THE ENVIRONMENTAL TECHNOLOGY VERIFICATION

PROGRAM,

m

Sandia
National

Laboratories

ETV JOINT VERIFICATION STATEMENT

TECHNOLOGY TYPE:
APPLICATION:

GROUNDWATER SAMPLING TECHNOLOGIES
VOC-CONTAMINATED WATER SAMPLING

TECHNOLOGY NAME: SamplEase Bladder Pump - Model SP15T36

COMPANY:
ADDRESS:

WEBSITE:
EMAIL:

Clean Environment Equipment

1133 Seventh St.

Oakland, CA 94607

PHONE: (510) 891-0880
FAX: (510) 444-6789

www.cee.com
service@cee.com

The U.S. Environmental Protection Agency (EPA) has created the Environmental Technology
Verification Program (ETV) to facilitate the deployment of innovative or improved environmental
technologies through performance verification and dissemination of information. The goal of the ETV
Program is to further environmental protection by substantially accelerating the acceptance and use of
improved and cost-effective technologies. ETV seeks to achieve this goal by providing high-quality,
peer-reviewed data on technology performance to those involved in the design, distribution, financing,
permitting, purchase, and use of environmental technologies.

ETV works in partnership with recognized standards and testing organizations and stakeholder groups
consisting of regulators, buyers, and vendor organizations, with the full participation of individual
technology developers. The program evaluates the performance of innovative technologies by
developing test plans that are responsive to the needs of stakeholders, conducting field or laboratory tests
(as appropriate), collecting and analyzing data, and preparing peer-reviewed reports. All evaluations are
conducted in accordance with rigorous quality assurance protocols to ensure that data of known and
adequate quality are generated and that the results are defensible.

The Site Characterization and Monitoring Technologies Pilot, one of 12 technology areas under ETV, is
administered by EPA's National Exposure Research Laboratory. Sandia National Laboratories, a
Department of Energy laboratory, is one of the verification testing organizations within the ETV Site
Characterization and Monitoring Technologies Pilot. Sandia collaborated with personnel from the US
Geological Survey (USGS) to conduct a verification study of groundwater sampling technologies. This
verification statement provides a summary of the results from a verification test of the SamplEase
bladder pump and pneumatic controller manufactured by Clean Environment Equipment.

EPA-VS-SCM-42 The accompanying notice is an integral part of this verification statement.

August 2000


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DEMONSTRATION DESCRIPTION

In August 1999, the performance of six groundwater sampling technologies was evaluated at the US
Geological Survey Hydrological Instrumentation Facility at the National Aeronautics and Space
Administration (NASA) Stennis Space Center in southwestern Mississippi. Each technology was
independently evaluated in order to assess its performance in the collection of volatile organic
compound- (VOC) contaminated water.

The verification test design incorporated the use of a 5-inch-diameter, 100-foot standpipe at the USGS
facility. The standpipe, serving as an "aboveground" well, was filled with tap water spiked with various
concentration levels of six target volatile organic compounds. The target compounds (1,2-
dichloroethane, 1,1-dichloroethene, trichloroethene, benzene, 1,1,2-trichloroethane, and
tetrachloroethene) were chosen to represent the range of VOC volatility likely to be encountered in
normal sampler use. Water sampling ports along the exterior of the standpipe were used to collect
reference samples at the same time that groundwater sampling technologies collected samples from the
interior of the pipe. A total of seven trials were carried out at the standpipe. The trials included the
collection of low (-20 |Jg/L) and high (-200 |Jg/L) concentrations of the six target VOC compounds in
water at sampler depths ranging from 17 to 91 feet. A blank sampling trial and an optional "clean-
through-dirty" test were also included in the test matrix. The "clean-through-dirty" test was included to
investigate the potential of contaminant carryover as a sampler is lowered through a "dirty" (high VOC
concentration) layer of water in order to sample an underlying "clean" (low VOC concentration) layer.
The test was optional for samplers such as the SamplEase bladder pump, which is designed for
permanent deployment in a single monitoring well.

The standpipe trials were supplemented with additional trials at groundwater monitoring wells in the
vicinity of sites with VOC-contaminated groundwater at the NASA Stennis facility. The technologies
were deployed in a number of 2-inch and 4-inch wells, along with colocated submersible electric gear
pumps as reference samplers. The principal contaminant at the onsite monitoring wells was
trichloroethene. The onsite monitoring provided an opportunity to observe the operation of the sampling
system under typical field-use conditions.

All technology and reference samples were analyzed by two identical field-portable gas chromatograph-
mass spectrometer (GC/MS) systems that were located at the test site during the verification tests. The
GC/MS analytical method used was a variation of EPA Method 8260 purge-and-trap GC/MS,
incorporating a headspace sampling system in lieu of a purge-and-trap unit. The overall performance of
the groundwater sampling technologies was assessed by evaluating sampler precision and comparability
with reference samples. Other logistical aspects of field deployment and potential applications of the
technology were also considered in the evaluation.

Details of the demonstration, including an evaluation of the sampler's performance, may be found in the
report entitled Environmental Technology Verification Report: Clean Environment Equipment,
SamplEase Bladder Pump, EPA/600/R-00/078.

TECHNOLOGY DESCRIPTION

The SamplEase is a bladder pump consisting of an internal flexible Teflon bladder that is positioned within
a rigid stainless steel pump body. The ends of the pump are also constructed of Teflon. The inner bladder
is equipped with one-way inlet and outlet valves and passively fills with water when the pump is at depth in
the well as a result of the hydrostatic pressure exerted by the surrounding water column. Following the fill
cycle, compressed air or nitrogen from a cylinder or compressor at the wellhead is driven down to the pump
through tubing to compress the bladder, thus driving the water sample up to the surface through a second
tubing line. The pumping sequence consists of repeated fill-compress cycles, using a pneumatic controller
positioned at the wellhead. The controller is used to vary the duration and frequency of the fill-compress
cycles in order to deliver the desired sample flow rate at the wellhead. The bladder design offers

EPA-VS-SCM-42 The accompanying notice is an integral part of this verification statement.

August 2000


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the advantage of minimizing sample turbulence, which can result in loss of VOCs in the sample, as well as
eliminating contact of the water sample with the compressed air or nitrogen used to lift the sample to the
surface.

Clean Environment Equipment offers a line of bladder pumps manufactured with various materials. The
pump tested during this evaluation was the Model SP15T36, which uses polytetrafluoroethylene (Teflon)
for the bladder and 316 stainless steel for the pump body, fittings, and intake screen. The pump and intake
screen is 40 inches long. The pump diameter is 1.5 inches and its weight is 3.8 pounds. The pump has a
maximum lift capacity of 500 feet, and flow rates are adjustable from less than 100 mL/min to over 5
L/min, depending on pump depth. The pump can draw samples from greater depths using an extended
intake attached to the inlet of the pump.

The Model SC250 controller is a mechanical controller used to regulate the flow of compressed nitrogen,
obtained from a cylinder at the wellhead, to the bladder pump. The controller is weatherproof and is
packaged in a durable case that can be easily hand carried. The controller has overall dimensions of 10 x 9
x 7 inches and a weight of 9.8 pounds. Drive air for the bladder pump can be delivered from compressed
gas cylinders or from a field-portable gasoline- or electric-powered compressor.

The bladder pump's list price is $630 and the controller lists at $1,550. An optional inlet screen is priced at
$50. Teflon-lined polyethylene dual tubing is also a requirement for most VOC sampling applications and
is priced at $1.30 per foot.

VERIFICATION OF PERFORMANCE

The following performance characteristics of the SamplEase bladder pump were observed:

Precision: The precision of the sampler was determined through the collection of a series of replicate
samples from 3 standpipe trials using low (-20 |Jg/L) and high (-200 |Jg/L) VOC concentrations at 17-
foot and 91-foot collection depths. Each trial included 6 target VOCs for a total of 18 cases. SamplEase
bladder pump precision, represented by the relative standard deviation, for all compounds at all
concentrations and sampling depths evaluated in this study, ranged from 5.1 to 24.2%, with a median
value of 11.7%. In 12 cases the relative standard deviation of the SamplEase bladder pump was greater
than the reference, with SamplEase bladder pump precision less than or equal to reference sample
precision in the other 6 cases. The F-ratio test was used to assess whether the observed precision
differences were statistically significant. Test results showed that precision differences between the
SamplEase bladder pump and reference samples were statistically insignificant at the 95% confidence
level in 16 of 18 cases.

Comparability with a Reference: SamplEase bladder pump results from the standpipe trials were
compared with results obtained from reference samples collected at the same time. Both SamplEase and
reference samples were analyzed by the same analytical method using the same GC/MS system.

Sampler comparability is expressed as percent difference relative to the reference data. Sampler
differences for all target VOC compounds at all concentrations and sampler depths in this study ranged
from -16 to 31%, with a median difference of-5%. The t-test for two sample means was used to assess
whether the differences between SamplEase bladder pump and reference sample results were statistically
significant. These tests showed that in 13 of 24 trials, differences were statistically indistinguishable
from 0% at the 95% confidence level. In the remaining 5 cases, statistically significant negative bias was
not in excess of 16%.

Versatility: Sampler versatility is the consistency with which the sampler performed over the range of
target compound volatility, concentration level, and sampling depth. SamplEase bladder pump
performance did not vary with changes in compound, concentration, or sampler depth. Thus, the
SamplEase bladder pump is regarded as a widely versatile sampling device and applicable for sampling
the types of VOCs likely to be encountered under actual field conditions.

EPA-VS-SCM-42 The accompanying notice is an integral part of this verification statement.

August 2000


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Logistical Requirements: The sampler can be deployed and operated in the field by one person. One
day of training is generally adequate to become proficient in the use of the system. The system requires
a source of compressed air or nitrogen at the wellhead, such as a compressed gas cylinder or a gas- or
electric-powered compressor. The SamplEase bladder pump is designed for dedicated use in a single
monitoring well and is not intended for repeated deployment and retrieval in a series of wells.

Overall Evaluation: The results of this verification test show that the SamplEase bladder pump and
associated pneumatic controller can be used to collect VOC-contaminated water samples that are
generally statistically comparable to reference samples when analyzed with the sample method. The
system is designed for use in well sampling programs that incorporate low-volume purge methodologies.

As with any technology selection, the user must determine if this technology is appropriate for the
application and the project data quality objectives. For more information on this and other verified
technologies, visit the ETV web site at http://www.epa.gov/etv.

Gary J. Foley, Ph.D.

Director

National Exposure Research Laboratory
Office of Research and Development

Samuel G. Varnado
Director

Energy and Critical Infrastructure Center
Sandia National Laboratories

NOTICE: EPA verifications are based on evaluations of technology performance under specific, predetermined
criteria and appropriate quality assurance procedures. The EPA and SNL make no expressed or implied
warranties as to the performance of the technology and do not certify that a technology will always operate as
verified. The end user is solely responsible for complying with any and all applicable federal, state, and local
requirements. Mention of commercial product names does not imply endorsement.

EPA-VS-SCM-42 The accompanying notice is an integral part of this verification statement.

August 2000


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