Otolith Microchemical Analysis of Tapertail Anchovy Coilia nasus from Ariake Sea and Its Adjacent Tributaries in Japan
LIU Hongbo1, JIANG Tao1, XUAN Zhongya2, QIU Chen2, YANG Jian1,2
1. Key Laboratory of Fishery Ecological Environment Assessment and Resource Conservation in Middle and Lower Reaches of the Yangtze River, Freshwater Fisheries Research Center, Chinese Academy of Fishery Sciences, Wuxi 214081, China; 2. Wuxi Fisheries College, Nanjing Agricultural University, Wuxi 214081, China
Abstract:The estuarine tapertail anchovy (Coilia nasus) only distributes in Ariake Sea and the adjacent tributary rivers (e.g., Chikugo River and Rokkaku River) flowing into this sea area of Japan. It is a traditional commercial fish resource in this region and has been listed in the category of “vulnerable” species by the Fisheries Agency of Japan. For investigating its population dynamics, life history, and salinity habitat requirement, tapertail anchovy sampled from the Ariake Sea, Rokkaku River, and Chikugo River were studied by examining the environmental signatures of strontium (Sr) and calcium (Ca) in their otoliths using microchemical analysis. The Sr and Ca concentrations were standardized to Sr∶Ca ratios of Sr∶Ca×103 (Sr∶Ca ratio >7, higher salinity seawater; 3—7, brackish water; ≤3, freshwater habitat); along line transects from the core (0 μm) to the edge and Sr intensity map (color patterns: reddish, higher salinity seawater; greenish-yellowish, brackish water; bluish, freshwater habitat), showing that fish studied was generally divided into two distinct freshwater originated (i.e., anadromous) and non-freshwater originated (i.e., sea origin) ecological types. The former type was further divided into three different patterns of habitat history. The phenomena clearly reflected the diversity of population composition, fluctuation migration patterns and flexible habitat requirement strategies of tapertail anchovy in studied waters. In addition, 30% of tapertail anchovy in the present study were found incubation in the brackish-water, indicating that for the tapertail anchovy around Ariake Sea, the recruitments originated from estuarine brackish water also played the an important role, beside those traditionally originated from the tributary rivers.
[1]石田宏一,塚原博. 有明海および築後川流域におけるエツの生態について[J]. 九大農学芸誌,1972,26(1/2/3/4):217-221. [2]大嶋雄治. 豊穣の海·有明海の現状と課題[M]. 東京:恒星社厚生閣,2012:88-94. [3]刘洪波,姜涛,杨健. 日本有明海水域刀鲚资源现状及存在的问题[J]. 渔业信息与战略,2019,34(1):48-52. [4]田北徹,山口敦子. 有明海の魚類の現状と保全[J]. 魚類学雑誌,2011,58(2):199-202. [5]筑紫康博,金澤孝弘. エツ遡上期における筑後川の環境[J]. 福岡水海技セ研報,2004,14:17-20. [6]伊藤毅史,神崎博幸,増田裕二,等. 有明海佐賀県海域におけるエツに関する研究[J]. 佐賀有明水振セ研報,2017,28:99-104. [7]伊藤毅史,Simanjuntak C P H,木下泉. 有明海六角川におけるエツ仔稚魚の分布[J]. 水産増殖,2018,66(1):17-23. [8]Jiang T, Liu H B, Lu M J, et al. A possible connectivity among estuarine tapertail anchovy (Coilia nasus) populations in the Yangtze River, Yellow Sea, and Poyang Lake[J]. Estuaries and Coasts,2016,39(6):1762-1768. [9]Jiang T, Liu H B, Lu M J, et al. Discovery of a spawning area for anadromous Coilia nasus Temminck et Schlegel,1846 in Poyang Lake, China[J]. Journal of Applied Ichthyology,2017,33(2):189-192. [10]Secor D H. Application of otolith microchemistry analysis to investigate anadromy in Chesapeake Bay striped bass Morone saxatilis[J]. Fishery Bulletin,1992,90(4):798-806. [11]Campana S E. Chemistry and composition of fish otoliths: pathways, mechanisms and applications[J]. Marine Ecology-Progress Series,1999,188(1):263-297. [12]Tsukamoto K, Nakai, Tesch W. Do all freshwater eels migrate? [J].Nature,1998,396(6712):635-636. [13]Panfili J, Pontual H, Troadec H, et al. Manual of Fish Sclerochronology[M]. Brest:Ifremer-IRD Coedition,2002:243-304. [14]熊瑛,刘洪波,汤建华,等. 耳石微化学在海洋鱼类洄游类型和种群识别研究中的应用[J]. 生命科学,2015,27(7):953-959. [15]卢明杰,姜涛,刘洪波,等. 信江发现溯河洄游型刀鲚的实证研究[J]. 中国水产科学,2015,22(5):978-985. [16]Liu H B, Jiang T, Yang J. Unravelling habitat use of Coilia nasus from the Rokkaku and Chikugo Rivers of Japan by otolith strontium and calcium[J]. Acta Oceanologica Sinica,2018,37(6):52-60. [17]熊瑛,刘洪波,姜涛,等. 黄海南部野生银鲳和鮸鱼的耳石元素微化学研究[J].海洋学报,2015,37(2):36-43. [18]Rodionov S N. A sequential algorithm for testing climate regime shifts[J]. Geophysical Research Letters,2004,31(9):111-142. [19]Rodionov S N, Overland J E. Application of a sequential regime shift detection method to the Bering Sea ecosystem[J]. ICES Journal of Marine Science,2005,62(3):328-332. [20]卢明杰,刘洪波,姜涛,等. 大辽河口红狼牙鰕虎鱼耳石微化学的初步研究[J]. 海洋渔业,2015,37(4):310-317. [21]Khumbanyiwa D D, Li M M, Jiang T, et al. Unraveling habitat use of Coilia nasus, from Qiantang River of China by otolith microchemistry[J]. Regional Studies in Marine Science,2018,18(2):122-128. [22]Jiang T, Liu H B, Shen X Q, et al. Life history variations among different population of Coilia nasus along the Chinese coast inferred from otolith microchemistry[J]. Journal of the Faculty of Agriculture Kyushu University,2014,59(2):383-389. [23]姜涛,周昕期,刘洪波,等. 鄱阳湖刀鲚耳石的两种微化学特征[J].水产学报,2013,37(2):239-244. [24]Chen T T, Jiang T, Liu H, et al. Do all long supermaxilla-type estuarine tapertail anchovies (Coilia nasus Temminck et Schlegel, 1846) migrate anadromously? [J].Journal of Applied Ichthyology 2017,33(2):270-273. [25]杨健,刘洪波. 长江口崇明水域鲻鱼耳石元素微化学分析[J].中国水产科学,2010,17(4):853-857. [26]Yang J, Arai T, Liu H, et al. Reconstructing habitat use of Coilia mystus, Coilia ectenes of the Changjiang River estuary and Taihu Coilia ectenes of the Taihu Lake based on otolith environmental strontium and calcium signature[J]. Journal of Fish Biology,2006,69(4):1120-1135. [27]Tsunagawa T, Arai T. Migratory history of the freshwater goby Rhinogobius sp. CB in Japan[J]. Ecology of Freshwater Fish,2015,20(1):33-41. [28]Tsukamoto K, Watanabe S, Kuroki M, et al. Freshwater habitat use by a moray eel species, Gymnothorax polyuranodon, in Fiji shown by otolith microchemistry[J]. Environmental Biology of Fishes,2014,97(12):1377-1385. [29]Whitehead P J P, Nelson G J, Wongratana T. FAO Species Catalogue. Vol.7. Clupeoid Fishes of the World (Suborder Clupeoidei): an annotated and illustrated catalogue of the herrings, sardines, pilchards, sprats, shads, anchovies, and wolfherrings: part 2. Engraulididae[M]. Rome:FAO Fisheries Synopsis(No.125),1988:460-475. [30]林宗徳,三浦慎一,松井誠一,等. 有明海湾奥部におけるエツ0歳魚の移動[J]. 福岡水海技セ研報, 2002,12:1-6. [31]李孟孟,姜涛,陈婷婷,等. 长江安庆江段刀鲚耳石微化学及洄游生态学意义[J]. 生态学报,2017,37(8):2788-2795. [32]小松利光,安達貴浩,朝田将,等. 河川水の間断放流による強混合型塩水侵入の人工的制御[J]. 水工学論文集,1998,42:787-792. [33]田北徹,増谷英雄. エツCoilia nasusの産卵域[J]. 長崎大学水産学部研究報告,1979,46:7-10. [34]Suzuki K W, Kanematsu Y, Nakayama K, et al. Microdistribution and feeding dynamics of Coilia nasus (Engraulidae) larvae and juveniles in relation to the estuarine turbidity maximum of the macrotidal Chikugo River estuary, Ariake Sea, Japan[J]. Fisheries Oceanography,2014,23(2):157-171. [35]松井誠一,冨重信一,塚原博. エツCoilia nasus Temminck et Schlegelの生態的研究 Ⅰ.遡上群の生態に関する予報[J]. 九大農学芸誌,1986,40(4):221-228. [36]茅志昌,沈焕庭. 长江河口与瓯江河口最大浑浊带的比较研究[J]. 海洋通报,2001,20(3):8-14. [37]史英标,潘存鸿,程文龙,等.钱塘江河口段盐水入侵的时空变化及预测模型[J]. 水科学进展,2012,23(3):409-418. [38]姜涛,郑朝臣,黄洪辉,等. 基于地标点法的九龙江口和珠江口凤鲚和七丝鲚鱼类耳石形态学特征比较[J]. 南方水产科学,2018,14(6):10-16. [39]McDowall R M. Diadromy, diversity and divergence: implications for speciation processes in fishes[J]. Fish and Fisheries,2001,2(3):278-285. [40]Simanjuntak C P H, Kinoshita I, Fujita S, et al. Reproduction of the endemic engraulid, Coilia nasus, in freshwaters inside a reclamation dike of Ariake bay, western Japan[J]. Ichthyological Research,2015,62(3):374-378 [41]Yagi Y, Kinoshita I, Fujita S, et al. Importance of the upper estuary as a nursery ground for fishes in Ariake Bay, Japan[J]. Environmental Biology of Fishes,2011,91(3):337-352. [42]刘引兰,吴志强,胡茂林. 我国刀鲚研究进展[J]. 水产科学,2008,27(4):205-209. [43]吴斌,方春林,张燕萍,等. 鄱阳湖刀鲚繁殖群体生物学参数及生长特性的初步分析[J]. 水产科学,2016,35(2):142-146. [44]佟佳琦,陈锦辉,高春霞,等. 基于栖息地适应性指数的长江口刀鲚时空分布特征[J]. 上海海洋大学学报,2018,27(4):142-146.