Studies on Improvement of Seed Production Techniques in Salmonids and Osmerids
S. Mizuno
{"title":"Studies on Improvement of Seed Production Techniques in Salmonids and Osmerids","authors":"S. Mizuno","doi":"10.5047/ABSM.2012.00504.0103","DOIUrl":null,"url":null,"abstract":"Anadromous salmonids and osmerids are artificially propagated in Japan by release of their seeds. However, there are many unsolved problems in the techniques of their propagation. In the present monograph, studies on the improvement of seed production techniques in 4 fishes (masu salmon Oncorhynchus masou, chum salmon O. keta, shishamo smelt Spirinchus lanceolatus and Japanese smelt Hypomesus nipponensis) were outlined. Techniques to evaluate dorsal fin pigmentation during smoltification as an external seed quality, and to improve seed quality of hatchery-reared fish, and the discovery of metabolic problems in hatchery-reared fish were described in yearling masu salmon. In underyearling masu salmon, techniques to evaluate nutritional conditions using kidney melano-macrophage density was developed, and applied to the evaluation of the nutritional condition in hatchery-reared fish after release. In chum salmon fry, the development of techniques to monitor the physical condition and to find its appropriate culture conditions was reviewed. In egg cultures of shishamo and Japanese smelt, techniques to eliminate egg adhesiveness with treatments of kaolin or scallop shell powder suspension were established in order to improve hatching rates. In addition, the appropriate embryogenetic stage for the release of shishamo smelt embryos was demonstrated. Consequently, this monograph reveals that these techniques contribute directly to the development of artificial propagation in some salmonids and osmerids. 1. General introduction Anadromous salmonids and osmerids including masu salmon Oncorhynchus masou, chum salmon O. keta, shishamo smelt Spirinchus lanceolatus and Japanese smelt Hypomesus nipponensis are important species for coastal and freshwater commercial fisheries in Hokkaido, the northern-most prefecture in Japan. These fish are not always abundant under natural reproduction systems (Nagata and Kaeriyama 2004; Torao 2005a, b; Miyakoshi 2006). Therefore, these fish are artificially propagated by releasing their seeds in order to increase their stock in various places in Hokkaido (Kusuda and Teranishi 1996; Kaeriyama 1999; Torisawa 1999). Masu salmon, which inhabit both Pacific Ocean and the Japan Sea coasts of Hokkaido, spawn in upstream regions in autumn and hatch the winter of the same year (Kato 1991). The fish are separated into two types: 104 S. Mizuno / Aqua-BioSci. Monogr. 5: 103–143, 2012 doi:10.5047/absm.2012.00504.0103 © 2012 TERRAPUB, Tokyo. All rights reserved. words, masu salmon propagation costs more money compared to chum salmon propagation. It is essential for the sustainable artificial propagation of masu salmon to reduce the cost of seed production by increasing the survival rate of seed. Hatchery masu salmon are released in two ways. One is called the smolt release method where yearling (1+) smoltified juveniles are released into downstream regions in spring, and the other is called the spring juvenile release method, where underyearling (0+) juveniles are released into upstream regions in spring (Mayama 1992). One of the keys to increasing survival rate of seed is stocking hatchery juveniles with high seed qualities determined from ethological, physiological and biochemical characteristics. However, seed quality of hatchery juveniles has not been perfectly evaluated in masu salmon. In addition, there has been no attempt to improve the seed quality of hatchery juveniles. Chum salmon, which inhabit the whole region of Hokkaido, hatch in rivers in winter, and migrate to the ocean the following spring. All of the fish are anadromous. After 2 to 6 years of marine life, adults return to spawn in their natal rivers in autumn (Salo 1991). In the program, 0+ fry, which were produced in hatcheries in the same way as the masu salmon, are released into the river in spring (Kobayashi 1980). However, the increased stock due to the propagationprogram has caused downsizing and aging (Kaeriyama and Edpaline 2004). This phenomenon is believed to be due to a population density-dependent effect: the growth of chum salmon fry is restrained by carrying capacity, such as the amount of food or habitat size, in the North Pacific (Kaeriyama et al. 2007). Hatchery fish have to coexist with wild fish in a narrow carrying capacity. Therefore, biological interactions between hatchery populations and wild populations are being studied (Kaeriyama and Edpaline 2004). Hilborn (1992) has warned that the excessive release of hatchery fish decreases the genetic diversity of Pacific salmon, including chum salmon. Accordingly, artificial propagation and the preservation of wild populations must be jointly considered in order to preserve the natural balance. Kaeriyama (2002) was concerned about the infection of wild fish by hatchery fish diseases. Considering this background, the reliable production of hatchery fry with good physical conditions is more important than an increased number of released hatchery fry for the sustainable artificial propagation of chum salmon. Chum salmon fry are intensively cultured in high density conditions in hatchery ponds. In general, intensively cultured fish are commonly under high physiological stress resulting from deteriorated rearing conditions (Patinõ et al. 1986; Papoutsoglou et al. 1987). On the other hand, it has been impossible to monitor the physical conditions of hatchery fry cultured in high density conditions, and practical environmental conditions for the culture of fry in good physical conditions have not yet been found. Shishamo smelt migrate to their natal river on the Pacific Ocean side of Hokkaido in early winter to spawn (Hikita 1930, 1958). Adults spawn 1.4 mm sized eggs in freshwater environments about 3 to 9 km upstream from the estuary (Ito 1959, 1963, 1964; Okada and Sasaki 1960; Okada et al. 1975, 1976; Omi 1978b). The larvae migrate to the estuary immediately after hatching carried by the snow-melt water during the following spring, and mature after 2 or 3 years of life in the ocean (Omi 1978a). All of the fish are anadromous (Miyaji et al. 1976). On the other hand, Japanese smelt, which are distributed around the whole of Hokkaido, consist of anadromous and lake-resident types (Hamada 1961; Katayama et al . 1999). Anadromous-type fish migrate to their natal stream and spawn 0.8 mm sized eggs in shallow streams from April to June (Shiraishi 1961; Torisawa 1999). The general lifespan of the fish is 1 to 2 years (Utoh and Sakazaki 1983, 1984, 1987; Torisawa 1999). For the artificial propagation of shishamo and Japanese smelt, larvae, obtained by artificial insemination, are released into the rivers or lakes through the drainage of hatchery waters (Iwai and Osama 1986; Kusuda and Teranishi 1996; Izuka 2003; Kitsukawa et al. 2003). However, the efficiency of the propagation has not yet been accurately evaluated. It is necessary to first produce a lot of seed to perform a pilot release, in order to establish effective seed-release methods and to elucidate the effects of releasing hatchery seed. Some shishamo and Japanese smelt hatcheries intensively culture eggs using upwelling flow-type acrylic and cylindrical jar incubators (Kusuda and Teranishi 1996; Kitsukawa et al. 2006). However, it was found that eggs cultured in the jar incubators showed low hatching rates (Takeda et al. 2002). In a few shishamo smelt hatcheries, eyed-stage embryos are released into the river (Mizuno et al. 2004b, 2005) before they hatch. However, the most appropriate time for releasing eyedstage embryos into the river is unknown. In this monograph, I review research performed on the improvement of seed production techniques in salmonids and osmerids, with the aim to solve some of the problems mentioned above. In Section 2, three approaches to evaluating and improving the seed quality of hatchery masu salmon smolt are described. Section 3 reviews 2 studies on the development and application of techniques evaluating seed quality in hatchery masu salmon parr for spring juvenile release. Section 4 deals with 2 studies dealing with the establishment of techniques to monitor physical conditions and the elucidation of appropriate culture conditions in chum salmon fry. In Section 5, three attempts to develop techniques to improve survival rate in artificial propagation of shishamo and Japanese smelt were deS. Mizuno / Aqua-BioSci. Monogr. 5: 103–143, 2012 105 doi:10.5047/absm.2012.00504.0103 © 2012 TERRAPUB, Tokyo. All rights reserved. scribed. The final chapter describes the implications and perspective studies of the improvement of seed production techniques in salmonids and osmerids. 2. Evaluation and improvement of seed qualities in 1+ hatchery masu salmon smolts","PeriodicalId":186355,"journal":{"name":"Aqua-bioscience Monographs","volume":"16 1","pages":"0"},"PeriodicalIF":0.0000,"publicationDate":"2012-12-21","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"2","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Aqua-bioscience Monographs","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.5047/ABSM.2012.00504.0103","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 2
Abstract
Anadromous salmonids and osmerids are artificially propagated in Japan by release of their seeds. However, there are many unsolved problems in the techniques of their propagation. In the present monograph, studies on the improvement of seed production techniques in 4 fishes (masu salmon Oncorhynchus masou, chum salmon O. keta, shishamo smelt Spirinchus lanceolatus and Japanese smelt Hypomesus nipponensis) were outlined. Techniques to evaluate dorsal fin pigmentation during smoltification as an external seed quality, and to improve seed quality of hatchery-reared fish, and the discovery of metabolic problems in hatchery-reared fish were described in yearling masu salmon. In underyearling masu salmon, techniques to evaluate nutritional conditions using kidney melano-macrophage density was developed, and applied to the evaluation of the nutritional condition in hatchery-reared fish after release. In chum salmon fry, the development of techniques to monitor the physical condition and to find its appropriate culture conditions was reviewed. In egg cultures of shishamo and Japanese smelt, techniques to eliminate egg adhesiveness with treatments of kaolin or scallop shell powder suspension were established in order to improve hatching rates. In addition, the appropriate embryogenetic stage for the release of shishamo smelt embryos was demonstrated. Consequently, this monograph reveals that these techniques contribute directly to the development of artificial propagation in some salmonids and osmerids. 1. General introduction Anadromous salmonids and osmerids including masu salmon Oncorhynchus masou, chum salmon O. keta, shishamo smelt Spirinchus lanceolatus and Japanese smelt Hypomesus nipponensis are important species for coastal and freshwater commercial fisheries in Hokkaido, the northern-most prefecture in Japan. These fish are not always abundant under natural reproduction systems (Nagata and Kaeriyama 2004; Torao 2005a, b; Miyakoshi 2006). Therefore, these fish are artificially propagated by releasing their seeds in order to increase their stock in various places in Hokkaido (Kusuda and Teranishi 1996; Kaeriyama 1999; Torisawa 1999). Masu salmon, which inhabit both Pacific Ocean and the Japan Sea coasts of Hokkaido, spawn in upstream regions in autumn and hatch the winter of the same year (Kato 1991). The fish are separated into two types: 104 S. Mizuno / Aqua-BioSci. Monogr. 5: 103–143, 2012 doi:10.5047/absm.2012.00504.0103 © 2012 TERRAPUB, Tokyo. All rights reserved. words, masu salmon propagation costs more money compared to chum salmon propagation. It is essential for the sustainable artificial propagation of masu salmon to reduce the cost of seed production by increasing the survival rate of seed. Hatchery masu salmon are released in two ways. One is called the smolt release method where yearling (1+) smoltified juveniles are released into downstream regions in spring, and the other is called the spring juvenile release method, where underyearling (0+) juveniles are released into upstream regions in spring (Mayama 1992). One of the keys to increasing survival rate of seed is stocking hatchery juveniles with high seed qualities determined from ethological, physiological and biochemical characteristics. However, seed quality of hatchery juveniles has not been perfectly evaluated in masu salmon. In addition, there has been no attempt to improve the seed quality of hatchery juveniles. Chum salmon, which inhabit the whole region of Hokkaido, hatch in rivers in winter, and migrate to the ocean the following spring. All of the fish are anadromous. After 2 to 6 years of marine life, adults return to spawn in their natal rivers in autumn (Salo 1991). In the program, 0+ fry, which were produced in hatcheries in the same way as the masu salmon, are released into the river in spring (Kobayashi 1980). However, the increased stock due to the propagationprogram has caused downsizing and aging (Kaeriyama and Edpaline 2004). This phenomenon is believed to be due to a population density-dependent effect: the growth of chum salmon fry is restrained by carrying capacity, such as the amount of food or habitat size, in the North Pacific (Kaeriyama et al. 2007). Hatchery fish have to coexist with wild fish in a narrow carrying capacity. Therefore, biological interactions between hatchery populations and wild populations are being studied (Kaeriyama and Edpaline 2004). Hilborn (1992) has warned that the excessive release of hatchery fish decreases the genetic diversity of Pacific salmon, including chum salmon. Accordingly, artificial propagation and the preservation of wild populations must be jointly considered in order to preserve the natural balance. Kaeriyama (2002) was concerned about the infection of wild fish by hatchery fish diseases. Considering this background, the reliable production of hatchery fry with good physical conditions is more important than an increased number of released hatchery fry for the sustainable artificial propagation of chum salmon. Chum salmon fry are intensively cultured in high density conditions in hatchery ponds. In general, intensively cultured fish are commonly under high physiological stress resulting from deteriorated rearing conditions (Patinõ et al. 1986; Papoutsoglou et al. 1987). On the other hand, it has been impossible to monitor the physical conditions of hatchery fry cultured in high density conditions, and practical environmental conditions for the culture of fry in good physical conditions have not yet been found. Shishamo smelt migrate to their natal river on the Pacific Ocean side of Hokkaido in early winter to spawn (Hikita 1930, 1958). Adults spawn 1.4 mm sized eggs in freshwater environments about 3 to 9 km upstream from the estuary (Ito 1959, 1963, 1964; Okada and Sasaki 1960; Okada et al. 1975, 1976; Omi 1978b). The larvae migrate to the estuary immediately after hatching carried by the snow-melt water during the following spring, and mature after 2 or 3 years of life in the ocean (Omi 1978a). All of the fish are anadromous (Miyaji et al. 1976). On the other hand, Japanese smelt, which are distributed around the whole of Hokkaido, consist of anadromous and lake-resident types (Hamada 1961; Katayama et al . 1999). Anadromous-type fish migrate to their natal stream and spawn 0.8 mm sized eggs in shallow streams from April to June (Shiraishi 1961; Torisawa 1999). The general lifespan of the fish is 1 to 2 years (Utoh and Sakazaki 1983, 1984, 1987; Torisawa 1999). For the artificial propagation of shishamo and Japanese smelt, larvae, obtained by artificial insemination, are released into the rivers or lakes through the drainage of hatchery waters (Iwai and Osama 1986; Kusuda and Teranishi 1996; Izuka 2003; Kitsukawa et al. 2003). However, the efficiency of the propagation has not yet been accurately evaluated. It is necessary to first produce a lot of seed to perform a pilot release, in order to establish effective seed-release methods and to elucidate the effects of releasing hatchery seed. Some shishamo and Japanese smelt hatcheries intensively culture eggs using upwelling flow-type acrylic and cylindrical jar incubators (Kusuda and Teranishi 1996; Kitsukawa et al. 2006). However, it was found that eggs cultured in the jar incubators showed low hatching rates (Takeda et al. 2002). In a few shishamo smelt hatcheries, eyed-stage embryos are released into the river (Mizuno et al. 2004b, 2005) before they hatch. However, the most appropriate time for releasing eyedstage embryos into the river is unknown. In this monograph, I review research performed on the improvement of seed production techniques in salmonids and osmerids, with the aim to solve some of the problems mentioned above. In Section 2, three approaches to evaluating and improving the seed quality of hatchery masu salmon smolt are described. Section 3 reviews 2 studies on the development and application of techniques evaluating seed quality in hatchery masu salmon parr for spring juvenile release. Section 4 deals with 2 studies dealing with the establishment of techniques to monitor physical conditions and the elucidation of appropriate culture conditions in chum salmon fry. In Section 5, three attempts to develop techniques to improve survival rate in artificial propagation of shishamo and Japanese smelt were deS. Mizuno / Aqua-BioSci. Monogr. 5: 103–143, 2012 105 doi:10.5047/absm.2012.00504.0103 © 2012 TERRAPUB, Tokyo. All rights reserved. scribed. The final chapter describes the implications and perspective studies of the improvement of seed production techniques in salmonids and osmerids. 2. Evaluation and improvement of seed qualities in 1+ hatchery masu salmon smolts
鲑科和尾鱼科制种技术的改进研究
在日本,产卵鲑科和尾鱼科通过释放种子进行人工繁殖。然而,在它们的传播技术方面还存在许多尚未解决的问题。本文综述了4种鱼类(masu salmon Oncorhynchus masou, chumsalmon O. keta, shishamo Spirinchus lanceolatus, Japanese Hypomesus nipponensis)制种技术的改进研究。本文介绍了以马苏鲑鱼为例,评价孵化过程中背鳍色素沉着作为外部种子质量的技术,以及提高孵育鱼类种子质量的技术,以及孵育鱼类代谢问题的发现。以马苏鲑鱼为研究对象,研究了利用肾脏黑素-巨噬细胞密度评估营养状况的技术,并将其应用于孵化场放生后的营养状况评估。综述了大马哈鱼鱼苗生理状态监测和适宜养殖条件的研究进展。研究了用高岭土或扇贝粉悬浮液处理水烟蛋和日本臭蛋的方法,以提高鸡蛋的孵化率。此外,还论证了水烟香精胚释放的适宜胚胎发生阶段。因此,本专著揭示了这些技术直接有助于人工繁殖的发展,在一些鲑鱼和半尾鱼。1. 鲤科鲑鱼和鲭鱼是日本北海道沿海和淡水商业渔业的重要物种,其中包括马苏鲑、Oncorhynchus masou、O. keta、shishamo smelchus lanceolatus和日本马苏鲑。这些鱼在自然繁殖系统中并不总是丰富的(Nagata和Kaeriyama 2004;Torao 2005a, b;Miyakoshi 2006)。因此,这些鱼通过释放种子进行人工繁殖,以增加北海道各地的鱼类数量(Kusuda和Teranishi 1996;Kaeriyama 1999;Torisawa 1999)。马苏鲑鱼栖息在太平洋和北海道的日本海沿岸,秋季在上游产卵,同年冬季孵化(加藤1991)。这些鱼被分为两类:104 S. Mizuno / Aqua-BioSci。学报,5:103-143,2012 doi:10.5047/absm.2012.00504.0103©2012 TERRAPUB, Tokyo。版权所有。换句话说,马苏鲑鱼的繁殖成本比鲑鱼的繁殖成本更高。通过提高种子成活率来降低制种成本,是实现马苏鲑鱼可持续人工繁殖的关键。孵化场马苏鲑鱼有两种释放方式。一种是春放生法,将1+龄幼鱼放生到下游地区,另一种是春放生法,将0+龄幼鱼放生到上游地区(Mayama 1992)。提高种子成活率的关键之一是放养从行为学、生理生化等方面决定种子品质的孵化幼鱼。然而,马苏鲑鱼孵育幼鱼的种子质量还没有得到很好的评价。此外,还没有尝试提高孵化幼鱼的种子质量。鲑鱼栖息在北海道的整个地区,冬天在河流中孵化,第二年春天迁徙到海洋。所有的鱼都是溯河产卵的。经过2至6年的海洋生活,成鱼在秋天回到它们的出生河流产卵(Salo 1991)。在该计划中,在孵化场以与马苏鲑鱼相同的方式生产的0+鱼苗在春天被释放到河中(Kobayashi 1980)。然而,由于繁殖计划而增加的库存导致了缩小规模和老化(Kaeriyama和Edpaline 2004)。这种现象被认为是由于种群密度依赖效应:北太平洋的鲑鱼鱼苗的生长受到承载能力的限制,例如食物量或栖息地大小(Kaeriyama et al. 2007)。孵化场鱼类必须与野生鱼类共存,承受能力很窄。因此,正在研究孵化场种群和野生种群之间的生物相互作用(Kaeriyama和Edpaline 2004)。Hilborn(1992)警告说,过度放养孵化场鱼类会减少太平洋鲑鱼的遗传多样性,包括鲑鱼。因此,为了保持自然平衡,必须将人工繁殖和野生种群的保护结合起来考虑。Kaeriyama(2002)关注野生鱼类受孵化场鱼类疾病感染的问题。 考虑到这一背景,对于大马哈鱼的可持续人工繁殖而言,可靠的鱼苗生产和良好的物理条件比增加鱼苗放生数量更为重要。大马哈鱼鱼苗是在孵化池的高密度条件下集约养殖的。一般来说,集约化养殖的鱼类通常由于饲养条件恶化而处于高度生理应激状态(Patinõ et al. 1986;Papoutsoglou et al. 1987)。另一方面,在高密度条件下养殖的孵化场鱼苗的物理条件一直无法监测,在良好的物理条件下养殖鱼苗的实际环境条件尚未找到。初冬时,盐摩鱼洄游到北海道太平洋一侧的出生河产卵(Hikita 1930, 1958)。成虫在河口上游约3至9公里的淡水环境中产卵1.4毫米大小的卵(Ito 1959, 1963, 1964;冈田和佐佐木1960;Okada et al. 1975,1976;尾身茂1978 b)。幼虫孵化后,在次年春季由融雪水携带立即迁移到河口,在海洋中生活2 - 3年后成熟(Omi 1978a)。所有的鱼都是溯河产卵的(Miyaji et al. 1976)。另一方面,分布在整个北海道的日本胡科鱼分为溯河型和湖栖型(Hamada 1961;Katayama等人。1999)。溯河型鱼从4月到6月洄游到它们的出生溪流,在浅水溪流中产卵0.8毫米大小的卵(Shiraishi 1961;Torisawa 1999)。鱼的一般寿命为1至2年(Utoh和Sakazaki 1983, 1984, 1987;Torisawa 1999)。为了人工繁殖水烟和日本香鱼,通过人工授精获得的幼虫通过孵化场水域的排水被释放到河流或湖泊中(Iwai和Osama 1986;久田和寺西1996;Izuka 2003;Kitsukawa et al. 2003)。然而,其传播效率尚未得到准确的评价。为了建立有效的放种方法,阐明放种效果,有必要先大量生产种子进行中试放种。一些shishamo和日本的熔体孵化场使用上升流型丙烯酸和圆柱形罐孵化箱集中培养鸡蛋(Kusuda和Teranishi 1996;Kitsukawa et al. 2006)。然而,发现在罐式孵卵器中培养的卵孵化率较低(Takeda et al. 2002)。在一些shishamo熔体孵化场,眼期胚胎在孵化前被释放到河中(Mizuno et al. 2004b, 2005)。然而,将眼期胚胎放入河里的最佳时间尚不清楚。在本专著中,我回顾了在鲑鱼和锇鱼种子生产技术改进方面所进行的研究,旨在解决上述一些问题。在第二节中,介绍了三种评价和提高马苏鲑鱼孵卵种子质量的方法。第三部分综述了马苏鲑鱼春季放生种子质量评价技术的开发与应用。第4节涉及两项研究,涉及建立监测物理条件的技术和阐明鲑鱼鱼苗的适当培养条件。在第5节中,尝试开发三种技术来提高鱼和日本鱼的人工繁殖成活率,分别是deS、Mizuno / Aqua-BioSci。学报,5:103-143,2012 105 doi:10.5047/absm.2012.00504.0103©2012 TERRAPUB,东京。版权所有。刻。最后一章描述了鲑鱼和半尾鱼种子生产技术改进的意义和前景研究。2. 1+孵化场马苏鲑鱼幼鱼种子品质评价与改良
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