WWW.AU.DK
Conclusion
•
PDMS fiber and silicone O-ring can measure
C
free
, chemical activity and diffusive mass fluxes in (un)planted soil
•
No detectable amounts of PAHs were measured either in the shoot or the leaves over 2 months
•
Adding AC may quickly and permanently reduce the acute toxicity and bioavailability of PAHs in soil
•
Plant-promoted microbial degradation may be a main mechanism of natural attenuation of PAHs
Impact of soil amendments on the freely dissolved concentrations,
chemical activities, and diffusive mass fluxes of PAHs in soil
Objectives
1. To investigate the potential of the soil amendments activated charcoal (AC), charcoal (biochar) and compost to
sorb
PAHs and the
effect of this on their bioaccessibility and bioavailability in soil.
2. To assess the capacity of plants to reduce the freely dissolved concentrations (
C
free
), chemical activities (
a
), and diffusive mass fluxes
of PAHs in a planted and unplanted spiked soil.
Geoffrey Marchal
1
, Kilian E. C. Smith
1
, Zuzanna Frková
1
, Philipp Mayer
1
, Lis Wollesen de Jonge
2
, and Ulrich G. Karlson
1
1
Department of Environmental Sciences, Aarhus University, Box. 358, Frederiksborgvej 399, DK 4000 Roskilde, Denmark
2
Aarhus University ,Department of Agroecology, Research Centre Foulum, Blichers Allé, Postbox 50, DK 8830 Tjele, Denmark
Sorbent carbonaceous soil amendment | phytoremediation | bioaccessibility | bioavailability | radish (
Raphanus sativus
L.)
Method
•
Agricultural soil (3% OM)
•
Phenanthridine, phenanthrene, anthracene, fluoranthene, pyrene spiked at 30 mg
kg
soil
-1and spiked soil was stored at 4°C for 1 month After 2 months (t = 0d),
radish (5 per pots) were planted. Control with PAHs spiked soil but no
amendment nor plant
•
AC, biochar or compost added at 10 g per kg soil
-1and stored again at 4°C for 1
month. Control with soil only and no amendment
•
Silicone (6 O-rings) added to the soil as an extractive sink to measure diffusive
mass fluxes
•
PDMS fiber added to the soil to measure freely dissolved concentration (
C
free)
•
At
t
= 7, 21, 42, 60 days 1 PDMS fiber was removed, and
C
freeand chemical
activity were measured
•
At
t
= 60 days all silicone O-rings were removed and diffusive mass fluxes were
measured
Geoffrey Marchal
geoffrey.marchal@hotmail.com
aquarium
water radish
Aluminium lined pot
PDMS fiber
root
Soil
Silicone O-ring stem leaf
Air exchange
Results
C
free
in planted soil
Fig. 1: Measured freely dissolved pore water concentration of PAHs (Cfree, µg L-1) in the soils with radish plants and amended with either 1% (w/w) of activated carbon (AC), charcoal or compost. The control was soil with radish plants but without
any soil amendment. The initial concentration of each PAH was 30 mg kg-1. Error bars indicate the range (n=4).
Fig. 2: Measured initial (t = 7d) and final (t = 60d) freely
dissolved pore water concentration of PAHs (Cfree, µg L-1) in the
control soil with radish plants (control soil) and the equivalent soil without plants (+B/+V). The initial concentration of each PAH was 30 mg kg-1. Error bars indicate the range (n =4).
Fig. 3: Comparison of the sum chemical activity over time of the PAHs (sum of 5 PAHs) in the soils with radish plants and amended with 1% (w/w) of activated carbon (AC), charcoal or compost. The control was soil with radish plants but without any soil amendment. Also shown is the sum chemical activity of the equivalent unplanted soil (+B/+V). The initial concentration of each PAH was 30 mg kg-1. The grey zone
indicates the range in chemical activities observed in the literature for the onset of lethal baseline toxicity.
C
free
planted soil
vs.
unplanted soil
Chemical activity planted soil
vs.
unplanted soil
Fig. 4: Measured uptake fluxes of PAHs into the silicone O-rings in ng cm-2 d-1 from
the soils with radish plants and amended with 1% (w/w) of activated carbon (AC), charcoal or compost. The control was soil with radish plants but without any soil amendment. Also shown is the sum chemical activity of the equivalent unplanted soil (+B/+V).The initial concentration of each PAH was 30 mg kg-1. Error bars
indicate the range (n =4).