Lg. Whyte et al., Bioremediation treatability assessment of hydrocarbon-contaminated soils from Eureka, Nunayut, COLD REG SC, 32(2-3), 2001, pp. 121-132
The bioremediation potential of three hydrocarbon-contaminated soil samples
with diverse soil physical/chemical characteristics from Eureka, Ellesmere
Island, Nunavut, was assessed. Microbial enumeration by viable plate count
s and MPN analyses combined with molecular analysis (PCR and colony hybridi
zation) for hydrocarbon catabolic genes (alkB(+), xylE(+), ndoB(+)) demonst
rated the presence of significant numbers of aerobic cold-adapted hydrocarb
on-degrading organisms in the three contaminated soils. The degradative act
ivities of the indigenous microbial populations were assessed by mineraliza
tion of C-14-labelled hexadecane (C16) and naphthalene at 5 degreesC or 23
degreesC in untreated and treated soil microcosms. Although very low rates
of C16 and naphthalene mineralization were observed in untreated microcosms
, nutrient supplementation with a commercial inorganic fertilizer (20:20:20
) markedly increased mineralization in the soil microcosms, indicating that
these soil are nutrient-deficient. Increasing the incubation temperature t
o 23 degreesC markedly decreased the acclimation period and increased the r
ate of mineralization in soil microcosms supplemented with 20:20:20. Optima
l treatments resulting in the greatest rates and levels of mineralization f
or each soil were determined: Soil #1, 20:20:20 + tilling; Soil #2, 20:20:2
0 + peat moss; Soil #3, 20:20:20 + water to 60% WHC. Total petroleum hydroc
arbon (TPH) analysis of cold soil microcosms revealed that, similar to the
soil mineralization assays, the optimal treatments' increased TPH degradati
on compared with fertilizer treatment alone. TPH levels in the contaminated
Eureka soils were reduced from 5166 to 2966 ppm in Soil #1, from similar t
o 4256 to 2466 ppm. in Soil #2, and from 4500 to 1933 ppm in Soil #3 follow
ing the appropriate treatment after 16 weeks incubation at 5 degreesC. Thes
e results indicate that the bioremediation potential of the Eureka soils at
low ambient summer temperatures is considerable. It is suggested that the
on-site treatment planned for the 2000 summer include the application of a
commercial fertilizer and, if feasible, additional treatments such as tilli
ng, addition of peat moss, or water, depending on the contaminated soil's p
hysical/chemical characteristics. (C) 2001 Published by Elsevier Science B.
V.