| With
a combined total of over 80 years of remediation experience, StoneHill
employees have selected and applied remediation strategies to address
numerous contaminant types in many different substrates including
soil, surface water, groundwater, sediment, structures, and indoor
air. StoneHill employees have extensive experience with remediation
of sites impacted with various petroleum distillates including gasoline,
diesel fuel, No. 2 fuel oil, No. 6 oil, waste oil, and mineral oil
dielectric fluid, as well as individual petroleum compounds including
benzene, methyl tertiary-butyl ether (MTBE), polynuclear aromatic
hydrocarbons (PAHs), and naphthalene. In addition, StoneHill has
experience remediating dense non-aqueous phase liquid (DNAPL) and
dissolved chlorinated solvents in bedrock and unconsolidated formations.
StoneHill also has designed and implemented remedial plans for soils,
sediments and urban fill sites impacted with lead, arsenic, chromium,
polychlorinated biphenyls (PCBs), and PAHs.
The remediation technology implemented is based
on site-specific chemical and physical characteristics, the nature
of the contaminant and migration pathways, regulatory requirements,
insurance coverage considerations, and optimal time frames. In light
of these considerations, StoneHill has experience with both traditional
methods and new innovative treatment methodologies which may be
appropriate in various scenarios. The traditional extraction technologies
for soil and groundwater include excavation of contaminated soils,
groundwater pumping and treatment, soil vapor extraction, air sparging,
high volume/low vacuum sub-slab vapor collection systems, and interceptor/recovery
trench collection systems. These technologies may be coupled with
standard treatment technologies including oil/water separators,
settling tanks, granular activated carbon (GAC), air stripping,
and UV irradiation systems, all of which have been employed by StoneHill.
StoneHill owns a customized mobile trailer equipped with product
recovery and water treatment equipment for rapid and cost effective
deployment to spill sites where groundwater has been impacted.
In some cases monitored natural attenuation (MNA)
or enhanced MNA is a more appropriate response action than implementing
one of the above techniques. MNA includes the regular monitoring
and testing of dissolved phase groundwater contaminants to ensure
natural in-situ degradation processes are reducing the contaminants
of concern. In an enhanced MNA program, biological degradation processes
are enhanced to more rapidly degrade the contaminants. Enhancement
technologies include nutrient injection, oxygenated water infiltration,
oxygen releasing products, and oxygen diffusion systems.
Selected Project Summaries
RESIDENTIAL FUEL OIL RELEASE,
Lunenburg, MA
Fuel Oil Spill Cleanup
|
A release of
heating oil throughout the basement impacted air, soil and
|
groundwater
at this residence. Severe winter weather worsened some conditions
and made completion of response actions very difficult in
this case. As the spill occurred in the early winter, the
air inside the home was quickly heavily impacted with fuel
oil vapors as the |
|
| forced hot air heating
system intake was in the basement, forcing the owners to
move out of the home. This situation was resolved owners
to move out of the home. This situation was resolved within
a few days by installation of a vapor barrier in the crawl
space and redesign of the heating system to collect exterior
air rather than recycle indoor air. In doing so, oil vapors
were eliminated from the living space of the home. Fuel
oil floating on water in the basement and outside the residence
was removed using a vacuum truck and the fuel oil impacted
soil floor of the basement was removed using a vactor truck.
The owner’s bedrock water supply well and a neighbor’s
dug well were located 50 feet downgradient of the release
location. Therefore, groundwater impacted with fuel oil
product and dissolved phase fuel oil constituents was pumped
to prevent impacts to the water supply wells and minimize
the movement of contamination. Contaminated water was treated
using StoneHill’s mobile groundwater treatment trailer.
An emergency discharge permit was obtained from the U.S.
EPA and treated groundwater was discharged to a catch basin
located in the street. Despite nature’s repeated attempts
to freeze the trailer treatment system, approximately 175,000
gallons of contaminated groundwater were treated over a
four month period. Groundwater quality improved to meet
Massachusetts groundwater quality standards within six months. |
FORMER PIG FARM/SAW MILL,
Central MA
Soil and Sediment Remediation
|
A 62-acre property formerly
used as part of a farm homestead, apple orchard, saw mill,
and pig farm since 1910, was impacted by the on-site |
|
burial of solid wastes,
farm waste, and 55-gallon drums containing waste paint during
the 1970's and 1980’s. The primary contaminants of
concern at the Site included arsenic in on-site stream sediments,
polynuclear aromatic hydrocarbons (PAHs) in large a volume
of fill |
| soils, and
waste paint residuals in soil. A Massachusetts Phase II
Comprehensive Site Investigation completed by StoneHill
identified that the arsenic in sediment was the result of
decades of natural arsenic precipitating with iron oxides,
and the PAHs in soil were associated with coal and wood
ash. As such, both of these contaminants were considered
local background and exempt for Massachusetts Contingency
Plan response action requirements. However, due to the possible
future residential use of the property, voluntary remedial
measures were undertaken to eliminate or minimize the potential
for direct human contact with PAHs in soils or arsenic in
sediments. The response actions were completed as a continuation
of Immediate Response Actions (IRAs) initiated by consultants
previously involved with the site. In the case of the PAH
impacted soils, large rocks and cobbles were screened from
the soil to reduce the total soil volume and the soil was
used to reclaim an on-site gravel pit area. Several feet
of clean fill were then placed over the PAH impacted soils
to complete the reclamation. In the case of the arsenic
in sediment along the brook, the material exhibiting the
highest arsenic concentrations was selectively removed by
vacuuming the sediment, thereby avoiding the need to enter
the brook area with heavy equipment, minimizing the impacts
to the stream environment. The former waste paint drum disposal
area was remediated by excavation and off site disposal
of soil exhibiting paint residuals. Finally, groundwater
quality data collected from an extensive network of overburden
and bedrock groundwater monitoring wells did not detect
exceedances of applicable groundwater standards. Therefore,
a condition of no significant risk was achieved at the site
and a Class A-2 Response Action Outcome (RAO) Statement
was filed with the MADEP. The most significant feature of
this project was that StoneHill’s common sense approach,
combined with comprehensive data collection, allowed the
successful closure of the site at a cost significantly less
than projected by other parties previously involved with
the site. A MADEP representative indicated that they were
impressed by the level of data collection used to decipher
contaminant origins and subsequently support the selection
of remedial alternatives. |
RESIDENTIAL FUEL OIL RELEASE, Whitman,
MA
Fuel Oil Spill Cleanup |
| Approximately 200 gallons
of No. 2 fuel oil leaked from an above ground residential
fuel tank onto the concrete basement floor and seeped into
the ground beneath the residence. Following an initial site
visit on behalf of the homeowner’s insurance company,
StoneHill conducted a Geoprobe™ investigation to assess
whether the release threatened to impact third party or
adjacent properties. The investigation identified a lens
of fuel oil migrating towards the property boundary and
a significant threat of third party impacts. Subsequently,
StoneHill was contracted by the homeowner |
| to manage the remediation
of the fuel oil release which included the removal of 300
tons of oil contaminated soil, recovery of fuel oil floating
on the water table, and pumping and treatment of contaminated
groundwater. Contaminated groundwater was pumped |
 |
through two
activated carbon drums and discharged to the Whitman sanitary
sewer system under an emergency discharge permit. Background
soil conditions were achieved in all but a small area where
removal of residually impacted soil beneath and adjacent
to the residence foundation was not reasonably feasible.
Field activities were completed and the disturbed areas
landscaped within four weeks of project initiation. |
600 State Street, Suite 2
Portsmouth, NH 03801
Telephone: 603-433-1935
Toll Free: 1-800-639-4503
Fax: 603-433-1942
info@stonehillenvironmental.com
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