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2003 Buzzards Bay Oil Spill: History and Cleanup Under the MCP
Rich Packard, MassDEP, Hyannis, MA
Kevin D. Trainer, GeoInsight, Inc., Westford, MA
Richard J. Wozmak, EnviroLogic, LLC, Londonderry, NH
Swanson Creek
(MD) Oil Spill: Response and Restoration
Erich R. Gundlach, E-Tech International Inc., New
Paltz, NY
The FAST:
MassDEP Field Assessment and
Support Team
John
J. Fitzgerald, MassDEP, Wilmington,
MA
Tankers, Tankers
and More Tankers
Dan Crafton, MassDEP,
Lakeville, MA
Dave Slowick, MassDEP, Springfield, MA
Kingsley Ndi, MassDEP, Wilmington, MA
Nick Child, MassDEP, Worcester, MA
Biofuels and the
Environment
Gregory Wilson, U.S. EPA, Washington,
DC
Response Considerations for Releases of Ethanol-Blended
Fuels
Curtis C. Stanley,
Shell Global Solutions (US) Inc.,
Houston,
TX
Brent P. Stafford,
Shell Global Solutions (US) Inc.
2003
Buzzards Bay
Oil Spill: History and Cleanup under the MCP
Richard F. Packard,
MassDEP, Oil Spill Prevention and Response Program, 973
Iyannough Rd, Hyannis, MA 02601, USA, Tel: 508-946-2865,
Email: richard.packard@state.ma.us
Kevin D. Trainer,
C.P.G., P.G., LSP, GeoInsight, Inc., 319 Littleton Road, Suite 105,
Westford,
MA 01886
USA, Tel:
978-692-1114, Email: kdtrainer@geoinc.com
Richard J. Wozmak,
P.E., P.H., LSP, LEP, EnviroLogic, LLC, 50 Nausha Road,
Londonderry, NH 03053, USA,
Tel: 603-421-2777, Email: rwozmak@envirologicllc.com
In April 2003 a tank barge carrying
more than 4 million gallons of No. 6 fuel oil grounded
at the entrance to Buzzards Bay.
The resulting spill of approximately 100,000
gallons was the second largest spill in
Buzzards Bay history, with more than 93
miles of coastline affected.
Buzzards Bay is heavily used for commercial and
recreational purposes, and portions of
Buzzards Bay
are sensitive habitat for threatened or endangered
species. As
with any marine oil spill of this size, the response
involved the coordinated efforts and resources of
federal, state, local, and private agencies.
However, unlike spills in other jurisdictions,
oil spill response and cleanup in Massachusetts utilizes a Licensed Site Professional (LSP)
to ensure compliance with
Massachusetts
cleanup regulations.
This presentation will discuss the spill itself,
the transition of the spill response from the emergency
cleanup directed by Unified Command to LSP-directed
comprehensive response actions, development of clean-up
approaches, challenges in defining “significant risk to
public welfare” and public involvement issues during the
spill response.
Swanson Creek (MD) Oil Spill: Response and Restoration
Erich R. Gundlach, E-Tech
International Inc., 15 River Park Drive,
New
Paltz, NY 12561,
Email:
ErichEti@cs.com
A pipeline break on 7 April 2000
spilled 126,000–139,000 gallons of No. 2 and No. 6 fuel
oils
into the brackish water environments of the upper Patuxent River, Maryland.
Particularly impacted was a large marsh area
adjacent to the break. This presentation will present an
overview of the spill management system used to combat
the spill and recover the oil, marsh planting and
restoration implemented during the response, cleanup end
points used by the State of Maryland to sign off on
shoreline habitats as requiring no further treatment,
and the results of the damage assessment process
implemented by state and federal trustees
Marsh cleanup operations guided by
U.S. EPA included mechanical trenching, limited
low-to-moderate pressure flushing, hand recovery using
sorbent pads and working from placed boardwalks, and the
aerial application of fertilizer (bio-stimulation).
During the response, the damaged marsh was
replanted with a total of 22,896 plugs of
Spartina
alterniflora and 2,880 plugs of
S. patens.
Vegetative recovery was approximately 85% after
year 1 and 99% after year 2.
Despite the successful replanting, damage
assessments conducted by the natural resource trustees
gave little credit for the restoration of the oiled
marsh area.
Other aspects of the damage valuation for the spill will
also be presented.
The FAST:
MassDEP Field
Assessment and Support Team
John J. Fitzgerald, Northeast Regional Office, MassDEP,
205B Lowell Street,
Wilmington,
MA
01887, Tel:
978-694-3308, Email: John.j.fitzgerald@state.ma.us
Many response agencies
and contractors have recognized the value of conducting
timely on-scene analysis of environmental media during
spill events and other environmental emergencies.
This often involves the deployment of a “mobile
laboratory” as well as an assortment of specialized
instrumentation and equipment.
The optimal use of these resources depends,
however, on the development and implementation of
effective strategies, systems and procedures.
MassDEP has
recently enhanced its capabilities in this regard by
designing and procuring a well-equipped mobile lab
vehicle (aka the FAST vehicle.)
Effective utilization of this new asset will be
based on the field response principles of the Incident
Command System (NIMS/ICS) combined with the “Triad”
approach to data acquisition and utilization, with
particular emphasis on systematic planning, dynamic work
plans, and real-time/near-real-time measurement
techniques.
This presentation will describe the capabilities of the
FAST vehicle and explain how it has been used during
recent emergency responses, and how it could have been
used on earlier ones.
Tankers,
Tankers and More Tankers
Dan Crafton, MassDEP, Lakeville, MA
Dave Slowick, MassDEP, Springfield, MA
Kingsley Ndi, MassDEP, Wilmington, MA
Nick Child, MassDEP, Worcester, MA
Large quantities of petroleum products are transported on roadways
throughout
Massachusetts
every day via tanker trailer truck.
Occasionally those trucks crash and cause large
spills that result in a variety of environmental and
safety hazards. Have you ever wondered how those get
cleaned up?
While the commuters are dealing with the traffic snarls,
environmental responders are working with local, state
and federal responders to address explosions,
neighborhood evacuations, fish-kills, and damage to
sensitive environments. MassDEP Emergency Response staff
will present several case studies illustrating a range
of recent tanker trailer petroleum spills that affected
wetlands, waterways and water supplies, and discuss
short- and long-term assessment and cleanup responses.
Biofuels and the
Environment
Gregory Wilson, Ph.D., U.S.
Environmental Protection Agency, Office of Emergency
Management (OEM), Regulation and Policy Development
Division, 1200 Pennsylvania Ave., NW (5104A),
Washington, DC 20460, Tel: 202-564-7989, Fax:
202-564-2625
Congress recently passed legislation
mandating increased usage of transportation-related
biofuels, which have prompted a phenomenal growth in
biofuel-related infrastructure.
Growth in the development of biofuels,
particularly biodiesel and ethanol, is raising a number
of questions about how biofuels behave in the
environment
The refining and distribution
infrastructure used for biofuels have both similarities
and differences from the infrastructure used for
conventional petroleum fuels.
Consequently, expansion of the biofuel sector
will require tailored response capabilities.
While the attention has so far been focused
primarily on some of the environmental benefits of
expanding use of biofuels, there also needs to be
greater clarity on how existing environmental response
capabilities apply to these fuels.
This presentation summarizes recent
energy legislation driving biofuel production and
distribution.
It also discusses the relationship between
biofuels and conventional fuels, focusing specifically
on those issues related to responding to biofuel
incidences.
Finally, the presentation discusses real-world case
studies on biofuel-related responses.
Response Considerations for Releases of Ethanol-Blended
Fuels
Curtis
C. Stanley, Shell Global Solutions (US) Inc., HSE
Consultancy - Soil and Groundwater Management,
Westhollow Technology Center, EC-218, 3333 Highway 6
South, Houston, TX 77082-3101, Tel: 281-544-7675 Fax:
281-544-8727, Email: Curtis.Stanley@Shell.com
Brent P. Stafford, PhD, PG, Shell Global
Solutions (US) Inc.
Concerns regarding
potential impacts to safety and environmental
resources from releases of ethanol-blended fuels along
with appropriate response measures have increased due to
the rise in use and transport of ethanol fuel
blends. Potential release scenarios include
ethanol-blended gasoline (10-20% v/v ethanol) or E85
(85% v/v ethanol) leaking from underground storage tanks
at service stations, and fuel grade (denatured) ethanol
(95-97.5% v/v ethanol) spills during transport or after
reaching bulk terminals.
The hydrophilic properties of
ethanol drive the environmental transport of these fuels
and influence the locations and geometries of generated
non-aqueous phase liquid (NAPL) secondary source zones
from the gasoline or denaturant fuel fractions. Also,
due to the ability of highly concentrated ethanol to
dissolve NAPL, large releases of fuel grade ethanol may
exacerbate impacts to groundwater or surface waters at
sites with pre-existing NAPL in soils or sediments.
As a result, commonly understood and utilized
conceptual models used as tools for site management for
released (non-ethanol blended) fuels may be inadequate
for some ethanol fuel blends.
Finally, considerations related to secondary
conditions (e.g. methane generation, BOD in surface
water, etc.) is discussed.
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