Invader or Indicator? Water Lettuce (Pistia stratiotes) and the Eutrophication Paradox in the Vaal River
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According to the Green Drop Watch Report 2023 (DWS, 2023), approximately 60% of WWTW within municipalities located in the Vaal River catchment are in a critical state - some of which discharge raw/partially treated sewage directly or indirectly (e.g., via tributaries such as the Rietspruit River) into the Vaal River. The Vaal River is the third largest river in South Africa (RSA) and supplies water to key sectors such as mining, power generators, agriculture (e.g., irrigation), various industrial activities, and urban development (Tempelhoff et al., 2007). This highlights the need to protect the Vaal River and its tributary.
Photo: Thomas du Toit |
The discharge of sewage and agricultural runoff, containing high levels of bioavailable forms of nitrogen (ammonium, nitrates, and nitrites), phosphorous (phosphates), and trace elements, as well as dissolved and suspended organic matter results in eutrophication and change in biological and hydrogeochemical characteristics of the Vaal River (Carey and Migliaccio, 2009). Eutrophication is a process whereby elevated nutrient levels promote the proliferation of algae, cyanobacteria (which may produce and release harmful toxins called cyanotoxins, such as microcystins, into the water and air), and alien invasive plant species (AIPS) such as Eichhornia crassipes (water hyacinth) and Pistia stratiotes (water lettuce) (Ballot et al., 2013; Matthews and Bernard, 2015).
The reported presence of Pistia stratiotes in the Vaal River system has raised concern due to the negative environmental and socioeconomic impacts associated with the aquatic plant. Water Lettuce is an alien invasive, free-floating aquatic plant with an adventitious root system that has two reproductive strategies, namely vegetatively (via plant fragments) and sexually (dispersal of seeds by wind and water) – contributing to its effective invasion dynamics. Pistia stratiotes can reach plant densities of approximately 1000 plants/m2 and 1kg/m2 dry mass (Dewald and Lounibous, 1990; Reddy and De Busk, 1984) – typically observed as dense P. stratiotes mats that cover the surface of the water body, reducing the penetration of sunlight to submerged aquatic organisms, as well as reducing the pH level and dissolved oxygen content (Das et al., 2014; Hill et al., 2020; Kumar et al., 2019). Such changes trigger a shift in the composition of the fauna and flora communities, which can have cascading effects on other trophic levels and lead to ecosystem collapse. Although P. stratiotes has a limited ability to overwinter (i.e., dies back during colder seasons), seeds have a high viability and germination potential under warmer conditions (Hussner et al., 2014). This must be considered in the management of the species whereby the absence of the plant does not indicate its complete eradication from a water body.
Although P. stratiotes is an invasive plant species, numerous studies have demonstrated the plant’s elevated phytoremediation potential, relative to a range of contaminants such as cadmium, copper, mercury, iron, and nutrients (improving the quality of eutrophic water) present in sewage and agricultural runoff (Das et al., 2014). Although the plant has an elevated phytoextraction potential (accumulating high concentrations of these contaminants within its biomass), plant dieback results in the reintroduction of accumulated nutrients into the water body through plant senescence and death – contributing to the biogeochemical cycling of nutrients within the Vaal River system (Mader et al., 2022). This contributes to the complex invasion dynamics of the species and ultimately, the P. stratiotes - eutrophication paradox. Although a legacy of wastewater discharge has resulted in the eutrophication of certain parts of the Vaal River (Mararakanye et al., 2022), the sudden exponential growth and spread of P. stratiotes raises various questions regarding the source of eutrophication. A key question raised is: what acute pollution event(s) created conditions favorable to the proliferation of P. stratiotes, differing from the legacy of point (PS) and non-point sources (NPS) of pollution over the past decades?
The occurrence of critical source areas (CSA), areas contributing disproportionate amounts of NPS pollution resulting from complex interactions between factors associated with the source and fate and transport of contaminants within the receiving water body (Wang et al., 2020), need to be identified to design and implement effective water management and AIPS control programs (Lintern et al., 2018). For example, the low water quality in the lower Vaal River Catchment is attributed to anthropogenic activities (such as agricultural activities), a key NPS pollution in the region (Mararakanye et al., 2022). The identification of these CSAs enables the implementation of mitigation measures to reduce/ prevent the release of harmful contaminants into the environment.
In November - December 2023, the South African Weather Service issued yellow Level 2 warnings for intense rainfall, severe thunderstorms, and hail storms in various provinces including the North West province. Hydroclimatological conditions mediate the introduction, fate, and transport of nutrients within receiving water bodies – attributed to intense rainfall events influencing maximum discharge, time to peak, and runoff rations (Bauwe et al., 2015; Xie et al., 2019). This highlights a potential acute NPS pollution event(s) whereby the observed proliferation of P. stratiotes may be attributed to the increased release of nutrients into the Vaal River and its tributaries via anthropogenic activities. These activities may have included increased runoff from recently fertilized cultivated areas, erosion of fertilizer and tailing storage facility stockpiles, overflow and subsequent discharge of additional raw/partially treated sewage from dysfunctional WWTWs, and increased volume of wastewater discharge from mining and other industrial processes during intense rainfall events. In further support of this potential contamination pathway, the currently reported proliferation of P. stratiotes is significant due to the absence of any previous P. stratiotes blooms in the Vaal River system despite decades of PS and NPS pollution events. Identifying the source and physicochemical characteristics of pollution provides valuable insight into the type of control required (biological, physical, and/or chemical) as well as timeframes whereby implemented control measures must be completed.
Based on the invasion biology of P. stratiotes, this AIPS has been designated a Category 1b invasive species (NEMBA) – indicating that the species poses a threat to aquatic ecosystems and species supported by such ecosystems. Various measures have been implemented to control the spread of P. stratiotes, namely the use of biocontrol agents (e.g., Neohydronomus affinis - Water lettuce weevil), physical removal (e.g. mechanical harvesting), and chemical (e.g., application of herbicides such as glyphosate). Since 1985, Neohydronomus affinis has been released in RSA in watercourses such as Sunset Dam, Letaba, Crocodile, and Sabie Rivers, located within the Kruger National Park (Cilliers, 1991).
A study conducted by Coetzee et al., (2020) demonstrated that N. affinis is an effective biological control agent, resulting in the reduction of P. stratiotes percentage cover while significantly increasing dissolved oxygen content and promoting the recovery of benthic macroinvertebrate community. Additionally, biocontrol measures can be supported by physical control measures, namely the mechanical removal of plants (e.g., plant harvesters) (Mugido et al., 2014). To increase the efficacy of physical control measures, temporal and spatial factors must be considered – such as the flowering season of P. stratiotes and the percentage cover (Galal et al., 2019). Furthermore, P. stratiotes can be controlled through the application of herbicides such as (but not limited to) glyphosate (Datta and Mahapatra, 2015) and bispyribac-sodium (Mudge and Netherland, 2015). However, the application of herbicides may have various ecotoxicological risks and may persist in the environment once introduced.
Based on the potential acute NPS pollution event, the application of a combination of mechanical harvesting and biocontrol measures would be effective, along with the creation of physical barriers (which are currently being deployed throughout the Vaal River system) to prevent P. stratiotes entering key strategic areas. Moreover, increased mechanical removal of P. stratiotes (currently at approximately 220 tons/hr – personal communication) is required to reduce the establishment of a P. stratiotes seed bank prior to the plant’s winter dieback. The simultaneous application of N. affinis would also reduce the plant’s vegetative and sexual reproductive strategies due to the weevil’s mechanism of biocontrol action (Moore and Hill, 2012). Although P. stratiotes has various environmental (e.g., elevated phytoremediation potential) and socioeconomic (harvesting of plant for medicinal uses – e.g. Tripathi et al., (2010)) benefits, the magnitude of the negative impact related to retaining these plants in vital watercourses has not been evaluated. These data could be obtained through undertaking an ecosystem services assessment – an assessment addressing the provisioning, regulating, supporting, and cultural services offered by the Vaal River with and without the presence of P. stratiotes. These data could then be used to support calls for physical and financial investment to control P. stratiotes along with identifying CSAs.
In alignment with our Sustainable Legacies strategy, AECOM RSA is committed to creating sustainable solutions to complex challenges and enhancing the provision of vital ecosystem services. The Small and Medium Enterprises (SMEs), forming part of AECOM’s Enterprise Capacities (EC) Sustainability as well as Environmental portfolios, provide various nature-based solutions (NbS) to address complex environmental and socioeconomic challenges. A key service offered by the EC SMEs is the design and implementation of constructed wetlands (CWs) - engineered biological and hydrogeochemical systems with controllable functional (integrating phyto- and bioremediation technologies) and operational (e.g., hydrological regime) parameters to optimize the remediation of a range of inorganic (viz. metals, salts, nutrients, and radionuclides) (Liang et al., 2019; Overall and Parry, 2004), and organic (e.g., per- and polyfluoroalkyl substances (PFAS) (Arslan and El-Din, 2021) contaminants present within wastewater produced by anthropogenic activities. For example, hybrid and novel CWs can be designed to address and mitigate PS and NPS pollution events, reducing the release of contaminants required for the proliferation of P. stratiotes and cyanobacteria. Simultaneously, this approach enhances the provision of ecosystem services, amid climate change – promoting sustainable development. Additional EC SME components include (but are not limited to) wetland and riparian zone rehabilitation, ecosystem services assessments, regenerative ecology, flood management, and carbon sequestration - incorporating sustainability frameworks (such as Envision) into the design and effective delivery of sustainable, resilient, and equitable NbS.
In conclusion, the presence of P. stratiotes is indicative of an underlying problem, namely the acute and chronic discharge of contaminants into the Vaal River and its tributaries from PS and NPS pollution events. Controlling the symptom (P. stratiotes) does not address the source of pollution - ultimately maintaining the P. stratiotes – eutrophication paradox. The presence of P. stratiotes highlights our need to shift our perspective on how we address environmental challenges, focusing on identifying and addressing CSAs and not the symptoms. Based on the latest scientific literature and best practice guidelines, the EC SMEs at AECOM offer holistic and sustainable NbS, ultimately contributing to your organization’s Sustainable Legacy.