Hennessey Ashley V, McDonald Michael B, Johnson Peyton P, Gladfelter Matthew F, Merrill Kate L, Tenison Suzanne E, Ganegoda Sathya S, Hoang Tham C, Torbert H Allen, Beck Benjamin H, Wilson Alan E
School of Fisheries, Aquaculture, and Aquatic Sciences, Auburn University, Auburn, AL, USA.
USDA-ARS, National Soil Dynamics Laboratory, Auburn, AL, USA.
Environ Pollut. 2025 Mar 1;368:125691. doi: 10.1016/j.envpol.2025.125691. Epub 2025 Jan 22.
Harmful algal blooms (HABs) cause severe economic and environmental impacts, including hypoxic events and the production of toxic and off-flavor compounds. Chemical treatments, such as copper sulfate pentahydrate (CuSO·5HO), are often used to mitigate the damaging effects of algal blooms. However, treatment effects are usually short-lived leading to waterbodies requiring repeated CuSO·5HO applications to control persistent algal blooms, particularly in highly eutrophic systems, such as aquaculture ponds or small agricultural impoundments. We hypothesized phytoplankton communities routinely treated with Cu develop community tolerance to treatment making algal blooms more difficult to manage over time. Pollution-induced community tolerance (PICT) is a method for measuring how a community can withstand selective pressures to a toxicant. To test whether phytoplankton develop community tolerance to algaecidal treatment, the toxic effects of Cu were evaluated at a standard dose (1.37 mg/L CuSO·5HO or 0.35 mg/L total Cu) and a low dose (0.69 mg/L CuSO·5HO or 0.17 mg/L total Cu) relative to untreated controls. Treatments were applied once to 1300 L mesocosm enclosures installed in a productive aquaculture pond and monitored for 28 days. Acute toxicity bioassays measured photosynthetic efficiency across a wide range of Cu concentrations (0.05-300 mg/L). The PICT bioassay results were used to generate dose-response curves for median effective concentrations (EC50s) to assess phytoplankton community tolerance to Cu toxicity. The results of this study showed that both doses of Cu led to over 99% removal of cyanobacteria in the first seven days and maintained a reduction in cyanobacterial abundance by at least 70% throughout the experiment. After three days of exposure, the phytoplankton communities in the standard and low-dose treatments exhibited a 12.4x and 5.2x increase in Cu community tolerance, respectively, compared to controls. This increase in community tolerance was driven by Cu-tolerant chlorophyte species. These findings suggest that, while community tolerance to Cu may alter the perceived effectiveness of treatment over time, it can promote a beneficial shift from cyanobacteria to chlorophyte species, ultimately contributing to a more sustainable system.
有害藻华(HABs)会造成严重的经济和环境影响,包括缺氧事件以及有毒和异味化合物的产生。化学处理方法,如五水硫酸铜(CuSO₄·5H₂O),常用于减轻藻华的破坏作用。然而,处理效果通常是短期的,导致水体需要反复施用五水硫酸铜来控制持续的藻华,特别是在高度富营养化的系统中,如水产养殖池塘或小型农业蓄水池。我们假设经常用铜处理的浮游植物群落会对处理产生群落耐受性,使得随着时间的推移藻华更难管理。污染诱导的群落耐受性(PICT)是一种衡量群落如何承受对有毒物质的选择性压力的方法。为了测试浮游植物是否对杀藻处理产生群落耐受性,相对于未处理的对照,在标准剂量(1.37毫克/升五水硫酸铜或0.35毫克/升总铜)和低剂量(0.69毫克/升五水硫酸铜或0.17毫克/升总铜)下评估了铜的毒性作用。将处理剂一次性施用于安装在一个高产水产养殖池塘中的1300升中宇宙围隔中,并监测28天。急性毒性生物测定法测量了在广泛的铜浓度范围(0.05 - 300毫克/升)内的光合效率。PICT生物测定结果用于生成半数有效浓度(EC50s)的剂量 - 反应曲线,以评估浮游植物群落对铜毒性的耐受性。这项研究的结果表明,两种剂量的铜在头七天内都导致蓝藻去除率超过99%,并且在整个实验过程中蓝藻丰度至少保持70%的降低。暴露三天后,标准剂量和低剂量处理中的浮游植物群落与对照相比,对铜的群落耐受性分别提高了12.4倍和5.2倍。这种群落耐受性的提高是由耐铜的绿藻物种驱动的。这些发现表明,虽然群落对铜的耐受性可能会随着时间改变处理的感知效果,但它可以促进从蓝藻到绿藻物种的有益转变,最终促成一个更可持续的系统。