Abstract
Freshwater ecosystems provide essential resources and vital ecosystem services. These ecosystems exist in a delicate state of balance and are under increasing anthropogenic and climatic pressures. One of the major anthropogenic threats to freshwater ecosystems is eutrophication that often leads to algal blooms, some of which may be extremely harmful. Current chemical and physical interventions to prevent algal blooms can be expensive, ephemeral and disruptive to other aspects of the ecosystem. Therefore, there is interest in utilising biological methods of control. This study aimed to assess the viability of allelopathic repression of nuisance algae species by invasive aquatic plants. The allelopathic effect of Hydrocotyle ranunculoides (Floating Pennywort) and Crassula helmsii (Swamp Stonecrop) were tested in both whole plant and crushed plant states for their ability to affect the average population growth of monocultures and co-cultures of the green algae Chlorella vulgaris and the cyanobacterium Synechocystis sp. PCC6803. Methanol extracts from these species have been identified in the literature to have high allelopathic potential. The key findings of this study are that, for Chlorella: whole H. ranunculoides and crushed C. helmsii had a negative effect on the average population growth; whole H. ranunculoides had a greater negative effect than crushed H. ranunculoides; and crushed C. helmsii had a more negative effect than crushed H. ranunculoides. For Synechocystis: crushed C. helmsii had a greater negative effect on the average population growth than crushed H. ranunculoides; and the presence of Chlorella in co-culture experiments had a universally positive effect on its average population growth. The species-specific nature of these allelopathic interactions suggests that the use of allelopathy for algal bloom control may have to be assessed on a case-by-case basis and the use of combination treatments should be assessed. Moreover, the effects exerted by allelochemicals in open water systems is likely to be direct, indirect and context specific. Although this study explores the possibility of embracing the allelopathic potential of invasive aquatic plants, we do not encourage novel introductions of invasive species into open freshwater systems. However, potential allelopathic effects could be leveraged in already invaded systems, or in closed systems within an invaded range.
Highlights
Freshwater ecosystems deliver numerous essential ecosystem services, including the provision of drinking water, food resources, diverse habitat, irrigation, and recreation
Especially shallow lakes, exist in a delicate state of balance between alternative equilibria, either occupying a favourable clear water state dominated by bottomrooting aquatic vegetation, or a turbid state characterised by high microalgal biomass (Scheffer et al, 1993)
Instead of using plant extractions, we focused on the effect of the whole plant, compared to the crushed plant, on their ability to affect axenic populations of the green algae Chlorella vulgaris and the cyanobacteria Synechocystis sp
Summary
Freshwater ecosystems deliver numerous essential ecosystem services, including the provision of drinking water, food resources, diverse habitat, irrigation, and recreation. Elevated nutrient conditions are one of the key causes of Harmful Algal Blooms (HABs) These accumulations of harmful algae vastly reduce water quality and disrupt aquatic ecosystems through increased turbidity (Capuzzo et al, 2015), oxygen depletion (Sun et al, 2018), shading out other organisms in the water column (Hu and Hong, 2008) and the release of algal toxins which can poison ecosystems and water supplies (Paerl et al, 2001; Azevedo et al, 2002). These effects can result in the death of large numbers of aquatic organisms; reducing biodiversity (Lund, 1965; Reynolds and Walsby, 1975; Nasri et al, 2008); reducing the aesthetic value of affected waterbodies (Mitra and Flynn, 2006); and toxins and necrotic material threaten human health by entering drinking water supplies (Lam et al, 1995)
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