Study on the colonization dynamics and successional trajectories of sessile organisms on steel-concrete cubic artificial algal reefs
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摘要: 针对海藻场修复中人工藻礁单一材料生境异质性不足、生物附着效果较差的问题,本研究设计了一种钢材—混凝土异质型复合材料藻礁,制作礁体12个并于2021年8月投放至荣成马山里海域,于2021年11月、2022年6月和9月及2023年5月和8月,分别对钢材和混凝土大型附着藻类和附着动物以及投礁区关键环境因子进行了跟踪监测。结果显示:(1)两种材料对大型藻类的建植效果存在显著不同,其中混凝土的大型藻类生物量显著高于钢材,整个监测周期平均达到钢材的1.7倍(P<0.05);(2)大型附着藻类群落结构主要受季节和礁龄的双重驱动,呈现出由绿藻门向褐藻门的演替规律,红藻门主要出现在演替的过渡期但未形成稳定的优势阶段,在投礁后20个月形成了以裙带菜(Undaria pinnatifida)为绝对优势种(Y=0.99)的稳定顶级群落;(3)不同材料对附着动物的定殖效果存在显著差异,钢材的附着动物生物量显著高于混凝土,平均是其8.3倍(P<0.05)。结果表明,在同一礁体单元内,混凝土更有利于大型藻类建植,钢材则更有利于附着动物定殖,二者组合使用不仅能够同步促进大型藻类和附着动物定殖的双效提升,从而实现了材料的功能互补,还可显著提高附着生物的生物量与多样性水平,为人工藻礁建礁材料筛选提供了新思路。Abstract: To address the limited habitat heterogeneity and suboptimal biological attachment capacity of single-material artificial algal reefs in seaweed bed restoration, this study designed a steel-concrete composite artificial algal reef. Twelve replicate reefs were fabricated and deployed in the Mashanli sea area of Rongcheng in August 2021. Attached macroalgae and animals colonizing both materials, as well as key environmental parameters at the reef site, were monitored in November 2021, June 2022, September 2022, May 2023, and August 2023. Results revealed: (1) the two materials differed significant in their macroalgal establishment effects, with the biomass of attached macroalgal on concrete being significantly higher than that attached on steel, reaching 1.7 times that on steel during the entire monitoring period on average (P < 0.05); (2) macroalgal community structure was jointly shaped by seasonality and reef age, progressing from an early Chlorophyta-dominated phase to a late Phaeophyta-dominated phase. Rhodophyta appeared transiently but never established a persistent dominant stage. After 20 months, a stable, top-level community dominated by Undaria pinnatifida emerged (Y = 0.99); (3) the colonization dynamics of attached animals varied significantly between two substrate materials. Specifically the biomass of attached animals on steel substrates was 8.3 times higher than that on concrete substrates (P < 0.05). These results indicate that, within identical reef units, concrete supported greater macroalgal establishment, whereas steel facilitated significantly higher settlement of attached animals. Combining both materials in artificial reef construction yields synergistic benefits: it concurrently promotes macroalgal development and attached animal colonization, thereby achieving functional complementarity, and significantly enhances both the total biomass and taxonomic diversity of sessile organisms. This dual-substrate strategy provides an evidence-based framework for optimizing material selection in artificial algal reef engineering.
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Key words:
- Artificial algal reef /
- Material selection /
- Macroalgae /
- Community succession /
- Attachment effect
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图 2 人工藻礁立体结构示意图(A)与内部结构俯视图(B)
注:①为水体交换孔(Φ80 mm);②为钢制立柱;③为半圆形钢板构件(Φ200 mm);④为1/4圆弧无孔钢板底座;⑤为不同材料水平板。
Fig. 2 Schematic diagram (A) and internal structural perspective (B) of the artificial algal reef
Note: ① a water exchange aperture (diameter: 80 mm); ② a load-bearing structural steel column; ③ a semi-circular steel plate component (diameter: 200 mm); ④ a quarter-circular, non-porous steel base plate; and ⑤ a horizontally oriented composite plate composed of different materials.
图 3 不同材料大型附着藻类生物量的变化
注:误差棒上小写字母表示相同材料不同时间之间存在显著差异,*表示相同时间不同材料之间存在显著差异(P<0.05)。
Fig. 3 Temporal changes in macroalgal biomass across substrate materials
Note: Lowercase letters on error bars denote significant differences among sampling times within each substrate material; and asterisks (*) denote significant differences between substrate types at each sampling time (P<0.05).
图 5 不同材料大型藻类香农-威纳多样性指数(A)、物种丰富度指数(B)和均匀度指数(C)的变化
注:S: 钢材; C: 混凝土; 误差棒上小写字母表示相同材料不同时间之间存在显著差异,*表示相同时间不同材料之间存在显著差异(P<0.05)。
Fig. 5 Temporal changes in Shannon-Wiener index (A), Margalef's index (B), and Pielou's index (C) of macroalgae between substrate types
Note: S: Steel; C: Concrete. Lowercase letters on error bars denote significant differences among sampling times within each substrate material; and asterisks (*) denote significant differences between substrate types at each sampling time (P<0.05).
图 6 大型藻类群落聚类分析(A)与非度量多维尺度排序(nMDS)(B)
注:分组表示为“时间-材料”。S:钢材,C:混凝土。
Fig. 6 Cluster analysis (A) and non-metric multidimensional scaling (nMDS) ordination (B) of macroalgal assemblages across substrate types
Note: Samples are grouped by sampling time and substrate type (S: steel; C: concrete), with substrate as the primary fixed factor in multivariate analyses.
图 7 不同材料附着动物生物量(A)与密度(B)的变化
注:S: 钢材 Steel; C: 混凝土 Concrete; 误差棒上小写字母表示相同材料不同时间之间存在显著差异,*表示相同时间不同材料之间存在显著差异(P<0.05)。
Fig. 7 Temporal changes in attached animal biomass (A) and density (B) across substrate materials
Note: S: Steel; C: Concrete. Lowercase letters on error bars denote significant differences among sampling times within each substrate material; and asterisks (*) denote significant differences between substrate types at each sampling time (P<0.05).
表 1 水体环境指标调查结果
Tab. 1 Investigation results of water environmental indicators
指标 Parameter 2021.11 2022.06 2022.09 2023.05 2023.08 温度T(℃) 15.87 ± 0.15d 24.93 ± 0.32a 21.53 ± 0.25c 15.40 ± 0.30d 23.67 ± 0.38b 盐度Sal(‰) 31.97 ± 0.06d 29.57 ± 0.64a 29.70 ± 0.36ab 30.23 ± 0.06bc 30.40 ± 0.17c 流速V(m·s−1) 0.13 ± 0.01ab 0.14 ± 0.02ab 0.15 ± 0.01b 0.13 ± 0.01ab 0.12 ± 0.02a 溶解氧DO(mg L−1) 7.60 ± 0.01c 7.43 ± 0.04d 6.68 ± 0.08e 12.56 ± 0.02a 9.06 ± 0.09b pH值 8.47 ± 0.06a 8.30 ± 0.10a 8.47 ± 0.15a 8.46 ± 0.04a 7.31 ± 0.09b $ {{\rm {PO}}_4^{3-}} $-P(mg L−1) 0.020 ± 0.001a 0.012 ± 0.001b 0.016 ± 0.001a 0.003 ± 0.001c 0.006 ± 0.002c 无机氮DIN(mg L−1) 0.35 ± 0.01b 0.28 ± 0.03c 0.34 ± 0.01c 0.55 ± 0.07a 0.40 ± 0.03b 注:小写字母表示不同调查时间之间存在显著差异(P<0.05)。 Note: Lowercase letters indicate statistically significant differences across survey time (P<0.05). 表 2 人工藻礁大型附着藻类名录
Tab. 2 Species composition of macroalgae associated with artificial algal reefs
门
Phylum种类
Species2021.11 2022.06 2022.09 2023.05 2023.08 温度性质
Temperature adaptation natureS C S C S C S C S C 绿藻门
Chlorophyta肠浒苔 Enteromorpha intestinalis + + CT 缘管浒苔 Enteromorpha linza + + + + WT 假根羽藻 Bryopsis corticulans + + WT 孔石莼 Ulva pertusa + + + + + + + WT 刺松藻 Codium fragile + WT 硬毛藻 Chaetomorpha antennina + + WT 线形硬毛藻 Chaetomorpha linum + + + + + + + WT 红藻门
Rhodophyta小珊瑚藻 Corallina pilulifera + + ST 角叉菜 Chondrus ocellatus + + WT 多管藻 Polysiphonia urceolata + LB 繁枝蜈蚣藻 Grateloupia ramosissima + WT 龙须菜 Asparagus schoberioides + WT 褐藻门
Phaeophyta水云 Ectocarpus siliculosus + CT 裙带菜Undaria pinnatifida + + + + WT 注:S表示钢材,C表示混凝土,+表示采到藻类,WT表示暖温带种类,CT表示冷温带种类,ST表示亚热带种类,LB表示亚寒带种类。 Note: S = steel; C = concrete; “+” denotes presence of the corresponding macroalgal species; WT = warm temperate; CT = cold temperate; ST = sub tropical; LB = lower boreal. 表 3 不同材料大型藻类优势种及优势度
Tab. 3 Dominant macroalgal species and their relative dominance across substrate types
时间
Time优势种
Dominant species优势度 Relative dominance 钢材 Steel 混凝土 Concrete 2021.11 假根羽藻 Bryopsis corticulans 0.49 0.50 缘管浒苔 Enteromorpha linza 0.30 0.42 小珊瑚藻 Corallina pilulifera 0.06 0.08 水云 Ectocarpus siliculosus 0.15 — 2022.06 孔石莼 Ulva pertusa 1.00 1.00 2022.09 孔石莼 Ulva pertusa 0.99 0.89 硬毛藻 Chaetomorpha antennina — 0.10 2023.05 裙带菜 Undaria pinnatifida 0.99 0.99 2023.08 裙带菜 Undaria pinnatifida 0.57 0.97 孔石莼 Ulva pertusa 0.42 — 龙须菜 Asparagus schoberioides — 0.03 表 4 不同调查时间两种材料表面绿藻门、红藻门和褐藻门生物量占大型附着藻类总生物量的比例
Tab. 4 Proportions of Chlorophyta, Rhodophyta and Phaeophyta biomass in the total attached macroalgal biomass on steel and concrete substrates survey times
时间
Time门
Phylum占比 Proportion 钢材 Steel 混凝土 Concrete 2021.11 绿藻门 Chlorophyta 64.80 92.18 红藻门 Rhodophyta 6.07 7.82 褐藻门 Phaeophyta 10.89 — 2022.06 绿藻门 Chlorophyta 100.00 100.00 红藻门 Rhodophyta — — 褐藻门 Phaeophyta — — 2022.09 绿藻门 Chlorophyta 100.00 100.00 红藻门 Rhodophyta — — 褐藻门 Phaeophyta — — 2023.05 绿藻门 Chlorophyta 1.31 0.20 红藻门 Rhodophyta 0.00 0.29 褐藻门 Phaeophyta 98.68 99.52 2023.08 绿藻门 Chlorophyta 42.52 — 红藻门 Rhodophyta — 3.00 褐藻门 Phaeophyta 57.48 96.99 注:—表示未检出,0.00表示已检出但占比极低。 Note: “—” denotes absence of detection; “0.00” indicates presence at trace levels. 表 5 人工藻礁附着动物名录
Tab. 5 Species composition of attached animals associated with artificial algal reefs
门
Phylum种类
Species2021.11 2022.06 2022.09 2023.05 2023.08 温度性质
Temperature adaptation natureS C S C S C S C S C 软体动物门
Mollusca长牡蛎 Crassostrea gigas + + + + + + + + WT 紫贻贝 Mytilus edulis + + + WT 东方缝栖蛤 Hiatella orientalis + + + WT 短滨螺 Littorina brevicula + WT 红带织纹螺 Nassarius succinctus + WT 秀丽织纹螺 Nassarius festivus + WT 布尔小笔螺 Mitrella burchardi + WT 丽小笔螺 Mitrella bella + WT 节肢动物门
Arthropoda四齿矶蟹 Pugettia quadridens + WT 大蜾蠃蜚 Corophium major + WT 脊索动物门
Chordata玻璃海鞘 Ciona intestinalis + + + WT 柄海鞘 Styela clava + + + WT 环节动物门
Annelida独齿围沙蚕 Perinereis cultrifera + + WT 长双须虫 Eteone longa + WT 多齿全刺沙蚕 Nectoneanthes multignatha + + WT 沙蚕 Nereis succinea + + WT 无疣齿吻沙蚕 Inermonephtys inermis + WT 寡鳃齿吻沙蚕 Nephtys oligobranchia + + WT 多鳃齿吻沙蚕 Nephtys polybranchia + WT 不倒翁虫 Sternaspis scutata + WT 网纹哈鳞虫 Harmothoё dictyophora + + WT 长须沙蚕 Nereis longior + + WT 树蛰虫 Pista cristata + WT 长锥虫 Haploscoloplos elongates + WT 拟特须虫 Paralacydonia paradoxa + WT 注:S表示钢材,C表示混凝土,+表示采集到附着动物,WT表示暖温带种类。 Note: S = steel; C = concrete; “+” denotes presence of the corresponding attached animal species; WT = warm temperate. 表 6 附着动物生物多样性指数
Tab. 6 Diversity indices of attached animal assemblages across substrate types
时间
Time材料
Material香农-威纳多样性指数H'
Shannon-Wiener index物种丰富度指数D
Margalef’s index均匀度指数J
Pielou’s index2021.11 钢材 0.81 ± 0.25* 0.24 ± 0.10* 0.97 ± 0.05 混凝土 0.00 ± 0.00 0.00 ± 0.00 — 2022.06 钢材 1.42 ± 0.02* 0.51 ± 0.01* 0.89 ± 0.01 混凝土 0.85 ± 0.16 0.31 ± 0.01 0.78 ± 0.15 2022.09 钢材 0.46 ± 0.40 0.13 ± 0.11 1.00 ± 0.00 混凝土 — — — 2023.05 钢材 0.52 ± 0.04 0.16 ± 0.00 0.77 ± 0.04 混凝土 0.21 ± 0.37 0.06 ± 0.10 0.87 ± 0.05* 2023.08 钢材 2.11 ± 0.15 1.13 ± 0.10* 0.93 ± 0.02 混凝土 1.71 ± 0.20 0.75 ± 0.14 0.96 ± 0.03 注:“*”表示相同时间不同材料间具有显著差异(P<0.05)。2021年11月混凝土表面仅记录到1种附着动物,故H'和D为0,J以“—”表示;2022年9月混凝土表面未记录到附着动物,故相关指数均以“—”表示。 Note: “*” denote significant differences between substrate types at each sampling time(P<0.05). In November 2021, only one attached animal species was detected on the concrete substrate; consequently H' and D were both zero, whereas J is undefined and reported as “—”. In September 2022, no attached animals species were detected on the concrete substrate; and therefore, all three diversity indices are undefined and reported as “—”. -
[1] United Nations Environment Programme. Into the blue: securing a sustainable future for kelp forests[R]. Nairobi: UNEP, 2023. [2] Hanley M E, Firth L B, Foggo A. Victim of changes? Marine macroalgae in a changing world[J]. Annals of Botany, 2024, 133(1): 1−16. doi: 10.1093/aob/mcad185 [3] Eger A M, Marzinelli E M, Beas-Luna R, et al. The value of ecosystem services in global marine kelp forests[J]. Nature Communications, 2023, 14(1): 1894. doi: 10.1038/s41467-023-37385-0 [4] Krause-Jensen D, Duarte C M. Substantial role of macroalgae in marine carbon sequestration[J]. Nature Geoscience, 2016, 9(10): 737−742. doi: 10.1038/ngeo2790 [5] Fourqurean J W, Duarte C M, Kennedy H, et al. Seagrass ecosystems as a globally significant carbon stock[J]. Nature Geoscience, 2012, 5(7): 505−509. doi: 10.1038/ngeo1477 [6] Breithaupt J L, Smoak J M, Smith III T J, et al. Organic carbon burial rates in mangrove sediments: strengthening the global budget[J]. Global Biogeochemical Cycles, 2012, 26(3): GB3011. doi: 10.1029/2012gb004375 [7] Mauffrey A R L, Cappelatti L, Griffin J N. Seaweed functional diversity revisited: confronting traditional groups with quantitative traits[J]. Journal of Ecology, 2020, 108(6): 2390−2405. doi: 10.1111/1365-2745.13460 [8] Valiela I, Bowen J L, York J K. Mangrove forests: one of the world’s threatened major tropical environments: at least 35% of the area of mangrove forests has been lost in the past two decades, losses that exceed those for tropical rain forests and coral reefs, two other well-known threatened environments[J]. BioScience, 2001, 51(10): 807−815. [9] United Nations General Assembly. United Nations Decade on Ecosystem Restoration (2021–2030): resolution/adopted by the general assembly[R]. New York: United Nations, 2019. [10] Harris L E, Mostkoff B J, Zadikoff G. Artificial reefs: from waste to resources[C]//OCEANS 96 MTS/IEEE Conference Proceedings. The Coastal Ocean-Prospects for the 21st Century. Fort Lauderdale: IEEE, 1996: 754−759. [11] 张磊, 郝振林, 张秀梅. 不同模型礁底栖藻类附着效果的初步研究[J]. 南方水产科学, 2011, 7(2): 1−7.Zhang Lei, Hao Zhenlin, Zhang Xiumei. Preliminary study on attaching effect of benthic algae on different reef models[J]. South China Fisheries Science, 2011, 7(2): 1−7. [12] Lee I C, Park S, Woo H E, et al. A study on macroalgae establishment on concrete substratum covered by oyster shells[J]. Journal of the Korean Society of Marine Environment and Safety, 2021, 27(5): 639−646. doi: 10.7837/kosomes.2021.27.5.639 [13] Harlin M M, Lindbergh J M. Selection of substrata by seaweeds: optimal surface relief[J]. Marine Biology, 1977, 40(1): 33−40. doi: 10.1007/BF00390625 [14] Jung S W, Choi C G. Seaweed community and succession on a trapezoidal-shaped artificial reef[J]. Ocean Science Journal, 2022, 57(1): 130−140. doi: 10.1007/s12601-021-00053-9 [15] Cho S H, Choi C G, Choa J H. Restoration of the seaweed forest and algal succession on a porous type (shaped half saw teeth) artificial reef[J]. Korean Journal of Fisheries and Aquatic Sciences, 2007, 40(4): 220−225. doi: 10.5657/kfas.2007.40.4.220 [16] Earp H S, Smale D A, Pérez-Matus A, et al. A quantitative synthesis of approaches, biases, successes, and failures in marine forest restoration, with considerations for future work[J]. Aquatic Conservation: Marine and Freshwater Ecosystems, 2022, 32(11): 1717−1731. doi: 10.1002/aqc.3880 [17] Romoth K, Darr A, Papenmeier S, et al. Substrate heterogeneity as a trigger for species diversity in marine benthic assemblages[J]. Biology, 2023, 12(6): 825. doi: 10.3390/biology12060825 [18] 邓筱凡, 张宏瑜, 吴忠迅, 等. 荣成马山里海域海草床分布现状及其生态特征[J]. 海洋学报, 2022, 44(8): 97−109.Deng Xiaofan, Zhang Hongyu, Wu Zhongxun, et al. Distribution and ecological characteristics of seagrass bed of Mashanli sea area in Rongcheng[J]. Haiyang Xuebao, 2022, 44(8): 97−109. [19] 李文涛, 王欢, 仲崇凤, 等. 山东荣成马山里海域大型藻类群落结构时空变化研究[J]. 海洋科学, 2022, 46(5): 74−85.Li Wentao, Wang Huan, Zhong Chongfeng, et al. Spatial and temporal variations in the benthic macroalgal communities along the Mashanli coast of Rongcheng, Shandong Province, China[J]. Marine Sciences, 2022, 46(5): 74−85. [20] 中华人民共和国农业部. SC/T 9416-2014, 人工鱼礁建设技术规范[S]. 北京: 中国农业出版社, 2014.Ministry of Agriculture of the People’s Republic of China. SC/T 9416-2014, Technical specifications for artificial reef construction[S]. Beijing: China Agriculture Press, 2014. [21] 中华人民共和国国家质量监督检验检疫总局, 中国国家标准化管理委员会. GB/T 12763.2-2007, 海洋调查规范 第2部分: 海洋水文观测[S]. 北京: 中国标准出版社, 2008.General Administration of Quality Supervision, Inspection and Quarantine of the People’s Republic of China, Standardization Administration of the People’s Republic of China. GB/T 12763.2-2007, Specifications for oceanographic survey—Part 2: marine hydrographic observation[S]. Beijing: Standards Press of China, 2008. [22] 中华人民共和国国家质量监督检验检疫总局, 中国国家标准化管理委员会. GB 17378.4-2007, 海洋监测规范 第4部分: 海水分析[S]. 北京: 中国标准出版社, 2008.General Administration of Quality Supervision, Inspection and Quarantine of the People’s Republic of China, Standardization Administration of the People’s Republic of China. GB 17378.4-2007, The specification for marine monitoring—Part 4: seawater analysis[S]. Beijing: Standards Press of China, 2008. [23] 刘涛, 陈伟州, 谢朝添. 黄、渤海及东海常见大型海藻图鉴[M]. 北京: 海洋出版社, 2018. (查阅网上资料, 未找到对应的标黄作者信息, 请确认)Liu Tao, Chen Weizhou, Xie Chaotian. Illustrated Atlas of Common Marine Macroalgae in the Yellow Sea, Bohai Sea and East China Sea[M]. Beijing: China Ocean Press, 2018. (查阅网上资料, 未找到对应的英文翻译, 请确认) [24] 张学雷. 黄海底栖动物常见种形态分类图谱[M]. 北京: 科学出版社, 2024.Zhang Xuelei. Illustrated Taxonomic Atlas of Common Benthic Animals in the Yellow Sea[M]. Beijing: Science Press, 2024. (查阅网上资料, 未找到对应的英文翻译, 请确认) [25] 生态环境部. HJ 1300-2023, 海水、海洋沉积物和海洋生物质量评价技术规范[S]. 北京: 中国环境科学出版社, 2023.Ministry of Ecology and Environment. HJ 1300-2023, Technical specification for assessment of sea water, marine sediment and marine biological quality[S]. Beijing: China Environmental Science Press, 2023. [26] Whitfield M, Watson A J. The influence of biomineralisation on the composition of seawater[M]//Westbroek P, Jong E W. Biomineralization and Biological Metal Accumulation. Dordrecht: Springer, 1983: 57−72. [27] Hargrave M S, Nylund G M, Enge S, et al. Co-cultivation with blue mussels increases yield and biomass quality of kelp[J]. Aquaculture, 2022, 550: 737832. doi: 10.1016/j.aquaculture.2021.737832 [28] Miller R J, Lafferty K D, Lamy T, et al. Giant kelp, Macrocystis pyrifera, increases faunal diversity through physical engineering[J]. Proceedings of the Royal Society B: Biological Sciences, 2018, 285(1874): 20172571. doi: 10.1098/rspb.2017.2571 [29] Natanzi A S, Thompson B J, Brooks P R, et al. Influence of concrete properties on the initial biological colonisation of marine artificial structures[J]. Ecological Engineering, 2021, 159: 106104. doi: 10.1016/j.ecoleng.2020.106104 [30] Hayek M, Salgues M, Souche J C, et al. Influence of the intrinsic characteristics of cementitious materials on biofouling in the marine environment[J]. Sustainability, 2021, 13(5): 2625. doi: 10.3390/su13052625 [31] Vivier B, Dauvin J C, Navon M, et al. Marine artificial reefs, a meta-analysis of their design, objectives and effectiveness[J]. Global Ecology and Conservation, 2021, 27: e01538. doi: 10.1016/j.gecco.2021.e01538 [32] Sousa W P. Experimental investigations of disturbance and ecological succession in a rocky intertidal algal community[J]. Ecological Monographs, 1979, 49(3): 227−254. doi: 10.2307/1942472 [33] Underwood A J, Anderson M J. Seasonal and temporal aspects of recruitment and succession in an intertidal estuarine fouling assemblage[J]. Journal of the Marine Biological Association of the United Kingdom, 1994, 74(3): 563−584. doi: 10.1017/S0025315400047676 [34] Choi C G, Takayama H, Segawa S, et al. Research Articles/Early stage of algae succession on artificial reefs at Muronohana, Ikata, Japan[J]. Fisheries and Aquatic Sciences, 2000, 3(1): 1−7. [35] 聂猛, 李文涛, 李勇, 等. 山东半岛典型海域大叶藻(Zostera marina)附着大型藻类群落结构[J]. 生态学杂志, 2014, 33(7): 1786−1794. doi: 10.13292/j.1000-4890.20140422.026Nie Meng, Li Wentao, Li Yong, et al. Structure of epiphytic algal community of eelgrass (Zostera marina) in a typical coastal area of Shandong Peninsula[J]. Chinese Journal of Ecology, 2014, 33(7): 1786−1794. doi: 10.13292/j.1000-4890.20140422.026 [36] Epstein G, Smale D A. Undaria pinnatifida: a case study to highlight challenges in marine invasion ecology and management[J]. Ecology and Evolution, 2017, 7(20): 8624−8642. doi: 10.1002/ece3.3430 [37] 张磊, 张秀梅, 吴忠鑫, 等. 荣成俚岛人工鱼礁区大型底栖藻类群落及其与环境因子的关系[J]. 中国水产科学, 2012, 19(1): 116−125.Zhang Lei, Zhang Xiumei, Wu Zhongxin, et al. Effect of environment on benthic macro-algal communities of artificial reefs in Lidao, Rongcheng[J]. Journal of Fishery Sciences of China, 2012, 19(1): 116−125. [38] Wang Baodong, Wang Xiulin, Zhan Run. Nutrient conditions in the Yellow Sea and the East China Sea[J]. Estuarine, Coastal and Shelf Science, 2003, 58(1): 127−136. doi: 10.1016/S0272-7714(03)00067-2 [39] Li Hongmei, Zhang Chuansong, Han Xiurong, et al. Changes in concentrations of oxygen, dissolved nitrogen, phosphate, and silicate in the southern Yellow Sea, 1980-2012: sources and seaward gradients[J]. Estuarine, Coastal and Shelf Science, 2015, 163: 44−55. [40] Booth J M, Fusi M, Giomi F, et al. Diel oxygen fluctuation drives the thermal response and metabolic performance of coastal marine ectotherms[J]. Proceedings of the Royal Society B: Biological Sciences, 2021, 288(1953): 20211141. doi: 10.1098/rspb.2021.1141 [41] Correia K M, Smee D L. Habitat suitability of drift macroalgae in two shallow coastal estuaries of the northern Gulf of Mexico[J]. Journal of Experimental Marine Biology and Ecology, 2022, 557: 151808. doi: 10.1016/j.jembe.2022.151808 [42] Li Yunxiao, Yang Hong, Dang Jiajia, et al. Seasonal variation of sea surface pH and its controls in the Jiaozhou Bay, China[J]. Continental Shelf Research, 2022, 232: 104613. doi: 10.1016/j.csr.2021.104613 [43] Zhang Guangzong, Wu Mengquan, Zhou Min, et al. The seasonal dissipation of Ulva prolifera and its effects on environmental factors: based on remote sensing images and field monitoring data[J]. Geocarto International, 2022, 37(3): 860−878. doi: 10.1080/10106049.2020.1745301 [44] Hiraoka M. Massive Ulva green tides caused by inhibition of biomass allocation to sporulation[J]. Plants, 2021, 10(11): 2482. doi: 10.3390/plants10112482 [45] Milazzo M, Badalamenti F, Riggio S, et al. Patterns of algal recovery and small-scale effects of canopy removal as a result of human trampling on a Mediterranean rocky shallow community[J]. Biological Conservation, 2004, 117(2): 191−202. doi: 10.1016/S0006-3207(03)00292-1 [46] Pocklington J B, Jenkins S R, Bellgrove A, et al. Disturbance alters ecosystem engineering by a canopy-forming alga[J]. Journal of the Marine Biological Association of the United Kingdom, 2018, 98(4): 687−698. doi: 10.1017/S0025315416002009 [47] Loke L H L, Liao L M, Bouma T J, et al. Succession of seawall algal communities on artificial substrates[J]. Raffles Bulletin of Zoology, 2016(S32): 1−10. -
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