitability index (HSI) model of C. mystus, taking the water depth, bottom salinity, bottom temperature, as well as bottom dissolved oxygen as indicator environment indicators. The analytic hierarchy process (AHP) was used to calculate the weight of the indicators. The arithmetic mean (AMM) and the geometric mean (GMM) were used to build a model. Then a suitability curve was developed and the HSI of C. mystus was calculated. Results show that the optimal bottom salinities for C. mystus in the Pearl River Estuary in winter and summer were 21.03‰−30.55‰ and 20.25‰−25.82‰, respectively; the mass concentrations of suitable dissolved oxygen were 6.79–7.28 and 3.85–4.01 mg·L⁻¹, respectively; the suitable water depths were 11.69–20.10 and 7.80–9.23 m, respectively; the suitable bottom temperatures were 19.84–19.95 and 28.36–29.44 ℃, respectively. The sites with HSI value greater than 0.5 accounted for 17.39% of the total survey sites. The study shows that the suitability of C. mystus was low, and its suitable habitats in the Pearl River Estuary are mainly located in the Sousa chinensis Nature Reserve in the Neilingding sea area.
- Coilia mystus /
- Habitat suitability index /
- Environment factors /
- Pearl River Estuary

HTML全文

图 1 珠江河口凤鲚调查站点图

Figure 1. Sampling sites of C. mystus in Pearl River Estuary

下载: 全尺寸图片幻灯片

图 2 珠江河口凤鲚冬、夏季底层盐度、底层溶解氧、深度、底层水温的适宜性指数曲线

Figure 2. Suitability index curves of bottom salinity, bottom DO, depth and bottom water temperature of C. mystus in Pearl River Estuary during winter and summer

下载: 全尺寸图片幻灯片

图 3 珠江河口凤鲚冬、夏季实际资源密度与栖息地适宜性指数的相关性

Figure 3. Pearson correlation between actual resource density of C. mystus and HSI in Pearl River Estuary during winter and summer

下载: 全尺寸图片幻灯片

图 4 珠江河口凤鲚冬、夏季HSI分布平面图

Figure 4. Distribution of HSI of C. mystus in Pearl River Estuary during winter and summer

下载: 全尺寸图片幻灯片

表 1 指示因子的判断矩阵

Table 1. Judgment matrix of indicator factors

指示因子 Indicator factor	底层盐度 Bottom salinity	底层溶解氧 Bottom DO	水深 Water depth	底层水温 Bottom temperature
底层盐度 Bottom salinity	1	3	5	5
底层溶解氧 Bottom DO	0.33	1	3	4
水深 Water depth	0.20	0.33	1	2
底层水温 Bottom temperature	0.20	0.25	0.5	1

下载: 导出CSV

参考文献(39)

[1]	林坤, 麦广铭, 王学锋. 2015—2018年珠江口近岸海域鱼类群落结构及其稳定性[J]. 水产学报, 2020, 44(11): 1841-1850.
[2]	庄平, 李桂峰. 珠江口鱼类资源多样性与资源保护 [M]. 北京: 中国农业出版社, 2018: 19-47.
[3]	费鸿年, 何宝全, 陈国铭. 南海北部大陆架底栖鱼群聚的多样度以及优势种区域和季节变化[J]. 水产学报, 1981(1): 1-20.
[4]	徐鹏, 谢木娇, 周卫国, 等. 近30年珠江口海域游泳动物经济物种群落结构变化特征[J]. 应用海洋学学报, 2021, 40(2): 239-250. doi: 10.3969/J.ISSN.2095-4972.2021.02.007
[5]	袁梦, 汤勇, 徐姗楠, 等. 珠江口南沙海域秋季渔业资源群落结构特征[J]. 南方水产科学, 2017, 13(2): 18-25. doi: 10.3969/j.issn.2095-0780.2017.02.003
[6]	袁传宓, 秦安舲. 我国近海鲚鱼生态习性及其产量变动状况[J]. 海洋科学, 1984(5): 35-37.
[7]	JIANG T, LIU H B, HUANG H H, et al. Migration patterns and habitat use of the tapertail anchovy Coilia mystus in the Oujiang River Estuary and the Zhujiang River Estuary, China[J]. Acta Oceanol Sin, 2019, 38(8): 35-40. doi: 10.1007/s13131-019-1436-0
[8]	李开枝, 尹健强, 黄良民, 等. 珠江口伶仃洋海域底层游泳动物的季节变化[J]. 生态科学, 2012, 31(1): 2-8. doi: 10.3969/j.issn.1008-8873.2012.01.001
[9]	刘守海, 徐兆礼, 田丰歌. 长江口及附近水域凤鲚摄食习性的分析[J]. 上海海洋大学学报, 2012, 21(4): 589-597.
[10]	郭爱, 陈峰, 金海卫, 等. 东、黄海凤鲚的食物组成及其食性的季节变化[J]. 海洋渔业, 2014, 36(5): 402-408. doi: 10.3969/j.issn.1004-2490.2014.05.003
[11]	CUI Y, WU Y, XU Z L, et al. Potential dietary influence on the stable isotopes and fatty acid composition of migratory anchovy (Coilia mystus) around the Changjiang Estuary[J]. J Mar Biol Assoc UK, 2014, 95(1): 1-13.
[12]	胡丽娟, 宋超, 耿智, 等. 长江口凤鲚仔稚鱼主要繁殖季节的时空分布特征[J]. 中国水产科学, 2021, 28(9): 1152-1161.
[13]	洪波, 周轩, 王淼. 杭州湾北部海域凤鲚个体繁殖力初步研究[J]. 水产科技情报, 2021, 48(6): 335-341. doi: 10.16446/j.fsti.20201200123
[14]	倪健夫, 郭弘艺, 唐文乔, 等. 长江口汛期凤鲚捕捞量年际变化研究[J]. 海洋渔业, 2020, 42(2): 192-204.
[15]	WANG L L, LIN L, LI Y, et al. Sustainable exploitation of dominant fishes in the largest estuary in southeastern China[J]. Water, 2020, 12: 3390. doi: 10.3390/w12123390
[16]	WANG C, KYNARD B, WEI Q, et al. Spatial distribution and habitat suitability indices for non-spawning and spawning adult Chinese sturgeons below Gezhouba Dam, Yangtze River: effects of river alterations[J]. J Appl Ichthyol, 2013, 29(1): 1-10. doi: 10.1111/jai.12157
[17]	周为峰, 李英雪, 程田飞, 等. 栖息地适宜性指数模型在鱼类生境评价中的应用进展[J]. 渔业信息与战略, 2020, 35(1): 48-54. doi: 10.13233/j.cnki.fishis.2020.01.007
[18]	GONG C X, CHEN X J, GAO F, et al. Effect of spatial and temporal scales on habitat suitability modeling: a case study of Ommastrephes bartramii in the northwest Pacific Ocean[J]. J Ocean Univ China, 2014, 13(6): 1-11.
[19]	ZHANG Z P, ZHOU J, SONG J J, et al. Habitat suitability index model of the sea cucumber Apostichopus japonicus (Selenka): a case study of Shandong Peninsula, China[J]. Mar Pollut Bull, 2017, 122(1/2): 1-12.
[20]	范秀梅, 杨胜龙, 张胜茂, 等. 基于栖息地指数的阿拉伯海鲐鱼渔情预报模型构建[J]. 南方水产科学, 2020, 16(4): 8-17. doi: 10.12131/20190255
[21]	邹易阳, 薛莹, 麻秋云, 等. 应用栖息地适宜性指数研究海州湾小黄鱼的空间分布特征[J]. 中国海洋大学学报, 2016, 46(8): 54-63.
[22]	BROWN S K, BUJA K R, JURY S H, et al. Habitat Suitability Index models for eight fish and invertebrate species in Casco and Sheepscot Bays, Maine[J]. N Am J Fish Manag, 2011, 20(2): 1-28.
[23]	毕雪娟. 长江口凤鲚繁殖生物学及HSI评估 [D]. 上海: 上海海洋大学, 2015: 43-63.
[24]	施炜纲, 王博. 长江河口区凤鲚的资源现状[J]. 水生生物学报, 2002, 26(6): 648-653. doi: 10.3321/j.issn:1000-3207.2002.06.012
[25]	莫伟均, 何用, 王建平, 等. 珠江河口鱼类分布现状及栖息水域特征[J]. 应用与环境生物学报, 2022, 28(5): 1-10. doi: 10.19675/j.cnki.1006-687x.2021.05048
[26]	WU J H, DAI L B, DAI X J, et al. Comparison of generalized additive model and boosted regression tree in predicting fish community diversity in the Yangtze River Estuary, China[J]. J Appl Ecol, 2019, 30(2): 1-9.
[27]	邓雪, 李家铭, 曾浩健. 等. 层次分析法权重计算方法分析及其应用研究[J]. 数学的实践与认识, 2012, 42(7): 93-100. doi: 10.3969/j.issn.1000-0984.2012.07.012
[28]	王云峰, 朱鑫华. 盐度对鱼类生态生理学特征的影响[J]. 海洋科学集刊, 2002(1): 151-158.
[29]	孙艳秋, 刘鉴毅, 庄平, 等. 温度、盐度和pH对多纹钱蝶鱼胚胎发育的影响[J]. 南方水产科学, 2021, 17(6): 122-129. doi: 10.12131/20210109
[30]	晁眉, 黄良敏, 李军, 等. 福建九龙江口凤鲚的生物学特征[J]. 集美大学学报(自然科学版), 2016, 21(1): 16-20.
[31]	张云雷, 薛莹, 于华明, 等. 海州湾春季皮氏叫姑鱼栖息地适宜性研究[J]. 海洋学报, 2018, 40(6): 83-91.
[32]	柳晓雪, 高春霞, 田思泉, 等. 基于栖息地适宜指数的浙江南部近海黄鲫最适栖息地分布[J]. 中国水产科学, 2020, 27(12): 1485-1495.
[33]	邓吉河. 浅谈水温与鱼类的关系[J]. 黑龙江水产, 2019(1): 25-27. doi: 10.3969/j.issn.1674-2419.2019.01.009
[34]	詹海刚. 珠江口及邻近水域鱼类群落结构研究[J]. 海洋学报, 1998, 20(3): 91-97.
[35]	黄彬彬, 郑淑娴, 蔡伟叙, 等. 珠江口枯水期和丰水期中小型桡足类种类组成、丰度分布及其与环境因子的关系[J]. 厦门大学学报(自然科学版), 2017, 56(6): 852-858.
[36]	肖尤盛, 陈海亮, 王雪辉, 等. 珠江口中华白海豚的食物变化[J]. 海洋与渔业, 2018(10): 72-73.
[37]	黄吉万, 孙典荣, 刘岩, 等. 珠江口中华白海豚自然保护区鱼类群落多样性分析[J]. 南方农业学报, 2018, 49(5): 1000-1007. doi: 10.3969/j.issn.2095-1191.2018.05.25
[38]	徐姗楠, 龚玉艳, 詹凤娉, 等. 珠江口海域南沙段浮游动物群落生态特征[J]. 海洋湖沼通报, 2017(6): 82-90.
[39]	官文江, 田思泉, 朱江峰, 等. 渔业资源评估模型的研究现状与展望[J]. 中国水产科学, 2013, 20(5): 1112-1120.