Herbivory impacts Vallisneria americana recovery in the lower St. Johns River, Florida

IF 1.2 4区 生物学 Q3 MARINE & FRESHWATER BIOLOGY Journal of Aquatic Plant Management Pub Date : 2023-07-01 DOI:10.57257/japm-d-23-00003
Riley Timbs, Dan Kolterman
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Abstract

Tape grass (Vallisneria americana) once formed large, dense meadows of long (up to 1 m) plants in the littoral zones of Lower St. Johns River (LSJR) and its associated lakes and tributaries (Sagan 2007). Tape grass and most other nonalgal submerged aquatic vegetation (SAV) vanished from much of the river basin after an extended period of high, tanninstained water and increased turbidity due to flooding from Hurricane Irma in 2017 (Goldberg and Trent 2020, Lundy et al. 2022, K.J., unpub. data). Flood events in the LSJR commonly cause temporary SAV die-offs (Lacoul and Freedman 2006, Bornette and Puijalon 2011). In 2004 prolonged conditions of low light availability caused by strikes from three major hurricanes (Charley, Frances, and Jeanne) were followed by extensive SAV loss throughout the river basin. Tape grass and other SAV re-emerged within 3 yr as the river returned to baseline hydrologic and water quality conditions. By contrast, SAV in the LSJR did not fully recover in the 5 yr between when Hurricane Irma made landfall in 2017 and 2022, despite a return to background water conditions. The tape grass plants that remain as of 2022 when data were collected for this study are sparse and have canopy heights below 10 cm (Goldberg and Trent 2020, Lundy et al. 2022, K.J., unpub. data). Herbivory commonly limits tape grass recovery in freshwater and estuarine habitats, including Kings Bay and other Florida waterways, but the extent to which it impacts SAV in the LSJR is unknown (Carter and Rybicki 1985, Hauxwell et al. 2004b, Johnson et al., 2019). Recent efforts to restore tape grass upstream of the LSJR in Lake George and Silver Glen Spring by using wire fenced enclosures to prevent grazing by herbivores yielded canopy heights approximately 10fold higher than surrounding unenclosed plants. When these protective fences were removed or breached the plants were grazed by cooters (Pseudemys spp.) within days to canopy heights equal to the surrounding SAV (, 10 cm). Additionally, blue tilapia (Oreochromis aureus) were observed uprooting unprotected plants near the restoration area (D.K., unpub. data). The Florida Fish and Wildlife Conservation Commission (FWC) has received multiple reports indicating that the tape grass beginning to re-establish areas of the LSJR appear similar to the heavily grazed plants in Lake George and Silver Glen Spring. This study was conducted to determine the effect of herbivory on the growth of tape grass in the Lower St. Johns River.
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除草剂影响佛罗里达州圣约翰河下游美洲苦草的恢复
在圣约翰河(LSJR)及其相关的湖泊和支流的沿岸地区,带状草(Vallisneria americana)曾经形成了长(长达1米)植物的大型、密集的草甸(Sagan 2007)。2017年飓风Irma引发的洪水导致长时间的高单色水和浊度增加后,带状草和大多数其他非藻类淹没水生植被(SAV)从大部分流域消失(Goldberg and Trent 2020, Lundy et al. 2022, k.j., unpub)。数据)。在LSJR的洪水事件通常会导致短暂的SAV死亡(Lacoul and Freedman 2006, Bornette and Puijalon 2011)。2004年,三个主要飓风(查理、弗朗西斯和珍妮)的袭击造成了长时间的低光照条件,随后整个流域出现了广泛的SAV损失。随着河流恢复到基线水文和水质条件,带状草和其他SAV在3年内重新出现。相比之下,在2017年飓风伊尔玛登陆至2022年之间的5年时间里,LSJR的SAV并没有完全恢复,尽管已经恢复到背景水条件。截至本研究收集数据的2022年,保留的带状草植物稀疏,冠层高度低于10厘米(Goldberg and Trent 2020, Lundy et al. 2022, K.J, unpub)。数据)。食草性通常限制淡水和河口栖息地(包括金斯湾和佛罗里达州其他水道)的带状草恢复,但它对LSJR中SAV的影响程度尚不清楚(Carter和Rybicki 1985, Hauxwell等人2004b, Johnson等人,2019)。最近,在乔治湖和银谷泉的LSJR上游,通过使用铁丝围栏来防止食草动物的放牧,恢复带状草的努力取得了比周围未封闭植物高约10倍的树冠高度。当这些保护栅栏被拆除或破坏时,这些植物在几天内被库特(pseudomyys spp.)放牧到与周围SAV相等的冠层高度(约10厘米)。此外,还观察到蓝罗非鱼(Oreochromis aureus)连根拔起恢复区附近未受保护的植物(d.k., unpub.)。数据)。佛罗里达鱼类和野生动物保护委员会(FWC)收到了多份报告,表明带状草开始在LSJR地区重新建立,与乔治湖和银谷泉的大量放牧植物相似。本研究旨在探讨草食对圣约翰河下游带状草生长的影响。
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来源期刊
Journal of Aquatic Plant Management
Journal of Aquatic Plant Management 生物-海洋与淡水生物学
自引率
9.10%
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0
审稿时长
12 months
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