Environmental factors affecting Edwardsiella ictaluri‐induced mortality of riverine ayu, Plecoglossus altivelis (Temminck & Schlegel)

We analysed the predisposing factors for Edwardsiella ictaluri infection in the riverine ayu Plecoglossus altivelis on the basis of environmental and epidemiological data obtained in a tributary to and the lower reaches of the Tama River, Japan, in July and August 2011–2015. Mortality of ayu due to...

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Veröffentlicht in:Journal of fish diseases 2021-08, Vol.44 (8), p.1065-1074
Hauptverfasser: Takeuchi, Hisato, Hiratsuka, Motoyuki, Hori, Kazutomo, Oinuma, Hiroki, Umino, Yoshiyuki, Nakano, Daiki, Iwadare, Mayu, Tomono, Ryuji, Imai, Toshihiro, Mashiko, Hirohito, Namba, Aki, Takase, Tomohiro, Shimizu, Sonoko, Nakai, Toshihiro, Mano, Nobuhiro
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container_end_page 1074
container_issue 8
container_start_page 1065
container_title Journal of fish diseases
container_volume 44
creator Takeuchi, Hisato
Hiratsuka, Motoyuki
Hori, Kazutomo
Oinuma, Hiroki
Umino, Yoshiyuki
Nakano, Daiki
Iwadare, Mayu
Tomono, Ryuji
Imai, Toshihiro
Mashiko, Hirohito
Namba, Aki
Takase, Tomohiro
Shimizu, Sonoko
Nakai, Toshihiro
Mano, Nobuhiro
description We analysed the predisposing factors for Edwardsiella ictaluri infection in the riverine ayu Plecoglossus altivelis on the basis of environmental and epidemiological data obtained in a tributary to and the lower reaches of the Tama River, Japan, in July and August 2011–2015. Mortality of ayu due to E. ictaluri infection was observed only in the tributary in August 2012 and 2013; both periods were unusually hot. During these mortality events, daily average water temperatures rose approximately 3–4°C over 4–8 days, reaching the optimum temperature for E. ictaluri infection (>25°C) and approaching the upper tolerable limit for ayu (30°C). Diurnal water temperature ranges (DWTRs) in the tributary during the mortality events exceeded 6°C, which was 1–2°C greater than in the lower reaches. Experimental infection of ayu with E. ictaluri resulted in higher mortality when exposed to 6°C DWTR than to 4°C DWTR. Furthermore, water levels in the tributary were generally low in August 2012 and 2013 because of low rainfall. From these results, we conclude that unusually high‐water temperatures combined with high DWTRs and low water levels drove riverine ayu mortality from E. ictaluri infection.
doi_str_mv 10.1111/jfd.13368
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Mortality of ayu due to E. ictaluri infection was observed only in the tributary in August 2012 and 2013; both periods were unusually hot. During these mortality events, daily average water temperatures rose approximately 3–4°C over 4–8 days, reaching the optimum temperature for E. ictaluri infection (&gt;25°C) and approaching the upper tolerable limit for ayu (30°C). Diurnal water temperature ranges (DWTRs) in the tributary during the mortality events exceeded 6°C, which was 1–2°C greater than in the lower reaches. Experimental infection of ayu with E. ictaluri resulted in higher mortality when exposed to 6°C DWTR than to 4°C DWTR. Furthermore, water levels in the tributary were generally low in August 2012 and 2013 because of low rainfall. 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Mortality of ayu due to E. ictaluri infection was observed only in the tributary in August 2012 and 2013; both periods were unusually hot. During these mortality events, daily average water temperatures rose approximately 3–4°C over 4–8 days, reaching the optimum temperature for E. ictaluri infection (&gt;25°C) and approaching the upper tolerable limit for ayu (30°C). Diurnal water temperature ranges (DWTRs) in the tributary during the mortality events exceeded 6°C, which was 1–2°C greater than in the lower reaches. Experimental infection of ayu with E. ictaluri resulted in higher mortality when exposed to 6°C DWTR than to 4°C DWTR. Furthermore, water levels in the tributary were generally low in August 2012 and 2013 because of low rainfall. 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Schlegel)</atitle><jtitle>Journal of fish diseases</jtitle><addtitle>J Fish Dis</addtitle><date>2021-08</date><risdate>2021</risdate><volume>44</volume><issue>8</issue><spage>1065</spage><epage>1074</epage><pages>1065-1074</pages><issn>0140-7775</issn><eissn>1365-2761</eissn><abstract>We analysed the predisposing factors for Edwardsiella ictaluri infection in the riverine ayu Plecoglossus altivelis on the basis of environmental and epidemiological data obtained in a tributary to and the lower reaches of the Tama River, Japan, in July and August 2011–2015. Mortality of ayu due to E. ictaluri infection was observed only in the tributary in August 2012 and 2013; both periods were unusually hot. During these mortality events, daily average water temperatures rose approximately 3–4°C over 4–8 days, reaching the optimum temperature for E. ictaluri infection (&gt;25°C) and approaching the upper tolerable limit for ayu (30°C). Diurnal water temperature ranges (DWTRs) in the tributary during the mortality events exceeded 6°C, which was 1–2°C greater than in the lower reaches. Experimental infection of ayu with E. ictaluri resulted in higher mortality when exposed to 6°C DWTR than to 4°C DWTR. Furthermore, water levels in the tributary were generally low in August 2012 and 2013 because of low rainfall. From these results, we conclude that unusually high‐water temperatures combined with high DWTRs and low water levels drove riverine ayu mortality from E. ictaluri infection.</abstract><cop>England</cop><pub>Blackwell Publishing Ltd</pub><pmid>33755230</pmid><doi>10.1111/jfd.13368</doi><tpages>10</tpages><orcidid>https://orcid.org/0000-0003-4658-9570</orcidid></addata></record>
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source Wiley Online Library Journals Frontfile Complete
subjects ayu
Edwardsiella ictaluri
Edwardsiella ictaluri infection
Environmental factors
Epidemiology
Experimental infection
Infections
Mortality
Plecoglossus altivelis
Rain
Rainfall
Temperature effects
Tributaries
Water levels
Water temperature
title Environmental factors affecting Edwardsiella ictaluri‐induced mortality of riverine ayu, Plecoglossus altivelis (Temminck & Schlegel)
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