Orthophosphate removal from wastewater by planted vertical-flow wetlands (V
FWs) occurs through three parallel paths, with reaction rates of: sorption
to substratum > biofilm assimilation >> macrophyte uptake. Short term tone
or two loadings) plant removal of phosphorus (P) is small but irreversible,
whereas P removed by substratum sorption, or non-reactive P (NRP) formatio
n, can be returned as reactive phosphorus (RP). The quantity of P removed b
y the three paths is substratum > macrophyte >> biofilm, in the short term,
but macrophyte > substratum >> biofilm, over months. Rhizosphere hydrology
restricts P removal, the rate is limited by mass transfer without liquid m
ixing, but trebled by mixing. Evapotranspirational mixing alone is small an
d erratic. In small, above-ground, systems environmental temperature change
s cause daily mixing, but prevailing soil temperature gradients limit below
-ground mixing. A planted wetland, conceptual model, explains: (1) retentio
n times: determined by initial RP removal rates, and operationally dependen
t on RP concentration and mixing. Aqueous phase cycling reduces retention t
imes several fold; (2) minimum outflow concentrations: controlled by the gr
avel-PO4 sorption equilibrium; (3) sustainable annual P removal: the quanti
ty harvested in the macrophytes. Substratum Fe(III) oxide-hydroxide sorptio
n provides additional assimilation for some years. Specific, model derived.
VFW design and operation recommendations are made. (C) 1999 Elsevier Scien
ce B.V. All rights reserved.