Sustainable Solutions for Environmental Pollution, Volume 2. Группа авторов
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concentration. Aquatic macroinvertebrate richness and density increase with aquatic macrophyte cover, while diversity increases with CW area. Therefore, a CW, installed to improve water quality and enhance biodiversity, must have a large surface area and significant macrophyte coverage (Hsu et al., 2011). Habitat diversity can be increased with the creation of floating islands (FT-CWs), resulting in an overall increase in edge habitat (Becerra-Jurado et al., 2012).
1.11.1 Biodiversity Management
Without proper management, CWs can promote biological invasion or act as an “ecological trap” for native species, i.e., trapping them in poor-quality habitat, jeopardizing individuals or the local or regional population (Sievers et al., 2018). Integrated basin-wide management and connection to natural wetlands can partially mitigate these negative impacts on the long-term biodiversity (Zhang et al., 2020a).
In CWs, the existence of suitable habitat and predatory pressure are the two factors influencing aquatic macroinvertebrate community structure. Fish are often the main predators in CWs and have an influence on the richness, density, diversity, and structure of aquatic macroinvertebrate communities (Hsu et al., 2011). Swans, ducks, and coots feed on aquatic vegetation: they can cause some damage, such as on floating mats.
The different factors can be actuated by proper management of CWs and can therefore be used to increase biodiversity. Among the environmental factors influencing CW biodiversity, connectivity is considered a key factor in the colonization by aquatic fauna. Indeed, the connectivity of CWs with other nearby lentic water bodies and their distribution in the landscape are at the heart of conservation strategies. Connecting CWs to the various water bodies isolated in the landscape by ecological corridors facilitates connectivity. In addition, for macroinvertebrates with low mobility such as gastropods, the introduction of sediment and vegetation samples from surrounding natural wetlands facilitates the colonization of new CWs by local flora and fauna species. In all cases, the introduction of invasive species should be avoided (Becerra-Jurado et al., 2012). Increasing the heterogeneity or complexity of habitats and their age increases the biodiversity of CWs. In order to maintain the biodiversity, it is essential to maintain irregular depth profiles by adjusting water depth and controlling the macrophyte sprawling (Manzo et al., 2020).
Although considered as low-maintenance systems, NBSs require minimal maintenance, such as monitoring the banks, and the quality of both the final effluent and the receiving water. Part of this monitoring can be easily carried out by local residents. In addition, the importance of the biodiversity of CWs for agricultural areas should be explained to farmers and local communities through educational programs (Becerra-Jurado et al., 2012).
1.12 Nuisances
1.12.1 Greenhouse Gases (GHG)
Some few studies directly measure GHG emissions from CWs by floating chambers or as their dissolved forms (Harrison et al., 2005; Clough et al., 2007; Beaulieu et al., 2008). Methane emissions from paddy fields contribute about 9% of total global anthropogenic emissions (Saunois et al., 2016). The magnitude of daily emissions varies from one study to another, from just a few µg/(m2 d) (Beaulieu et al., 2010) to around 5 mg/(m2 d) (Beaulieu et al., 2010) at around 5 mg/(m2 d) (Hinshaw and Dahlgren, 2013) for N2O and from less than 0.4 mg/(m2 d) to almost 200 mg/(m2 d) for methane; i.e., from about 0.5 ml/(m2 d) to about 270 ml/(m2 d) (Wilcock and Sorrell, 2008). However, to our knowledge, no study has evaluated these emissions over a complete hydrological cycle. In addition, several studies show that GHG emissions are strongly dependent on organic input for both methane (Maeck et al., 2013) and N2O (Lefebvre et al., 2004). Discharges of organic inputs, such as combined sewer overflow discharges, strongly condition these emissions. Vegetation helps to decrease GHG emissions and its maintenance should be carefully planned: decaying plant remnants increase GHG emissions as well as sediment disturbance induced by mechanical plant removal (Badiou et al., 2019). Methane can be transported from the sediment to the atmosphere by emergent and floating-leaved plants themselves: a higher conductance (by a factor of two) has been observed in floating-leaved plants (American lotus and water lily) than in Typha angustifolia L. (Villa et al., 2020). The influence of the type of vegetation is rarely considered and not incorporated in models.
1.12.2 Noxious Gases
Wastewater rich in OM and mineral compounds such as sulfates and phosphates can be anaerobically reduced to form noxious gases such as hydrogen sulfide (H2S) or phosphine (PH3). The property of sulfide ion to form insoluble precipitates with heavy metal ions makes it an excellent immobilizing agent for toxic metals in the bottom sediments. However, high sulfide concentrations can have a negative effect on wetland plant growth and microbial activity, particularly nitrification (Wu et al., 2013). H2S is a toxic and foul-smelling gas highly toxic to mammals (including humans) and aquatic species. The creation of dynamic oxidation-reduction gradients (aerobic-anaerobic) in the rhizosphere of CWs can simultaneously produce nitrification/denitrification and anaerobic ammonium oxidation (Anammox) and sulfur oxidation/reduction conditions that allow sulfide removal (Gonzalias et al., 2007; Jones et al., 2017). Bacteria such as Desulfovibrio and Desulfobacter and Archaea, such as Archaeoglobus are able to reduce sulfate in anaerobic conditions: these conditions can be obtained for example when a surface-flow wetland is completely covered by free-floating plants (such as duckweed). The flora of aquatic systems (including wetlands) is diversely sensitive to sulfide. Threshold values between 10 µmol/L (for Carex sp.) and 1500 µmol/L (for P. australis) have been reported (Lamers et al., 2013).
The natural phenomenon known as “Ignis fatuus” or “Will-o’-the-wisp” (flickering glows observed during night on bogs and swamps) is due to the spontaneous ignition of phosphine (swamp gas) in the presence of methane resulting from the decomposition of OM under anaerobic conditions (Roels and Verstraete, 2001). Indeed, anaerobic wetlands are capable of producing phosphites and PH3 from phosphate (Bains et al., 2019). The former has been detected in marsh gas (Dévai and Delaune, 1995; Geng et al., 2005), paddy fields (Niu et al., 2013), and wastewater and sewage (Devai et al., 1999). The matrix-bound PH3 has been detected in various types of sediments in estuaries and coastal areas (Zhu et al., 2011).
1.12.3 Mosquitoes
The main nuisance associated with CWs is the prospect of an increase of the mosquitoes’ population and the potential transmission of diseases (e.g., West Nile, dengue and chikungunya viruses, or Plasmodium malaria). Mosquitoes are Diptera insects of the family “Culicidae” represented by more than 3,500 species worldwide. They develop in two phases: a strictly aquatic thermo-dependent larval phase and an aerial adult phase. Larval development can last between five days and three months depending on the water temperature (thermo-dependence) and the availability of food resources (they consume small planktonic organisms). Following their emergence out of the water, adult females search for the proteins necessary for the maturation of their eggs thanks to blood meals on various hosts such as mammals, birds and reptiles (Valdelfener et al., 2019).
A drastic strategy, for subsurface flow structures, is to ensure that no area will remain in water for a period of more than four days. Running and covered water minimizes mosquito development. Water levels can be managed at certain times of the year to create habitat that is hostile to mosquito development. In the case of permanent water bodies, such as FSF-CWs, the most effective strategy consists to achieve a well-balance ecosystem, allowing the permanent presence of communities of predators and competitors of larval mosquitoes (fish, crustacean zooplankton, and aquatic insects) and imagoes (insects, amphibians, bats, and birds such as swallows) (Medlock and Vaux, 2015). More permanent CWs have more predators, and therefore, mosquitoes’ density is reduced (Holmes and Cáceres, 2020). However, caution should be exercised on the introduction of non-native fish species. Indeed, an overpopulation of predators can considerably reduce macro-invertebrate