Challenges
for Ethanol Fuels Contaminated Sites Assessment
Student Presenter
Juliana G. de Freitas, Dept. of Earth and
Environmental Sciences, University
of
Waterloo, Waterloo, ON,
Canada
James F. Barker, Dept. of Earth and
Environmental Sciences,
University
of
Waterloo
,
Waterloo
,
ON
,
Canada
Ioannis Chatzis, Chemical Engineering,
University
of
Waterloo
,
Waterloo
,
ON
,
Canada
Ambient
Groundwater Quality in the
Lower
Hudson
Valley
of Southeastern
New York
State
Student Presenter
Steven Parisio, Regional Solid Waste Geologist, New
York State Department of Environmental Conservation,
New
Paltz
,
NY
Eva
M. Knoth, New York State Department of Environmental
Conservation, New Paltz, NY
Michael Rispoli, Student Intern, New York State
Department of Environmental Conservation, New Paltz,
NY
Challenges
for Ethanol Fuels Contaminated Sites Assessment
Student Presenter
Juliana G. de Freitas, Dept. of Earth and
Environmental Sciences, University of Waterloo, 200
University Avenue West, Waterloo, ON, N2L 3G1, Canada,
Tel: 519-888-4567 ext.35284, Fax: 519-746-7484, Email:
jgardena@scimail.uwaterloo.ca
James F. Barker, Dept. of Earth and Environmental
Sciences, University of Waterloo, 200 University
Avenue West, Waterloo, ON, N2L 3G1, Canada, Tel:
519-888-4567 ext. 32103, Fax: 519-746-7484,
Email: jfbarker@sciborg.uwaterloo.ca
Ioannis Chatzis, Chemical Engineering, University of
Waterloo, 200 University Avenue West, Waterloo, ON,
N2L 3G1, Canada, 519-888-4567 ext.33306, Fax:
519-746-7484, Email: ichatzis@uwaterloo.ca
The
use of ethanol as an additive in gasoline is
increasing significantly in
North America
, raising concerns about the consequences of ethanol
usage when monitoring the subsurface for groundwater
contamination. One piece of the problem is the effect
of ethanol on contaminant distribution in the source
zone. Ethanol can change important properties of the
system which can result in an unexpected distribution
of the gasoline contaminants. Ethanol can also enhance
the solubility of aromatic hydrocarbons such as
benzene.
In 2D
visualization experiments gasoline was injected in the
top of the unsaturated zone and then ethanol was
injected in the same position. It was shown that
ethanol can mobilize the gasoline and alter its
distribution significantly. The visualization
experiments also indicate that ethanol stays mainly in
the capillary fringe, being transported above the
water table along with cosolubilized hydrocarbons.
However, typical monitoring techniques applied at fuel
contaminated sites are not intended to sample the
capillary fringe. Although under some conditions a
typical monitoring well may draw some ethanol
contaminated water, providing an indication of
contamination, the sample will be diluted and
therefore the measured concentration may be
significantly smaller than the actual concentration in
the capillary fringe. Therefore, the horizontal
transport of high concentrations of hydrocarbons and
ethanol in the capillary fringe at field scale
presents significant challenges for monitoring. For
example, since sampling in the vadose zone requires
suction, volatile losses are more likely to happen
when sampling water from the vadose zone. Laboratory
experiments showed that the use of ceramic suction
samplers may result in loss of volatile organics of up
to 30%, depending on the pressure applied and compound
properties. The concentration of ethanol in the
aqueous phase was also shown to interfere with the
sample bias.
Ambient
Groundwater Quality in the
Lower
Hudson
Valley
of Southeastern
New York
State
Student Presenter
Steven Parisio, New
York State Department of Environmental Conservation,
Region 3 Office, New Paltz, NY 12561, USA, Tel:
845-256-3126, Fax: 845-255-3414; Email: sxparisi@gw.dec.state.ny.us
Eva M. Knoth, New York State Department of
Environmental Conservation, Region 3 Office, New Paltz,
NY 12561, USA, Tel: 845-256-3142, Fax: 845-255-3414;
Email: emknoth@gw.dec.state.ny.us
Michael Rispoli, New York State Department
of Environmental Conservation, Region 3 Office, New
Paltz,
NY
12561
,
USA
, Tel: 845-256-3142, Fax: 845-255-3414 Email: rispol36@newpaltz.edu
A large volume of
groundwater quality monitoring data has been collected
in connection with solid waste landfills which are
regulated by the New York State Department of
Environmental Conservation.
The data set for the seven counties which
comprise the study area in southeastern
New York
State
includes more than sixty monitored landfills.
Most sites have at least one upgradient
monitoring well which is located outside of the
potential zone of influence for landfill-derived
groundwater contamination and is used to establish
ambient groundwater quality for the site.
At the typical site, between fifteen and thirty
rounds of sampling
have been completed with a list of more than forty
water quality parameters being analyzed during each
round of sampling.
Although sampling personnel and analytical
laboratories are different for each site, a high
degree of uniformity in methods used is assured by
State regulations which govern environmental
monitoring at solid waste landfills.
In this study, data for selected parameters was
pooled from a large number of sites to develop a basis
for characterizing ambient groundwater quality
variability on a regional basis.
Parameters selected for this study are those
which are considered to be the most useful in
detecting landfill-derived groundwater contamination
and include alkalinity, ammonia, arsenic, chloride,
chemical oxygen demand, hardness, iron, manganese,
phenols and total dissolved solids.
Comparisons are made with data from monitoring
wells downgradient of the landfills and with other
available data sets. Special emphasis is placed on
whether parameters exceed applicable water quality
standards in ambient groundwater and whether the
parameters selected are reliable indicators of
landfill-derived groundwater contamination. This study
should be particularly useful in cases where
topography, property boundaries or other site
constraints make it impossible to site a valid
upgradient monitoring point or where groundwater
quality impact assessments must be made using a single
monitoring point.