“…Hou, Guo, and Wen (2018) studied sulfate and sulfide removal rates in CWs treating water resource recovery facility secondary effluents with varying sulfate loads and found that an increase in the sulfate loading (1.42-7.01 g S/m 3 day) rate increases sulfate removal (1.42-3.16 g S/m 3 day) and sulfide discharging rates (0.08-1.46 g S/m 3 day). Sandhi, Landberg, and Greger (2018) investigated the phytofiltration performance of an aquatic moss (Warnstorfia fluitans) originating from arsenic (As)-contaminated wetlands with varying concentrations of arsenic (1, 10, and 100 μM of arsenate), nutrient loading (0%, 1%, and 10% Hoagland nutrient solution), removal times (0 to 192 hr) along with the adsorption/absorption mechanism of living and dead moss, where 82% removal was observed within 1 hr of operation with 1 μM As and no nutrient in the water. However, a HSSFCW treating acid mine drainage(AMD) containing As-rich acidic waters in the presence and absence of P. australis and two different filter media setups (zeolite and limestone) showed removal rates of As and Pb (>99%), Fe (>98%), and Zn (23%-75%, depending on the cell type (Lizama-Allende, Jaque, Ayala, Montes-Atenas, & .…”