The
Half-Life of Gaseous Ozone Pulsed Soil Perfusion for MTBE
and Other Oxygenate Removal
William
B. Kerfoot, Kerfoot Technologies, Inc., 766-B Falmouth
Road, Mashpee, MA 02649,
Tel: 508-539-3002,
Fax: 508-539-3566,
Email: wbkerfoot@kerfoottech.com
It
is a common misconception that ozone gas has a short
half-life. Dissolved
ozone, which reacts with water to release hydroxyl
radicals, has a half-life of minutes; whereas ozone in
gaseous form has a half-life measured in hours or longer.
W. S. Sease in “Ozone Mass transfer and contact
Systems,” stated that at 0°C, the half life of gaseous
ozone is 2,000 years.
Ozone-air mixtures placed in sampling VOC vials,
checked periodically, showed an initial quick drop
(half-life 5-9.5 hours) during which time the gas reacts
with other air components (nitrogen and moisture), then a
slow half-life of 35 hours commonly exists.
Reducing microbubble size has a profound effect on
capacity of bubbles to remain in solution, their
reactivity, and in transmission through soils.
Below 100 micron size, stable solutions of nano to
microbubbles can be produced in aqueous solutions.
With pulsing at certain frequencies and pressure
differentials, the bubble emulsions can be transmitted
vertically and laterally for oxidative reactions with
target organic compounds, like MTBE.
By controlling bubble size, ozone concentration and
air/ozone volume released per pulse, the likelihood of
fugitive ozone emissions can be reduced or eliminated
while oxidation reactions proceed.
Laboratory tests were conducted to compare
microbubble buoyancy versus diameter for various column
diameters. Vertical
travel velocities were then compared to columns of sand of
differing permeabilities.
The effect of pressure differentials in producing
significant vertical and horizontal transport were defined
and compared to observed field transport.
The arrival of microbubbles into monitoring wells
could be counted and was correlated with the arrival of
wavefronts. The
observed rate of removal of MTBE at different release
sites from retail gasoline service operations is compared
with theoretical mechanics.
Observed half-life (pseudo-first order) attenuation
coefficients ranged from 3 to 14 days when mean midway ROI
values from nano to microporous diffusors are compared.
The radial spread must be taken into account when
comparing efficiencies of removal from site to site.
A modification of Clayton’s equation for ozone
reactivity can be used for predictive purposes.
Air
Spacing Effectiveness in MtBE Removal from Water, Tested
on an Intermediate Scale Laboratory Apparatus
Daniele
Lausdei, Golder Associates S.r.l., Via Messina, 25, 00198
Roma, Italy, Tel: +39-06-44250873, Fax: +39-06-44250951,
Email: dlausdei@golder.it
Claudio Alimonti, Università di Roma "La Sapienza",
Via Eudossiana, 18, O0184 Roma, Italy, Tel:
+39-06-44585628, Fax: +39-06-44585618, Email:
claudio.alimonti@uniroma1.it
In
the last decade the groundwater contamination by MtBE due
to fuel spills or leakage from underground storage
facilities became a high sensible environmental issue.
Among all the in-situ groundwater remediation treatments,
aimed to remove MtBE and the other gasoline components,
the Air Sparging (AS) has been widely used since it is one
of the best established economical and reliable
technologies for the remediation of volatile compounds
dissolved in groundwater. Nevertheless there are still
many uncertainties regarding the airflow distribution in
saturated media and the interactions of various
physical-chemical processes during AS applications. Thus,
the present experimental study was aimed to investigate
the effectiveness of AS in dissolved MtBE removal from a
saturated media, performing a removal test under confined
and controlled conditions in an intermediate scale tank (m
1 x 1 x 1,2). The experimental conditions have been
focused to study the stripping process driven by the air
injection, since stripping is considered to be the most
effective among the removal processes driven by AS, in the
short terms of its in situ application. Through data
interpretation, several considerations were made to
evaluate the effects of geometry, water temperature and
bulk water movement on the effectiveness of AS removal
from MtBE contaminated water. This study confirmed that
in-situ AS has a significant potential in groundwater
remediation contaminated by MtBE, showing that the
stripping action driven by the air injection give such a
strong contribution to the comprehensive removal action of
the AS technology. Following this, was also investigated
the influence of some factors governing the efficiency of
the process of stripping, such as the sparge point screen
size and the usage of surfactants to enhance the AS
performance.
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