As a cost and energy-efficient technology, constructed wetland treatment systems (CWTS) have gained significant popularity for the remediation of environmental contaminants1,2,3. CWTS uses physical, chemical, and biological processes to remove, transform, or stabilize contaminants. While the physical and chemical processes involved in chemical turnover have been well characterized since the genesis of CWTS, the impact of vegetation remained largely enigmatic2. In recent years, there has been an increased focus on understanding the mechanisms by which plants transform organic and inorganic contaminants of potential concern in wastewaters2,4,5. However, mechanistic studies such as these rely on the ability to cultivate large numbers of macrophytes and favor growth from seed to ensure each plant is at the same stage of growth and development.
CWTS in North America are frequently established using vegetation native to natural wetlands in the region, such as Typha, Scirpus, Juncus, and Phragmites species6,7. The choice of vegetation also depends on the constructed wetland being employed, which can vary in depth, water flow, substrate sourcing, and water sourcing (with or without recirculation)2. Finally, climate also influences wetland vegetation, with cooler climates favoring submerged plants due to their increased adaptability8. Typha species are of particular interest in deep, surface-flow constructed wetlands due to their ability to rapidly colonize an environment and to adapt to diverse environmental conditions9,10.
A recent review of results reported that, of 87 phytotoxicity tests using Typha species, only 15 studies started the test plants from seed, and of those, only one study examined growth in mature plants11. This underrepresentation of cattail experimentation from seed indicates a gap in the literature concerning protocols aimed at describing the cultivation of cattail for laboratory studies. The protocols outlined here aim to bridge this gap by presenting an in-depth protocol for the growth of Typha latifolia from seed to mature plant under sterile and non-sterile conditions. Additionally, this paper discusses a technique for bacterial bioaugmentation of cattail species at the seed stage where early inoculation can help maintain the long-term persistence of introduced rhizo- and endo-phytic microbes.