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A
Pilot Study of Passive Diffusion Bag (PDB) Sampling in a
Fractured Bedrock Environment
Thomas
W. Biolsi, Steven G. Feldmann, and Barbara A. O’Grady,
EA Engineering, Science, and Technology, Inc., 485 Route 1
South, Building C, Suite 260, Iselin, New Jersey 08830,
Tel: 732-404-9370, Fax: 732-404-9382
Jeffery M. Dale, United States Navy, Engineering Field
Activity Northeast, Naval Facilities Engineering Command,
10 Industrial Highway, Mail Stop No. 82, Lester,
Pennsylvania 19113, Tel: 610-595-0567, Fax: 610-595-0555
In a
joint effort between the Navy, United States Geological
Survey, and EA Engineering, a pilot study of passive
diffusion bag (PDB) sampling was conducted at the former
Naval Air Warfare Center in Trenton, New Jersey.
The Navy currently operates and maintains a
comprehensive ground-water extraction and treatment system
for volatile organic compounds (VOCs) and ten metals at
the site. The
Navy sought to evaluate a New Jersey Department of
Environmental Protection (NJDEP)-acceptable ground-water
sampling method that minimizes sampling costs and the
treatment of purge water, without sacrificing data
quality. Research
of sampling options led to the implementation of a pilot
study on the use of PDB samplers.
The use of PDB samplers substantially reduces
equipment and labor costs and produces virtually no
investigation-derived waste, as compared to conventional
purging and sampling techniques.
However, unlike typical PDB samplers that are
usually constructed of polyethylene-based material and
used to monitor for VOCs only, a regenerated
cellulose-based material was used in this PDB pilot study
in an attempt to also monitor inorganic parameters.
Samples from nine bedrock wells, representing a
wide range of trichloroethene concentrations, were
collected using PDB samplers, the Environmental Protection
Agency’s low-flow method, and a modified version of the
standard 3 to 5 well-volume purge method in March 2000 and
March 2001. The
majority of the organic data indicate that the PDB
samplers yielded similar results to conventional purging
and sampling techniques.
Even though only minor sporadic concentrations of
inorganic parameters were reported above the applicable
reporting limits, similar results were observed for
several metals including barium and manganese using the
three sampling methods.
To gain regulatory acceptance by the NJDEP,
additional data are being collected to further support the
effectiveness of the PDB sampling technique for inorganic
constituents. The
results of the assessments made to date will be presented
for discussion.
Correlation
of Field Analytical Detectors in the Analysis of Soil
Contaminated with Diesel Fuel
Clayton
J. Clark II, Dept. of Civil & Coastal Engineering,
University of Florida, P.O. Box 116580, Gainesville, FL
32611, Tel: 352-392-9537 ext.1440, Fax: 352-392-3394,
Email: clark@ce.ufl.edu
Joseph J. Delfino, Dept. of Environmental Engineering
Sciences, University of Florida, P.O. Box 116450,
Gainesville, FL 32611, Tel: 352-392-9377, Fax:
352-392-3076, Email: jdelf@eng.ufl.edu
Analysis
of soil by field instrumentation is widely used for
preliminary soil contamination detection and site
delineation. Research
was conducted to determine if there is a correlation
between the data gathered by field analytical instruments
in analyzing soil contaminated with diesel fuel.
One instrument was equipped with a flame ionization
detector (FID) and the other a photoionization detector (PID).
The results showed that the concentration readings
of the PID and FID displayed a linear relationship (R2
= 0.94) for soil recently contaminated with diesel fuel.
However, for soil containing weathered diesel fuel
in the field, a logarithmic relationship between the PID
and FID readings was displayed.
It was also determined by laboratory
experimentation that the PID and FID readings both
exhibited log-linear decreases over time for uncovered
diesel fuel contaminated soil. Analysis for the
composition of diesel fuel, by volume, was also derived
for the diesel fuel used in this research and it was found
that the targeted volatile and semivolatile compared
favorably with estimates found in the literature.
It was concluded that the PID and FID can both
individually be used to evaluate soil contaminated by
diesel fuel and might be interchangeable depending upon
the need of the researcher.
EPA
Performance Study for Field Measurement of Total Petroleum
Hydrocarbons using Ultraviolet Fluorescence Technology
Steve
Greason, Sitelab Corporation, 27 Greensboro Road, Hanover,
NH 03755,
Tel: 603-643-7800, Fax:
603-643-7900
The
Sitelab UVF-3100 portable test kit was demonstrated under
the U.S. Environmental Protection Agency Superfund
Innovative Technology Program from 1999 to 2001.
The purpose of the demonstration was to collect
reliable performance and cost data for the UVF-3100 and
six other field measurement devices for total petroleum
hydrocarbons (TPH) in soil.
In addition to assessing ease of device operation,
the key objectives of the demonstration included
determining the (1) method detection limit, (2) accuracy
and precision, (3) effect of interferents and soil
moisture content on TPH measurement, (4) sample
throughput, and (5) TPH measurement costs for each device.
The demonstration involved analysis of both
performance evaluation samples and environmental samples
collected in five areas contaminated with gasoline,
diesel, lubricating oil, or other petroleum products.
The performance and cost results for a given field
measurement device were compared to those for an off-site
laboratory reference method, “Test Methods for
Evaluating Solid Waste” (SW-846) Method 8015B
(modified).
During
the demonstration, siteLAB required less than 38 hours for
TPH measurement of 212 samples.
The TPH measurement costs were as low as $7,090 for
Sitelab’s UVF-3100 rental option compared to $42,500 for
the reference method.
The method detection limits were determined to be
3.4 and 6.32 milligrams per kilogram for the UVF-3100 and
reference method, respectively.
Sitelab was also the only developer who analyzed
the samples for both GRO and DRO hydrocarbons separately
(like the laboratory).
EPA reported the UVF-3100 exhibited good accuracy
and precision, ease of use, and lack of sensitivity to
interferents that are not petroleum hydrocarbons.
The demonstration findings collectively indicated
that the UVF-3100 is a reliable field measurement device
for TPH in soil.
A series
of ten sub-posters illustrating Sitelab’s successful
performance testing the SITE samples will be presented
using data and references taken directly from the EPA’s
Innovative Technology Verification Report (ITVR).
Analysis
of Volatile Organics in Produce Using Solid Phase
Microextraction and GC/MS
C.K.
Tan, Ph.D., Southwest Research Institute, 6220 Culebra
Rd., San Antonio, Texas 78238, Tel:
210-522-2356
Kevin Shannon, Southwest Research Institute, 6220 Culebra
Rd., San Antonio, Texas 78238, Tel: 210-522-3041
Robert Acosta, Southwest Research Institute, 6220 Culebra
Rd., San Antonio, Texas 78238, Tel: 210-522-3840
Jesse Rodriguez, Southwest Research Institute, 6220
Culebra Rd., San Antonio, Texas 78238, Tel: 210-522-3840
Ron Porter, Ph.D., MitreTek, 13526 George Rd., San
Antonio, Texas 78230, Tel: 210-479-0478
Public
concern has recently focused on the potential impact of a
contaminated shallow aquifer on fruit- and nut-bearing
trees and plants drawing upon the contaminated aquifer as
a source of hydration.
Residents who harvest and consumes these fruits and
nuts from gardens and indigenous plant species may risk
exposure to harmful chemicals.
An effort was undertaken by Southwest Research
Institute (SwRI) to detect trace levels of volatile
organic chemicals in fresh produce using solid phase
microextraction (SPE) and gas chromatography and mass
spectrometry (GC/MS).
Previous
efforts to analyze produce and other foodstuffs for
volatile organics have relied upon the use of cryogen to
prevent target compound concentration losses during
extraction and/or homogenization.
However, the effectiveness of the cryogen in
retaining the volatile organic compounds, especially those
having low molecular weights and low boiling points, was
difficult to assess.
The challenge was to innovate a technique that
overcomes the weaknesses of the cryogen approach.
Instead
of submersion of the produce samples in liquid nitrogen
then homogenizing in an industrial grinder or piercing the
produce samples and submersion in salty water, the whole
produce sample is weighed and transferred to a stainless
steel bender fitted with an airtight sealed lid. Standards
and heated water (to aid in volatilization) are spiked
through a septum in the sampling port of the blender lid
prior to high-speed homogenization, which drives target
volatile organics into the contained headspace.
A needle-borne SPME fiber is introduced through the
septum and exposed to the headspace, allowing for capture
of volatile organics.
The needle/SPME fiber assembly is withdrawn from
the blender and injected into the GC/MS.
The SPME
approach has notable advantages over the other methods.
Since the entire produce sample is homogenized in a
sealed container, compound concentration loss is
minimized. Extraction-to-analysis
times are reduced considerably.
Detection limits are lower for a wide range of
compounds and sample sizes.
Laboratory
Determination of Diffusion Coefficient of Contaminant Ions
using Clay Soil
Xi
Yong-hui, Lecture, Master, School of Civil Engineering,
Tongji University, 1239 Siping Road, Shanghai, 200092,
China. Tel: 0086-021-65111745
Ren Jie , Master , Associate Professor, State
Key-Laboratory of Concrete Research, School of Material
Science and Engineering, Tongji University, 1239 Siping
Road, Shanghai 200092, China, Tel:
0086-021-65989010
Hu Zhong-xiong, Professor, School of Civil Engineering,
Tongji University, 1239 Siping Road, Shanghai, 200092,
China, Tel: 0086-021-65635001
This
paper describes a special laboratory device to determine
diffusion coefficients of contaminant ions using clay soil
.The technique is illustrated with a number of laboratory
tests involving diffusion migration of contaminants
through clay soil from Shanghai, China. The contaminants
used in these tests are solutions of inorganic compounds
(e.g., NaCl, CaCl2, KCl,ZnSO4,CuSO4
and so on). The device described in this paper is a
rectangle box made up of polyethylene plastic plates of
0.3cm thickness, which have quality of good chemical
stability. The device is divided into three parts by two
polyethylene porous plates. The middle part contains the
soil sample, and the other two parts contain source of
contaminants and distilled water respectively. The water
level of the two parts apart from the soil sample is
equal. Contaminant ions migrate from the source solution
to the distilled water through soil samples. The
contaminant migration in these tests is controlled mainly
by diffusion. The
results are consistent with the equation developed from
the Fick’s second law, that is, the logarithm of
concentration is linear with the square of diffusive
distance. The concentration of contaminant ions at
different specified distance of a soil sample is measured
after a definite diffusion time .The data are arranged in
a semi-logarithm co-ordinate system. The Diffusion
coefficient can be calculated from the slope of a line. It
is found from the experiment results that the diffusion
coefficients of anions (e.g., Cl-) through the
clay are much larger than those of cations (e.g., Ca2+,
Zn2+, Ni2+, Cd2+), and
there are obvious relations between diameters and electric
conductivities of divalent cations and diffusion
coefficients. The results also show that adding of cement
to soil reduces the diffusion velocity of contaminant ions
greatly.
Large
Volume Sample Stacking For Analysis Of EDTA By Capillary
Electrophoresis
Lifeng
Zhang, Centre for Advanced Water Technology, 18 Nanyang
Drive, Singapore 637723
, Tel:
65-6794-3715, Fax: 65-6794-2791
Zhiwei Zhu, Centre for Advanced Water Technology, 18
Nanyang Drive, Singapore 637723, Tel: 65-6794-3865, Fax:
65-6794-2791
Arun Marimuthu, Centre for Advanced Water Technology, 18
Nanyang Drive, Singapore 637723, Tel: 65-6794-3718, Fax:
65-6794-2791
Zhaoguang Yang, Centre for Advanced Water Technology, 18
Nanyang Drive, Singapore 637723, Tel: 65-6794-1561, Fax:
65-6794-2791
The
widespread use of ethylenediaminetetraacetic acid (EDTA)
has requested an urgent monitoring program regarding
surface and drinking water. Analysing EDTA at low-level
concentrations (such as mg/L
in the environmental samples) is quite complex using the
conventional GC/MS or HPLC methods. In this study, a
simple, quick and sensitive capillary electrophoretic
technique -large volume stacking using the EOF pump (LVSEP)-
has been developed for determining EDTA in drinking water
for the first time. It is based on a precapillary
complexation of EDTA with Fe(III) ions, followed by large
volume sample stacking and direct UV detection at 258 nm.
The curve of peak response versus concentration was linear
between 5.0 and 600.0 mg/L,
as well as between 0.7 and 30.0 mg/L. The regression
coefficients were 0.9988 and 0.9990, respectively. The
detection limit of current technique for EDTA analysis was
0.2 mg/L
with additional 10-fold preconcentration procedure, based
on the signal-to-noise ratio of 3. As opposed to the
classical CE method, a 1000-fold concentration factor
could be smoothly achieved on this LVSEP method. To the
best of our knowledge, it represents the highest
sensitivity for EDTA analysis via CE. Several drinking
water samples were tested by this novel method with
satisfactory results.
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