Dc. Mcavoy et al., CHEMICAL FATE AND TRANSPORT IN A DOMESTIC SEPTIC SYSTEM - SORPTION AND TRANSPORT OF ANIONIC AND CATIONIC SURFACTANTS, Environmental toxicology and chemistry, 13(2), 1994, pp. 213-221
The sorption and transport of linear alkylbenzene sulfonate (LAS) and
dialkyl quaternary ammonium compounds [ditallow dimethyl ammonium chlo
ride (DTDMAC) and distearyl dimethyl ammonium chloride (DSDMAC)] were
determined within the upper soil horizons and in the aquifer below a s
eptic tank tile field at a study site in Ontario. Sorption of LAS was
greatest immediately below the tile field (K-d = 17 L/kg) within the u
pper unsaturated soil horizons and lowest in the aquifer (K-d = 1 L/kg
). LAS sorption appeared to be controlled by a hydrophobic mechanism a
nd was positively correlated with the organic carbon (r = 0.9) and the
clay content (r = 0.9) in the subsurface environment. The sorption of
DTDMAC/DSDMAC (K-d = 25-62 L/kg) was an order of magnitude higher tha
n LAS but showed no trend throughout the subsurface environment. The r
etention of DTDMAC/DSDMAC was believed to be by ion exchange within th
e clay interlayer basal spaces. Samples collected from the field showe
d concentrations of DTDMAC to range from approximately 60 mg/kg in the
tile field gravel to <2 mg/kg within 10 cm of soil below the tile fie
ld gravel. Concentrations of LAS were approximately 20 mg/kg in the ti
le field gravel and diminished to <1 mg/kg within 5 cm of soil below t
he tile field gravel. Soil solution and aquifer concentrations of LAS
were always <50 mu g/L and usually below the detection limit of 10 mu
g/L in the aquifer. Concentrations of DTDMAC in the aquifer were below
the limit of detection (4 mu g/L). Mathematical calculations illustra
ted the importance of biodegradation and sorption as removal mechanism
s of these materials in subsurface environments.