Back to Table of Contents
46099-G2
Are Natural Chars Important for the Sorption of PAHs? A Field Study With Lake Sediments and Soils in Oriole Lake
Rainer Lohmann, University of Rhode Island
Progress to date
We successfully completed field sampling of sediment cores
from Oriole Lake (CA) in July 2007. A total of three surface (biological, ca 1
m) and three deep (Livingstone-style, ca 4 m cores) cores were taken from the Lake and shipped back to URI. Initially, we worked on the
surface cores first, by sectioning every one cm interval. Subsamples
have been sent out for 210Pb determination of sediment ages (the
results of which are still pending). Subsamples were
analyzed for % moisture, loss on ignition, organic (OC) and soot black carbon
(BC) content and polycyclic aromatic hydrocarbons (PAHs). BC was isolated via a
thermal oxidation method at 375 °C.
We routinely included NIST SRM 1649a (marine sediment) for
BC analysis. Our results (average 0.62% ± 0.06%) are not significantly
different from the average published by the international BC ring trial (0.51%
± 0.14%). Our analysis of the top 50 cm of the cores showed minor fluctuations
in BC content (around 0.5 %), and a very high OC content of ca. 20%. We
therefore decided to bulk the top 15 cm, and use the homogenized sediment
samples to derive porewater concentrations and
sorption equilibrium of the PAHs involved. Sediment samples were incubated with
different masses of polyethylene (PE) samplers to derive
In a modification of our proposal, I decided to use the null
hypothesis (H0) that:
Black carbon and
organic carbon are sufficient to explain the sorption of PAHs to Oriole Lake
sediments.
Alternatively, if the sorption of PAHs to sediments is
significantly underpredicted in Lake Oriole,
then we will quantify chars as a potential 3rd sedimentary phase.
According to H0, the
overall partitioning of PAHs can be attributed to absorption into the OC fraction
(foc) and to adsorption onto the BC fraction
(fBC) via:
Kd = focKoc
+ fBCKBCCwn-1 (1)
with Koc the HOC's OC-water
partitioning constant,
K\BC the HOC's soot BC-water adsorption constant,
n the Freundlich coefficient,
and Cw the dissolved
concentration in µg/L.
Values of the Freundlich coefficient
n, Kocs and KBCs were
taken from the literature. Cw was
calculated after equilibrating the sediments with the PE samplers.
In more detail, Koc was calculated
based on a linear free-energy relationship
Log
Koc
= 0.989*log Kow
- 0.346 (2).
K\BC was derived based on a linear free-energy
relationship between the activity coefficients of the PAHs in water (gw) and
average K\BCs reported by Lohmann et al
(2005) for harbor sediments in Boston and New York:Log
KBC = 0.59*log gw + 2.33 (3).
Activity coefficients were
estimated based on a linear free-energy relationship between log Kow
and gw (Schwarzenbach et al., 2005):
gw = (log Kow + 0.13)/0.75) (4).
As expected, explaining the
observed sorption in Oriole Lake sediments (Kd
= focKoc )
was insufficient to account for the observed partitioning. In contrast, the
combined OC-absorption and BC-adsorption model using equation (1) gave a
satisfactory result for the sediments – 8 out of 12 PAHs were within a factor
of 3 of the predicted results. For most PAHs, sorption was overpredicted
using equation (1), implying that the charred sediments exerted no additional
sorption.
Our next step is to
verify these results with sediments from deeper layer that represents previous
fire-events, to see if sorption of the PAHs changes over time.
Training and
education
The project provided training and education to two
undergraduate students at URI-GSO: Julia Sullivan and Kevyn
Bollinger (URI-GSO). Kevyn was involved in the field
sampling, while Julia has been in charge of the OC, BC and PAH analysis, and
the sediment equilibrations. Both undergraduate students excelled in the
project, and rose to the challenge of being responsible for their own part of
the research to be carried out.
Back to top