U. Markaida, I. Méndez-Loeza, Almendra Rodríguez-Domínguez
{"title":"墨西哥坎佩切的玛雅章鱼、玛雅章鱼和渔业诱饵线中人工诱饵的捕获效率","authors":"U. Markaida, I. Méndez-Loeza, Almendra Rodríguez-Domínguez","doi":"10.7755/mfr.81.1.3","DOIUrl":null,"url":null,"abstract":"The Mayan octopus, Octopus maya, fishery from the Campeche Bank is the largest octopus fishery in the Americas and one of the largest worldwide. This fishery uses a large quantity of crabs, Brachyura, as bait, and these crustacean populations are heavily impacted. To investigate alternative lures we examined the efficacy of various artificial lures ranging from plastic crabs to jigs baited with fish during the 2012 and 2013 seasons. Artificial PVC “crab” lures showed the best yields. However, their performance was less effective than natural crab in all cases. A simple simulation showed that using these lures, harvests would decrease by 42–44% compared to using natural crab. We suggest the use of PVC crab combined with an organic compound that releases an attractive scent for octopus in further experiments. Requirements for Marine Stewardship Council certification to minimize impacts on ecosystems are a serious constraint to certifying bait fisheries (Goyert et al., 2010). Introduction of exotic baits also can carry undesirable ecological and social impacts (Gillett, 2011). Additionally, some baits such as crabs, Brachyura, may themselves be taken with baited devices (Dellinger et al., 2016), and this may in turn impact or harm other fisheries. These shortcomings are also documented in octopus fisheries using baits. For example, Japanese ghost crabs, Macrophthalmus japonicus, used as bait in traps for Octopus minor in the Republic of Korea must be imported from China (Kim et al., 2015). The Mayan octopus, Octopus maya, fishery on Mexico’s Campeche Bank with annual landings over 15,000 t is the largest octopus fishery in the Americas and one of the largest worldwide (FAO, 2018). This fishery employs lines baited with various crab species such as Florida stone crab, Menippe mercenaria; longnose spider crab, Libinia dubia; and blue crab, Callinectes spp., among others. This fishing method is considered to be sustainable regarding the octopus, as no spawning females, which stop feeding, are taken (Markaida et al., 2017). However, this fishery consumes a vast quantity of crabs, whose populations are negatively impacted, a fact noticed long ago (Solís-Ramírez, 1998; SolísRamírez et al., 1999; Carmona-Osalde and Rodríguez-Serna, 2012). Stone crab is the main bait used in the octopus fishery in Lerma and Campeche, despite its express prohibition by both stone crab and octopus regulations (DOF, 2016a,b). A local commercial fishery harvests 16 annual tons of crab claws using traps. Additionally, it is taken illegally by skin divers. Our limited data from six octopus fishermen during the 2012 and 2013 seasons estimated that each fisherman used 145 dozen (174 kg) declawed stone crabs per season (110 days) as bait. A rough estimate from a conservative figure of 700 fishermen in Lerma and Campeche would use 122 t of declawed crabs per season. This is a far larger amount than the official catch of stone crab as suggested by claw landings. If the octopus fishery employs 10,000 fishermen in all the Yucatan peninsula, bait use would be 900 t of crabs per year, which represents half of all combined crab species (mainly blue crabs) landings in the Yucatan peninsula in those years (CONAPESCA, 2017). Crabs are a particularly expensive bait that may comprise half of the total daily costs involved in the fishery (see below). Use of crabs is a current concern in the management plan of this fishery (DOF, 2014) and it might constrain its desirable future certification. Several discrete experiments have been worked out to try to substitute plastic crabs for natural crabs in this fishery. Clay pots “nummarellas” and collapsible traps have also been tested, but with no further follow up (SolísRamírez, 1998; Solís-Ramírez et al., 1999). Most experimental octopus fishing worldwide has been done using baited traps or artificial habitats (Barry et al., 2010; Rudershausen, 2013). To our knowledge, the only bait substitution experiment with fishing lines was performed in the giant Pacific octopus,","PeriodicalId":39440,"journal":{"name":"Marine Fisheries Review","volume":" ","pages":""},"PeriodicalIF":0.0000,"publicationDate":"2019-10-17","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"4","resultStr":"{\"title\":\"Capture Efficiency of Artificial Lures in Baited Lines for Mayan Octopus, Octopus maya, Fishery in Campeche, Mexico\",\"authors\":\"U. Markaida, I. Méndez-Loeza, Almendra Rodríguez-Domínguez\",\"doi\":\"10.7755/mfr.81.1.3\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"The Mayan octopus, Octopus maya, fishery from the Campeche Bank is the largest octopus fishery in the Americas and one of the largest worldwide. This fishery uses a large quantity of crabs, Brachyura, as bait, and these crustacean populations are heavily impacted. To investigate alternative lures we examined the efficacy of various artificial lures ranging from plastic crabs to jigs baited with fish during the 2012 and 2013 seasons. Artificial PVC “crab” lures showed the best yields. However, their performance was less effective than natural crab in all cases. A simple simulation showed that using these lures, harvests would decrease by 42–44% compared to using natural crab. We suggest the use of PVC crab combined with an organic compound that releases an attractive scent for octopus in further experiments. Requirements for Marine Stewardship Council certification to minimize impacts on ecosystems are a serious constraint to certifying bait fisheries (Goyert et al., 2010). Introduction of exotic baits also can carry undesirable ecological and social impacts (Gillett, 2011). Additionally, some baits such as crabs, Brachyura, may themselves be taken with baited devices (Dellinger et al., 2016), and this may in turn impact or harm other fisheries. These shortcomings are also documented in octopus fisheries using baits. For example, Japanese ghost crabs, Macrophthalmus japonicus, used as bait in traps for Octopus minor in the Republic of Korea must be imported from China (Kim et al., 2015). The Mayan octopus, Octopus maya, fishery on Mexico’s Campeche Bank with annual landings over 15,000 t is the largest octopus fishery in the Americas and one of the largest worldwide (FAO, 2018). This fishery employs lines baited with various crab species such as Florida stone crab, Menippe mercenaria; longnose spider crab, Libinia dubia; and blue crab, Callinectes spp., among others. This fishing method is considered to be sustainable regarding the octopus, as no spawning females, which stop feeding, are taken (Markaida et al., 2017). However, this fishery consumes a vast quantity of crabs, whose populations are negatively impacted, a fact noticed long ago (Solís-Ramírez, 1998; SolísRamírez et al., 1999; Carmona-Osalde and Rodríguez-Serna, 2012). Stone crab is the main bait used in the octopus fishery in Lerma and Campeche, despite its express prohibition by both stone crab and octopus regulations (DOF, 2016a,b). A local commercial fishery harvests 16 annual tons of crab claws using traps. Additionally, it is taken illegally by skin divers. Our limited data from six octopus fishermen during the 2012 and 2013 seasons estimated that each fisherman used 145 dozen (174 kg) declawed stone crabs per season (110 days) as bait. A rough estimate from a conservative figure of 700 fishermen in Lerma and Campeche would use 122 t of declawed crabs per season. This is a far larger amount than the official catch of stone crab as suggested by claw landings. If the octopus fishery employs 10,000 fishermen in all the Yucatan peninsula, bait use would be 900 t of crabs per year, which represents half of all combined crab species (mainly blue crabs) landings in the Yucatan peninsula in those years (CONAPESCA, 2017). Crabs are a particularly expensive bait that may comprise half of the total daily costs involved in the fishery (see below). Use of crabs is a current concern in the management plan of this fishery (DOF, 2014) and it might constrain its desirable future certification. Several discrete experiments have been worked out to try to substitute plastic crabs for natural crabs in this fishery. Clay pots “nummarellas” and collapsible traps have also been tested, but with no further follow up (SolísRamírez, 1998; Solís-Ramírez et al., 1999). Most experimental octopus fishing worldwide has been done using baited traps or artificial habitats (Barry et al., 2010; Rudershausen, 2013). To our knowledge, the only bait substitution experiment with fishing lines was performed in the giant Pacific octopus,\",\"PeriodicalId\":39440,\"journal\":{\"name\":\"Marine Fisheries Review\",\"volume\":\" \",\"pages\":\"\"},\"PeriodicalIF\":0.0000,\"publicationDate\":\"2019-10-17\",\"publicationTypes\":\"Journal Article\",\"fieldsOfStudy\":null,\"isOpenAccess\":false,\"openAccessPdf\":\"\",\"citationCount\":\"4\",\"resultStr\":null,\"platform\":\"Semanticscholar\",\"paperid\":null,\"PeriodicalName\":\"Marine Fisheries Review\",\"FirstCategoryId\":\"1085\",\"ListUrlMain\":\"https://doi.org/10.7755/mfr.81.1.3\",\"RegionNum\":0,\"RegionCategory\":null,\"ArticlePicture\":[],\"TitleCN\":null,\"AbstractTextCN\":null,\"PMCID\":null,\"EPubDate\":\"\",\"PubModel\":\"\",\"JCR\":\"Q2\",\"JCRName\":\"Agricultural and Biological Sciences\",\"Score\":null,\"Total\":0}","platform":"Semanticscholar","paperid":null,"PeriodicalName":"Marine Fisheries Review","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.7755/mfr.81.1.3","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q2","JCRName":"Agricultural and Biological Sciences","Score":null,"Total":0}
引用次数: 4
摘要
坎佩切河岸边的玛雅章鱼渔场是美洲最大的章鱼渔场,也是全球最大的章鱼渔场之一。这种渔业使用大量的短尾蟹作为诱饵,这些甲壳类动物的种群受到严重影响。为了研究替代诱饵,我们在2012年和2013年期间研究了各种人工诱饵的效果,包括塑料螃蟹和鱼饵。人工聚氯乙烯“蟹”饵产量最佳。然而,在所有情况下,它们的表现都不如天然螃蟹。一个简单的模拟表明,与使用天然螃蟹相比,使用这些诱饵的收获将减少42-44%。我们建议在进一步的实验中使用PVC螃蟹和一种有机化合物,这种化合物可以释放出吸引章鱼的气味。要求海洋管理委员会认证以尽量减少对生态系统的影响是对诱饵渔业认证的严重限制(Goyert等,2010)。引进外来饵料也会带来不良的生态和社会影响(Gillett, 2011)。此外,一些饵料,如蟹,短尾蟹,本身可能使用诱饵装置(Dellinger et al., 2016),这可能反过来影响或损害其他渔业。这些缺点在使用鱼饵的章鱼渔业中也有记载。例如,在韩国用作小章鱼陷阱诱饵的日本鬼蟹(Macrophthalmus japonicus)必须从中国进口(Kim et al., 2015)。墨西哥坎佩切河岸边的玛雅章鱼渔业年捕捞量超过1.5万吨,是美洲最大的章鱼渔业,也是世界上最大的章鱼渔业之一(粮农组织,2018年)。这个渔场使用鱼线,用各种螃蟹作诱饵,如佛罗里达石蟹,曼尼佩;长鼻蜘蛛蟹,产自利比亚;以及蓝蟹(Callinectes spp.)等。对于章鱼来说,这种捕捞方法被认为是可持续的,因为没有产卵的雌性章鱼会停止进食(Markaida et al., 2017)。然而,这种渔业消耗了大量的螃蟹,螃蟹的数量受到了负面影响,这是一个很久以前就注意到的事实(Solís-Ramírez, 1998;SolísRamírez et al., 1999;Carmona-Osalde and Rodríguez-Serna, 2012)。石蟹是Lerma和Campeche地区章鱼捕捞的主要饵料,尽管石蟹和章鱼法规都明确禁止使用石蟹(DOF, 2016a,b)。当地一家商业渔场利用捕蟹器每年捕获16吨蟹爪。此外,它是非法的皮肤潜水员。我们在2012年和2013年季节从六名章鱼渔民那里获得的有限数据估计,每个渔民每个季节(110天)使用145打(174公斤)有爪石蟹作为诱饵。保守估计,在勒玛和坎佩切州,700名渔民每个季节将使用122吨爪蟹。这远远超过了石蟹爪着地的官方捕获量。如果整个尤卡坦半岛的章鱼渔业雇佣了10,000名渔民,那么每年的诱饵使用量将为900吨螃蟹,这代表了那些年在尤卡坦半岛登陆的所有螃蟹品种(主要是蓝蟹)的一半(CONAPESCA, 2017)。螃蟹是一种特别昂贵的诱饵,可能占渔业日常总成本的一半(见下文)。螃蟹的使用是该渔业管理计划中当前关注的问题(DOF, 2014),它可能会限制其理想的未来认证。在这个渔场中,已经进行了几项独立的实验,试图用塑料螃蟹代替天然螃蟹。粘土罐“nummarellas”和可折叠陷阱也进行了测试,但没有进一步的后续工作(SolísRamírez, 1998;Solís-Ramírez et al., 1999)。世界上大多数章鱼的实验捕捞都是使用带饵的陷阱或人工栖息地进行的(Barry et al., 2010;Rudershausen, 2013)。据我们所知,唯一一次用鱼线代替诱饵的实验是在太平洋巨型章鱼身上进行的,
Capture Efficiency of Artificial Lures in Baited Lines for Mayan Octopus, Octopus maya, Fishery in Campeche, Mexico
The Mayan octopus, Octopus maya, fishery from the Campeche Bank is the largest octopus fishery in the Americas and one of the largest worldwide. This fishery uses a large quantity of crabs, Brachyura, as bait, and these crustacean populations are heavily impacted. To investigate alternative lures we examined the efficacy of various artificial lures ranging from plastic crabs to jigs baited with fish during the 2012 and 2013 seasons. Artificial PVC “crab” lures showed the best yields. However, their performance was less effective than natural crab in all cases. A simple simulation showed that using these lures, harvests would decrease by 42–44% compared to using natural crab. We suggest the use of PVC crab combined with an organic compound that releases an attractive scent for octopus in further experiments. Requirements for Marine Stewardship Council certification to minimize impacts on ecosystems are a serious constraint to certifying bait fisheries (Goyert et al., 2010). Introduction of exotic baits also can carry undesirable ecological and social impacts (Gillett, 2011). Additionally, some baits such as crabs, Brachyura, may themselves be taken with baited devices (Dellinger et al., 2016), and this may in turn impact or harm other fisheries. These shortcomings are also documented in octopus fisheries using baits. For example, Japanese ghost crabs, Macrophthalmus japonicus, used as bait in traps for Octopus minor in the Republic of Korea must be imported from China (Kim et al., 2015). The Mayan octopus, Octopus maya, fishery on Mexico’s Campeche Bank with annual landings over 15,000 t is the largest octopus fishery in the Americas and one of the largest worldwide (FAO, 2018). This fishery employs lines baited with various crab species such as Florida stone crab, Menippe mercenaria; longnose spider crab, Libinia dubia; and blue crab, Callinectes spp., among others. This fishing method is considered to be sustainable regarding the octopus, as no spawning females, which stop feeding, are taken (Markaida et al., 2017). However, this fishery consumes a vast quantity of crabs, whose populations are negatively impacted, a fact noticed long ago (Solís-Ramírez, 1998; SolísRamírez et al., 1999; Carmona-Osalde and Rodríguez-Serna, 2012). Stone crab is the main bait used in the octopus fishery in Lerma and Campeche, despite its express prohibition by both stone crab and octopus regulations (DOF, 2016a,b). A local commercial fishery harvests 16 annual tons of crab claws using traps. Additionally, it is taken illegally by skin divers. Our limited data from six octopus fishermen during the 2012 and 2013 seasons estimated that each fisherman used 145 dozen (174 kg) declawed stone crabs per season (110 days) as bait. A rough estimate from a conservative figure of 700 fishermen in Lerma and Campeche would use 122 t of declawed crabs per season. This is a far larger amount than the official catch of stone crab as suggested by claw landings. If the octopus fishery employs 10,000 fishermen in all the Yucatan peninsula, bait use would be 900 t of crabs per year, which represents half of all combined crab species (mainly blue crabs) landings in the Yucatan peninsula in those years (CONAPESCA, 2017). Crabs are a particularly expensive bait that may comprise half of the total daily costs involved in the fishery (see below). Use of crabs is a current concern in the management plan of this fishery (DOF, 2014) and it might constrain its desirable future certification. Several discrete experiments have been worked out to try to substitute plastic crabs for natural crabs in this fishery. Clay pots “nummarellas” and collapsible traps have also been tested, but with no further follow up (SolísRamírez, 1998; Solís-Ramírez et al., 1999). Most experimental octopus fishing worldwide has been done using baited traps or artificial habitats (Barry et al., 2010; Rudershausen, 2013). To our knowledge, the only bait substitution experiment with fishing lines was performed in the giant Pacific octopus,