2020年冬季大亚湾西南海域主要渔业生物碳氮稳定同位素研究

doi:10.11978/2021108

热带海洋学报 ›› 2022, Vol. 41 ›› Issue (3): 147-155.doi: 10.11978/2021108CSTR: 32234.14.2021108

2020年冬季大亚湾西南海域主要渔业生物碳氮稳定同位素研究

张婉茹^1,²(), 刘庆霞^2,³, 黄洪辉^1,^2,³(), 覃晓青², 李佳俊², 陈建华¹()

1.江苏海洋大学海洋科学与水产学院, 江苏连云港 222005
2.中国水产科学研究院南海水产研究所, 广东省渔业生态环境重点实验室, 广东广州 510300
3.南方海洋科学与工程广东省实验室(广州), 广东广州 511485

收稿日期:2021-08-25 修回日期:2021-12-02 发布日期:2021-12-13
通讯作者: 黄洪辉,陈建华
作者简介:张婉茹(1997—), 女, 山东省烟台市人, 硕士研究生, 从事海洋生态与环境科学研究。email: zhangwanru0617@163.com
基金资助:
国家重点研发计划项目(2018YFC1407501);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(GML2019ZD0402);广东省科技计划项目(2020B1212060001);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(2020TD15);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(2021SD03);农业农村部财政专项项目(NFZX2021)

Study on stable isotopes of carbon and nitrogen of main fishery organisms in the southwestern waters of Daya Bay, South China Sea in winter 2020

ZHANG Wanru^1,²(), LIU Qingxia^2,³, HUANG Honghui^1,^2,³(), QIN Xiaoqing², LI Jiajun², CHEN Jianhua¹()

1. Jiangsu Ocean University, School of Marine Science and Fisheries, Lianyungang 222005, China
2. South China Sea Fisheries Research Institute, Chinese Academy of Fishery Sciences, Guangdong Provincial Key Laboratory of Fishery Ecology and Environment, Guangzhou 510300, China
3. Southern Marine Science and Engineering Guangdong Laboratory (Guangzhou), Guangzhou 511485, China

Received:2021-08-25 Revised:2021-12-02 Published:2021-12-13
Contact: HUANG Honghui,CHEN Jianhua
Supported by:
National Key Research and Development Program of China(2018YFC1407501);Key Special Project for Introduced Talents Team of Southern Marine Science and Engineering Guangdong Laboratory (Guangzhou)(GML2019ZD0402);Guangdong Provincial Science and technology plan project(2020B1212060001);Central Public-interest Scientific Institution Basal Research Fund, CAFS(2020TD15);Central Public-interest Scientific Institution Basal Research Fund, South China Sea Fisheries Research Institute, CAFS(2021SD03);Financial Fund of the Ministry of Agriculture and Rural Affairs, P.R. China(NFZX2021)

摘要/Abstract

摘要：

为了解大亚湾西南海域食物网的营养结构特征, 本研究于2020年1月份使用底拖网采集了该海域的渔业生物, 并分析了35种主要渔业生物的碳氮稳定同位素值。根据δ¹³C和δ¹⁵N值, 计算出该海域食物网6种营养结构的生态指标和主要渔业生物的营养级, 并绘制了连续营养谱。本次调查渔业生物主要为鱼类和虾蟹类, 鱼类的δ¹³C和δ¹⁵N值范围分别为-17.63‰ ~ -14.85‰和12.92‰~15.46‰, 平均值分别为-16.47‰和13.80‰; 虾蟹类的δ¹³C和δ¹⁵N值范围分别为-17.67‰ ~ -15.51‰和11.05‰~12.62‰, 平均值分别为-16.30‰和11.85‰。根据δ¹⁵N值, 用相加模型(trophic position by the additive model, TPA)和缩比模型(trophic position by the scaled model, TPS)分别计算了主要渔业生物的营养级, 结果显示两个模型计算的结果无显著性差异(P>0.1), 呈现鱼类平均营养级>虾蟹类的趋势。本研究发现大亚湾西南海域食物网初始食物来源较为单一, 存在食物链营养层级较少和长度不足, 食物网营养级多样性较低和营养结构冗余程度高的现象。与30多年前相比, 大亚湾近年高营养级生物量减少, 食物网结构由复杂趋向简单化, 生态系统稳定性较差。本研究结果不仅为了解大亚湾食物网结构组成提供了基础资料, 也为保护大亚湾渔业资源, 维持生态系统结构的稳定性提供参考依据。

关键词: 大亚湾, 渔业生物, 碳氮稳定同位素, 营养结构

Abstract:

To understand the trophic structure of food webs in the southwestern waters of Daya Bay, 35 fishery organisms were collected by bottom trawl in January 2020, and the stable isotopes of carbon and nitrogen (δ¹³C and δ¹⁵N) of the fishery organisms were analyzed. Based on the stable isotopes of carbon and nitrogen, six quantitative ecological indicators for nutritional structure of the food web and the trophic levels of the main fishery organisms were calculated; and a continuous nutrition spectrum was made. Most of the fishery organisms captured were fish, crabs and shrimp. The δ¹³C and δ¹⁵N values were -17.63‰ to -14.85‰ and 12.92‰ to 15.46‰ for fishes, respectively, with average values being -16.47‰ and 13.80‰. They were -17.67‰ to -15.51‰ and 11.05‰ to 12.62‰ for shrimp and crabs, with average values of -16.30‰ and 11.85‰, respectively. According to the value of δ¹⁵N, the trophic levels of the main fishery organisms were calculated using the additive model (trophic position by the additive model, TPA) and the scaled model (trophic position by the scaled model, TPS). The result showed that there was no significant differences between the results calculated by the two models (P > 0.1), and the average trophic level of fish was higher than that of shrimp and crabs. This study indicates the food web in the southwestern waters of Daya Bay is characterized by a relatively simple initial food source, few trophic levels, short food chain, low trophic level diversity, and high degree of redundancy in trophic structure. The abundance of organisms with high trophic levels decreased, and the structure of the food web shifted from complex to simplistic, and the ecosystem became less stable in the past 30 years. The study adds new basic information about the food web structure in the study area. It also provides a reference for protecting the fishery resources of Daya Bay and maintaining the stability of the ecosystem structure there.

Key words: Daya Bay, fishery organism, carbon and nitrogen stable isotopes, trophic structure

中图分类号:

S931

张婉茹, 刘庆霞, 黄洪辉, 覃晓青, 李佳俊, 陈建华. 2020年冬季大亚湾西南海域主要渔业生物碳氮稳定同位素研究[J]. 热带海洋学报, 2022, 41(3): 147-155.

ZHANG Wanru, LIU Qingxia, HUANG Honghui, QIN Xiaoqing, LI Jiajun, CHEN Jianhua. Study on stable isotopes of carbon and nitrogen of main fishery organisms in the southwestern waters of Daya Bay, South China Sea in winter 2020[J]. Journal of Tropical Oceanography, 2022, 41(3): 147-155.

图/表 6

图1

表1

大亚湾西南海域主要渔业生物的碳稳定同位素比值、氮同位素比值、长度范围和营养级(n=2)"

	种类	δ¹³C/‰	δ¹⁵N/‰	长度范围/mm	营养级
	种类	δ¹³C/‰	δ¹⁵N/‰	长度范围/mm	TPA	TPS
鱼类	多鳞鱚 Sillago sihama	-15.88	13.82	120~170	3.64	3.66
	单角革鲀 Aluterus monoceros	-16.50	12.92		3.37	3.32
	黄斑篮子鱼 Siganus canaliculatus	-16.63	13.69	167~176	3.60	3.61
	小头栉孔鰕虎鱼 Ctenotrypauchen microcephalus	-16.76	13.83	65~69	3.64	3.66
	小黄鱼 Larimichthys polyactis	-16.67	12.31	116~148	3.19	3.12
	绿斑细棘鰕虎鱼 Acentrogobius chloorstigmatoides	-16.46	13.85		3.65	3.67
	孔鰕虎鱼 Trypauchen vagina	-16.53	13.22	89~100	3.46	3.43
	矛尾鰕虎鱼 Chaeturichthys stigmatias	-17.15	13.14	94~178	3.44	3.40
	虎鲉 Minous monodactylus	-15.46	14.38		3.80	3.88
	黄吻棱鳀 Thryssa vitrirostris	-17.52	13.11		3.43	3.39
	李氏? Callionymus richardsoni	-16.23	13.37	70~91	3.51	3.49
	海鳗 Muraenesox cinereus	-15.97	13.64	98~120	3.58	3.59
	短吻鲾 Leiognathus brevirostris	-17.63	13.84	44~59	3.64	3.67
	截尾白姑鱼 Pennahia anea	-17.39	14.36	145	3.80	3.88
	线纹鳗鲶 Plotosus lineatus	-16.29	14.53	21~215	3.85	3.95
	长蛇鲻 Saurida elongata	-16.31	14.91	185~233	3.96	4.12
	艾氏蛇鳗 Ophichthus lithinus	-16.20	14.17	185~260	3.74	3.80
	单斑笛鲷 Lutjanus monostigma	-14.85	15.23		4.05	4.26
虾蟹类	远海梭子蟹 Portunus pelagicus	-16.09	11.05		2.82	2.73
	红星梭子蟹 Portunus sanguinolentus	-16.11	12.09		3.13	3.04
	晶莹蟳 Charybdis lucifera	-16.64	11.72		3.02	2.93
	伪装关公蟹 Dorippe facchino	-16.83	11.93		3.08	2.99
	香港蟳 Charybdis hongkongensis	-16.17	11.94		3.08	3.00
	隆线强蟹 Eucrate crenata	-15.73	12.12		3.14	3.05
	美人蟳 Charybdis callianassa	-15.99	11.67		3.01	2.91
	阿氏强蟹 Eucrate alcocki	-15.96	12.22		3.17	3.09
	日本蟳 Charybdis japonica	-15.85	11.88		3.07	2.98
	口虾蛄 Oratosquilla oratori	-16.94	12.06		3.12	3.04
	饰尾绿虾蛄 Clorida decorata	-16.35	11.83		3.05	2.96
	断脊口虾蛄 Oratosquillina interrupta	-15.51	12.62		3.28	3.22
	近缘新对虾 Metapenaeus affinis	-16.45	12.03		3.11	3.03
	长毛对虾 Penaeus penicillatus	-16.03	11.70		3.01	2.92
	宽突赤虾 Metapenaeopsis palmensis	-16.45	11.66		3.00	2.91
	毛虾 Acetes	-17.67	11.08		2.83	2.73
头足类	杜氏枪乌贼 Loligo duvaucelii	-16.27	15.03	30~200	3.99	4.17

表1

图2

图3

表2

表3

参考文献 31

[1]	贡艺, 陈玲, 李云凯, 2017. 海洋生态系统稳定同位素基线的选取[J]. 应用生态学报, 28(7): 2399-2404.
	GONG YI, CHEN LING, LI YUNKAI, 2017. Selection of isotopic baselines in marine ecosystems[J]. Chinese Journal of Applied Ecology, 28(7): 2399-2404. (in Chinese with English abstract)
[2]	黄佳兴, 龚玉艳, 徐姗楠, 等, 2019. 南海中西部渔场主要渔业生物碳氮稳定同位素特征[J]. 热带海洋学报, 38(1): 76-84.
	HUANG JIAXING, GONG YUYAN, XU SHANNAN, et al, 2019. Characteristics of stable carbon and nitrogen isotopes of major fishery organisms in the fishing ground of central western South China Sea[J]. Journal of Tropical Oceanography, 38(1): 76-84. (in Chinese with English abstract)
[3]	黄小平, 黄良民, 宋金明, 等, 2019. 营养物质对海湾生态环境影响的过程与机理[M]. 北京: 科学出版社: 549-558. (in Chinese)
[4]	纪炜炜, 李圣法, 陈雪忠, 等, 2015. 基于稳定同位素方法的东海北部及其邻近水域主要游泳动物营养结构变化[J]. 海洋渔业, 37(6): 494-500.
	JI WEIWEI, LI SHENGFA, CHEN XUEZHONG, et al, 2015. Variation in trophic structure of nekton organisms from the northern East China Sea and adjacent waters based on stable isotope values[J]. Marine Fisheries, 37(6): 494-500. (in Chinese with English abstract)
[5]	牟新悦, 陈敏, 张琨, 等, 2017. 夏季大亚湾悬浮颗粒有机物碳、氮同位素组成及其物源指示[J]. 海洋学报, 39(2): 39-52.
	MOU XINYUE, CHEN MIN, ZHANG KUN, et al, 2017. Stable carbon and nitrogen isotopes as tracers of sources of suspended particulate organic matter in the Daya Bay in summer[J]. Haiyang Xuebao, 39(2): 39-52. (in Chinese with English abstract)
[6]	宁加佳, 杜飞雁, 王雪辉, 等, 2016. 南沙群岛西南部陆架区底层鱼类营养结构研究[J]. 海洋与湖沼, 47(2): 468-475.
	NING JIAJIA, DU FEIYAN, WANG XUEHUI, et al, 2016. The trophic structure of demersal fish species in Southwestern continental shelf of Nansha Islands, South China Sea[J]. Oceanologia et Limnologia Sinica, 47(2): 468-475. (in Chinese with English abstract)
[7]	王友绍, 王肇鼎, 黄良民, 2004. 近20年来大亚湾生态环境的变化及其发展趋势[J]. 热带海洋学报, 23(5): 85-95.
	WANG YOUSHAO, WANG ZHAODING, HUANG LIANGMIN, 2004. Environment changes and trends in Daya Bay in recent 20 years[J]. Journal of Tropical Oceanography, 23(5): 85-95. (in Chinese with English abstract)
[8]	王玉堃, 2015. 耳石微细结构和微化学示踪技术在鱼类种群生态学研究中的应用[D]. 青岛: 中国海洋大学.
	WANG YUKUN, 2015. Preliminary studies on the population ecology based on fish otolith microstructure and microchemistry[D]. Qingdao: Ocean University of China. (in Chinese with English abstract)
[9]	谢斌, 李云凯, 张虎, 等, 2017. 基于稳定同位素技术的海州湾海洋牧场食物网基础及营养结构的季节性变化[J]. 应用生态学报, 28(7): 2292-2298.
	XIE BIN, LI YUNKAI, ZHANG HU, et al, 2017. Food web foundation and seasonal variation of trophic structure based on the stable isotopic technique in the marine ranching of Haizhou Bay, China[J]. Chinese Journal of Applied Ecology, 28(7): 2292-2298. (in Chinese with English abstract)
[10]	徐军, 张敏, 谢平, 2010. 氮稳定同位素基准的可变性及对营养级评价的影响[J]. 湖泊科学, 22(1): 8-20. doi: 10.18307/2010.0102
	XU JUN, ZHANG MIN, XIE PING, 2010. Variability of stable nitrogen isotopic baselines and its consequence for trophic modeling[J]. Journal of Lake Sciences, 22(1): 8-20. (in Chinese with English abstract) doi: 10.18307/2010.0102
[11]	徐姗楠, 郭建忠, 范江涛, 等, 2020. 夏季大亚湾鱼类群落结构与多样性[J]. 生态学杂志, 39(4): 1254-1264.
	XU SHANNAN, GUO JIANZHONG, FAN JIANGTAO, et al, 2020. Fish community structure and diversity in Daya Bay in summer[J]. Chinese Journal of Ecology, 39(4): 1254-1264. (in Chinese with English abstract)
[12]	杨文超, 黄道建, 陈继鑫, 等, 2020. 大亚湾近十年沉积物中汞、砷分布及污染评价[J]. 水产科学, 39(6): 915-921.
	YANG WENCHAO, HUANG DAOJIAN, CHEN JIXIN, et al, 2020. Distribution and pollution assessment of Hg and As contents in surface sediments of Daya Bay in the past ten years[J]. Fisheries Science, 39(6): 915-921. (in Chinese with English abstract)
[13]	曾艳艺, 赖子尼, 杨婉玲, 等, 2018. 珠江河口渔业生物稳定同位素营养级分析[J]. 生态学杂志, 37(1): 194-202.
	ZENG YANYI, LAI ZINI, YANG WANLING, et al, 2018. Trophic spectrum of fishery species from the Pearl River Estuary by stable isotope analysis[J]. Chinese Journal of Ecology, 37(1): 194-202. (in Chinese with English abstract)
[14]	张硕, 高世科, 于雯雯, 等, 2019. 碳、氮稳定同位素在构建海洋食物网及生态系统群落结构中的研究进展[J]. 水产养殖, 40(7): 6-10.
	ZHANG SHUO, GAO SHIKE, YU WENWEN, et al, 2019. Research progress of stable carbon and nitrogen isotopes in the construction of marine food web and ecosystem community structure[J]. Journal of Aquaculture, 40(7): 6-10. (in Chinese with English abstract)
[15]	张文博, 黄洪辉, 李纯厚, 等, 2019. 华南典型海湾主要渔业生物碳氮稳定同位素研究[J]. 南方水产科学, 15(5): 9-14.
	ZHANG WENBO, HUANG HONGHUI, LI CHUNHOU, et al, 2019. Study on carbon and nitrogen stable isotopes of main fishery species in typical gulf, southern China[J]. South China Fisheries Science, 15(5): 9-14. (in Chinese with English abstract)
[16]	BODE A, CARRERA P, GONZÁLEZ-NUEVO G, et al, 2018. A trophic index for sardine (Sardina pilchardus) and its relationship to population abundance in the southern Bay of Biscay and adjacent waters of the NE Atlantic[J]. Progress in Oceanography, 166: 139-147. doi: 10.1016/j.pocean.2017.08.005
[17]	DE SMET B, FOURNIER J, DE TROCH M, et al, 2015. Integrating ecosystem engineering and food web ecology: testing the effect of biogenic reefs on the food Web of a soft-bottom intertidal area[J]. PLoS One, 10(10): e0140857. doi: 10.1371/journal.pone.0140857
[18]	HOBSON K A, FISK A, KARNOVSKY N, et al, 2002. A stable isotope (δ¹³C, δ¹⁵N) model for the North Water food web: implications for evaluating trophodynamics and the flow of energy and contaminants[J]. Deep Sea Research Part II: Topical Studies in Oceanography, 49(22-23): 5131-5150. doi: 10.1016/S0967-0645(02)00182-0
[19]	HUSSEY N E, MACNEIL M A, MCMEANS B C, et al, 2014. Rescaling the trophic structure of marine food webs[J]. Ecology Letters, 17(2): 239-250. doi: 10.1111/ele.12226
[20]	JACKSON M C, DONOHUE I, JACKSON A L, et al, 2012. Population-level metrics of trophic structure based on stable isotopes and their application to invasion ecology[J]. PLoS One, 7(2): e31757. doi: 10.1371/journal.pone.0031757
[21]	LAYMAN C A, ARRINGTON D A, MONTAÑA C G, et al, 2007. Can stable isotope ratios provide for community-wide measures of trophic structure[J]. Ecology, 88(1): 42-48. doi: 10.1890/0012-9658(2007)88[42:CSIRPF]2.0.CO;2
[22]	MATTHEWS B, MAZUMDER A, 2005. Consequences of large temporal variability of zooplankton δ¹⁵N for modeling fish trophic position and variation[J]. Limnology and Oceanography, 50(5): 1404-1414. doi: 10.4319/lo.2005.50.5.1404
[23]	MCMEANS B C, ROONEY N, ARTS M T, et al, 2013. Food web structure of a coastal Arctic marine ecosystem and implications for stability[J]. Marine Ecology Progress Series, 482: 17-28. doi: 10.3354/meps10278
[24]	PAULY D, PALOMARES M L, FROESE R, et al, 2001. Fishing down Canadian aquatic food webs[J]. Canadian Journal of Fisheries and Aquatic Sciences, 58(1): 51-62. doi: 10.1139/f00-193
[25]	POST D M, 2002. Using stable isotopes to estimate trophic position: Models, methods, and assumptions[J]. Ecology, 83(3): 703-718. doi: 10.1890/0012-9658(2002)083[0703:USITET]2.0.CO;2
[26]	SABEEL R A O, INGELS J, PAPE E, et al, 2015. Macrofauna along the Sudanese Red Sea coast: potential effect of mangrove clearance on community and trophic structure[J]. Marine Ecology, 36(3): 794-809. doi: 10.1111/maec.12184
[27]	SÁNCHEZ-HERNÁNDEZ J, AMUNDSEN P A, 2018. Ecosystem type shapes trophic position and omnivory in fishes[J]. Fish and Fisheries, 19(6): 1003-1015. doi: 10.1111/faf.12308
[28]	YING RUI, CAO YITING, YIN FANGMIN, et al, 2020. Trophic structure and functional diversity reveal pelagic-benthic coupling dynamic in the coastal ecosystem of Daya Bay, China[J]. Ecological Indicators, 113: 106241. doi: 10.1016/j.ecolind.2020.106241
[29]	ZANDEN M J V, CHANDRA S, ALLEN B C, et al, 2003. Historical food web structure and restoration of native aquatic communities in the Lake Tahoe (California-Nevada) Basin[J]. Ecosystems, 6(3): 274-288. doi: 10.1007/s10021-002-0204-7
[30]	ZANDEN M J V, FETZER W W, 2007. Global patterns of aquatic food chain length[J]. Oikos, 116(8): 1378-1388. doi: 10.1111/j.0030-1299.2007.16036.x
[31]	ZHOU LINBIN, HUANG LIANGMIN, TAN YEHUI, et al, 2015. Size-based analysis of a zooplankton community under the influence of the Pearl River plume and coastal upwelling in the northeastern South China Sea[J]. Marine Biology Research, 11(2): 168-179. doi: 10.1080/17451000.2014.904882

Metrics

Viewed

Full text

1120

HTML			PDF

最新录用	在线预览	正式出版	最新录用	在线预览	正式出版
0	0	288	6	0	826

来源	本网站	其他网站

次数	437	683
比例	39%	61%

Abstract

545

最新录用	在线预览	正式出版

9	0	536

来源	本网站	其他网站

次数	477	69
比例	87%	13%

Cited

Web of Science	Crossref	ScienceDirect	Search for Citations in Google Scholar >>


This page requires you have already subscribed to WoS.

Shared

参数名称	简写	含义	参数值
δ¹³C比值范围	CR	图中δ¹³C 最大值与最小值之间的绝对距离, 反映初始食源的多样性特征	2.83
δ¹⁵N比值范围	NR	图中δ¹⁵N 最大值与最小值之间的绝对距离, 反映消费者所占的营养层次	4.18
多边形面积	TA	由所有物种在δ¹³C-δ¹⁵N 双位图上组成的多边形面积, 是衡量群落占据的生态位空间的总数量, 代表食物网中营养多样性的总范围	8.30
质心均距	CD	质心坐标为所有样品δ¹³C、δ¹⁵N的平均值, 计算所有样品到质心的欧氏距离, 并得出平均值, 表示群落营养多样性的平均水平	1.18
最短均值	NND	相邻两点间最短距离的平均值, 反映群落的聚集度密度	0.31
最短均值标准差	SDNND	相邻两点间最短距离的标准差, 反映群落物种聚集度均匀度, 表示营养生态位分布范围水平	0.23

区域	参考文献	CR	NR	TA	CD	NND	SDNND
大亚湾西南海域	本文	2.83	4.18	8.30	1.18	0.31	0.23
海陵湾	张文博等, 2019	2.44	3.06	5.10	0.93	0.55	0.35
陵水湾	张文博等, 2019	4.45	4.66	11.18	1.49	0.60	0.54
珠江口海域	曾艳艺等, 2018	12.58	7.57	—	—	—	—
海州湾	谢斌等, 2017	3.70	6.40	13.00	1.37	0.61	0.64
南海中西部海域	黄佳兴等, 2019	3.49	4.91	9.48	1.20	1.69	0.74
南沙群岛西南陆架区	宁加佳等, 2016	3.40	4.30	5.80	1.00	0.37	0.43
东海中北部海域	纪炜炜等, 2015	3.38	3.45	7.02	1.12	0.42	0.28

2020年冬季大亚湾西南海域主要渔业生物碳氮稳定同位素研究

Study on stable isotopes of carbon and nitrogen of main fishery organisms in the southwestern waters of Daya Bay, South China Sea in winter 2020

RichHTML

PDF (PC)

赞

可视化

摘要/Abstract

引用本文

使用本文

图/表 6

参考文献 31

相关文章 15

Metrics

本文评价

推荐阅读 0

[1]	奚琛, 林宗轩, 萨如拉, 邓玺, 刘强, 倪亮, 罗来才, 马腾, 谢智杰, 陈思若, 陈松泽. 基于双浮标连续监测资料分析大亚湾西南部海域水体环境变化特征及其影响因素[J]. 热带海洋学报, 2024, 43(4): 153-164.
[2]	孙翠慈, 岳维忠, 赵文杰, 王友绍. 大亚湾表层沉积物碳水化合物活性酶基因分布特征[J]. 热带海洋学报, 2023, 42(5): 76-91.
[3]	宋星宇, 林雅君, 张良奎, 向晨晖, 黄亚东, 郑传阳. 粤港澳大湾区近海中小型浮游动物分布特征及影响因素^*[J]. 热带海洋学报, 2023, 42(3): 136-148.
[4]	姜迅, 武文, 宋德海. 大亚湾水质对人类活动响应的关键控制指标识别和量化解析[J]. 热带海洋学报, 2023, 42(1): 182-191.
[5]	陈靖夫, 钟瑜, 王磊, 郭雨沛, 邱大俊. 环境DNA分析大亚湾夜光藻藻华对真核浮游生物群落的影响^*[J]. 热带海洋学报, 2022, 41(5): 121-132.
[6]	李尧, 向晨晖, 江志坚, 宋星宇. 大亚湾夏季浮游群落生产代谢特征及其影响因素^*[J]. 热带海洋学报, 2021, 40(6): 83-92.
[7]	向晨晖, 刘甲星, 柯志新, 周林滨, 谭烨辉. 大亚湾浮游植物粒级结构和种类组成对淡澳河河口水加富的响应^*[J]. 热带海洋学报, 2021, 40(2): 49-60.
[8]	张立明, 谭烨辉, 李佳俊, 黄小平, 刘甲星. 大亚湾夏季浮游植物群落结构及对淡澳河输入的响应特征*[J]. 热带海洋学报, 2020, 39(5): 43-54.
[9]	王卉,李恒翔,李路,严岩. 大亚湾大型海藻丛的大角玻璃钩虾种群分布特征[J]. 热带海洋学报, 2019, 38(4): 52-58.
[10]	谢福武, 宋星宇, 谭烨辉, 谭美婷, 黄亚东, 刘华雪. 模拟升温和营养盐加富对大亚湾浮游生物群落代谢的影响^*[J]. 热带海洋学报, 2019, 38(2): 48-57.
[11]	黄佳兴, 龚玉艳, 徐姗楠, 王欢欢, 张魁, 张俊, 陈作志. 南海中西部渔场主要渔业生物碳氮稳定同位素特征[J]. 热带海洋学报, 2019, 38(1): 76-84.
[12]	谢福武, 刘华雪, 黄洪辉, 宋星宇. 大亚湾浮游植物粒级结构对温排水和营养盐输入的响应^*[J]. 热带海洋学报, 2018, 37(3): 55-64.
[13]	徐翠莲, 李涛, 胡思敏, 王有军, 黄晖, 刘胜. 大亚湾核电站邻近水域桡足幼体现场摄食研究[J]. 热带海洋学报, 2018, 37(2): 17-25.
[14]	武文, 严聿晗, 宋德海. 大亚湾的潮汐动力学研究——I.潮波系统的观测分析与数值模拟^*[J]. 热带海洋学报, 2017, 36(3): 34-45.
[15]	严聿晗, 武文, 宋德海, 鲍献文. 大亚湾的潮汐动力学研究——Ⅱ.潮位和潮流双峰现象的产生机制[J]. 热带海洋学报, 2017, 36(3): 46-54.