L. Zanini et al., PHOSPHORUS CHARACTERIZATION IN SEDIMENTS IMPACTED BY SEPTIC EFFLUENT AT 4 SITES IN CENTRAL CANADA, Journal of contaminant hydrology, 33(3-4), 1998, pp. 405-429
Citations number
31
Categorie Soggetti
Water Resources","Environmental Sciences","Geosciences, Interdisciplinary
Characterization of phosphorus (P) enriched solids was undertaken in t
he sediments below four mature septic system infiltration beds, where
previous monitoring of phosphate (PO4) concentrations in the groundwat
er had indicated that substantial retention of P was occurring in the
vadose zone. At each site, zones of sediment P enrichment were identif
ied by an acid extraction procedure. Acid extractable sediment P conce
ntrations were found to be 2-5 times higher than background values, wi
thin narrow discrete zones generally 10-30 cm in thickness, located wi
thin one meter of the infiltration pipes. Back scattered electron imag
es of the P enriched zones indicated that the P solids occurred as dis
tinct authigenic grains (up to 300 mu m diameter) and as grain coating
s. Microprobe analyses indicated predominantly Fe-P in calcareous sedi
ments (Cambridge and Langton) and AI-Fe-P in non-calcareous sediments
(Muskoka and Harp Lake). Porewater analyses indicated that the zones o
f P accumulation were closely associated with zones of redox change ch
aracterized by the conversion of effluent NH4+ to NO3-. The data sugge
sts that a substantial amount of the septic derived P is being attenua
ted by mineral precipitation reactions that occur rapidly after the ef
fluent encounters subsurface sediments. Reductive dissolution of ferri
c (oxy)hydroxide minerals as a consequence of reducing environments ne
ar the infiltrations pipes, the release of Fe2+ in solution and subseq
uent conversion of Fe2+ to Fe3+ may promote the precipitation of ferri
c or ferrosoferric PO4 minerals. In sediments with limited buffering c
apacity (calcite deficient), the decrease in pH resulting from effluen
t oxidation may cause Al (oxy)hydroxide dissolution and subsequent pre
cipitation of AI-P rich phases. These precipitation reactions appear t
o have the capacity to immobilize a substantial amount of septic deriv
ed P (25-99% at these sites) for a considerable period of time. (C) 19
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