Tolerance to flooding
Brachiaria mutica, thanks to its adventitious roots, was reported to have a better tolerance to flooding than Brachiaria decumbens, B. brizantha and B. humidicola (Mattos et al., 2005). Flooding has no impact on growth, even during long periods (Haddade et al., 2002).
Water flow and erosion control
Para grass is particularly adapted for the control of water flow and erosion of river banks (Schultze-Kraft et al., 1992). However, para grass may become an issue in ditches, headlands drains and earth tanks where it may choke water flow, increase sedimentation and cause waterlogging of neighbouring crops as this is the case for sugarcane crops in Australia (Hannan-Jones et al., 2012). Sedimented conditions were also reported to smother benthic species and thus reduce the biodiversity of wetlands (Hannan-Jones et al., 2012).
Fire
If ungrazed in wetlands of northern Australia, para grass may become a fuel for fires that occur during the dry season. It was reported to represent a much bigger fuel load than native grasses and is thus more likely to burn every dry season (Hannan-Jones et al., 2012). These fires are a threat to natural stands of Melaleuca trees (Cook et al., 2005).
Invasiveness
As a long-lived, vegetatively propagating pioneering species of disturbed areas, para grass has potential for invasiveness. It is reported to benefit from cultivation, browsing pressure, mutilation and fire (Rojas-Sandoval et al., 2014). It may have deleterious effects on native plant species such as wild rice (Oryza australiensis) whose seeds provide food for indigenous birds. In 1977, para grass was listed as a serious weed in Australia, Fiji and Thailand, as a weed in Sri Lanka, Colombia, Hawaii, Jamaica, Malaysia, Peru, the Philippines, Puerto Rico and Trinidad, and as a common weed in Borneo and Mauritius (Holm, 1977).
Phytoremediation
Para grass, when coupled with a complex of endophytic bacteria (Acinetobacter sp. and Pseudomonas aeruginosa), holds great potential for the remediation of polluted environments, such as crude-oil contaminated soils. It could degrade up to 78% crude oil (Fatima et al., 2016). These results are in accordance with those obtained earlier with the use of para grass to remove organic and inorganic matter from sewage effluets (Ijaz et al., 2015). Para grass could be grown on chromite mine areas, having rapid massive growth in spite of high chromium (Cr) levels. It mainly accumulated Cr in its roots and could be used to reduce the Cr level of the soil (Mohanty et al., 2012).
In soils with high salinity levels, such as those of rice irrigated with wasterwater in periurban areas, para grass could help recovering good conditions for rice cultivation while responding to the increasing demand in fodder (Biggs et al., 2009; Mattos et al., 2005).
Agroforestry
Para grass can be grown under coconut trees, and yielded good DM amounts provided it received adequate N fertilizer (Pandey et al., 2011).