Taking of Marine Mammals Incidental to Specified Activities; Construction of the East Span of the San Francisco-Oakland Bay Bridge, 532-535 [E6-22615]
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Federal Register / Vol. 72, No. 3 / Friday, January 5, 2007 / Notices
(‘‘Continuation Notice’’). Subsequent to
the signature of the Continuation
Notice, we identified an inadvertent
error in the above–referenced notice.
Specifically, the ‘‘Scope of the Order’’
listed in the Continuation Notice was
incorrect. It should read as follows:
Scope of the Order
The merchandise covered by this
order is silicon metal containing at least
96.00 percent but less than 99.99
percent silicon by weight. Also covered
by this antidumping order is silicon
metal containing between 89.00 and
96.00 percent silicon by weight but
which contains more aluminum than
the silicon metal containing at least
96.00 percent but less than 99.99
percent silicon by weight. Silicon metal
is currently provided for under
subheadings 2804.69.10 and 2804.69.50
of the Harmonized Tariff Schedule of
the United States (‘‘HTSUS’’) as a
chemical product, but is commonly
referred to as a metal. Semiconductor
grade silicon (silicon metal containing
by weight not less than 99.99 percent
silicon and provided for in subheading
2804.61.00 of the HTSUS) is not subject
to the order. Although the HTSUS item
numbers are provided for convenience
and for customs purposes, the written
description remains dispositive.
Conclusion
This notice serves solely to correct the
scope as it was detailed in the
Continuation Notice. The Department’s
findings in the Continuation Notice
remain unchanged. This notice is issued
and published in accordance with
section 777(i) of the Tariff Act of 1930,
as amended.
Dated: December 27, 2006.
Stephen J. Claeys,
Deputy Assistant Secretary for Import
Administration.
[FR Doc. E6–22641 Filed 1–4–07; 8:45 am]
BILLING CODE 3510–DS–S
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
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[I.D. 113006A]
Taking of Marine Mammals Incidental
to Specified Activities; Construction of
the East Span of the San FranciscoOakland Bay Bridge
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
AGENCY:
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Notice; proposed authorization
for an incidental take authorization;
request for comments.
ACTION:
SUMMARY: NMFS has received a request
from the California Department of
Transportation (CALTRANS) for
renewal of an authorization to take
small numbers of California sea lions,
Pacific harbor seals, harbor porpoises,
and gray whales, by harassment,
incidental to construction of a
replacement bridge for the East Span of
the San Francisco-Oakland Bay Bridge
(SF-OBB) in California. Under the
Marine Mammal Protection Act
(MMPA), NMFS is requesting comments
on its proposal to issue an authorization
to CALTRANS to incidentally take, by
harassment, small numbers of these
species of pinnipeds and cetaceans
during the next 12 months.
DATES: Comments and information must
be received no later than February 5,
2007.
ADDRESSES: Comments on the
application should be addressed to P.
Michael Payne, Chief, Permits,
Conservation and Education Division,
Office of Protected Resources, National
Marine Fisheries Service, 1315 EastWest Highway, Silver Spring, MD
20910–3225, or by telephoning the
contact listed here. The mailbox address
for providing email comments is
PR1.113006A@noaa.gov. Comments
sent via e-mail, including all
attachments, must not exceed a 10–
megabyte file size. A copy of the 2001
application, the 2006 renewal request,
the January 2005 Marine Mammal and
Acoustic Monitoring report, and the
August 2006 Hydroacoustic
Measurements report may be obtained
by writing to this address or by
telephoning one of the contacts listed
here.
FOR FURTHER INFORMATION CONTACT:
Shane Guan, NMFS, (301) 713–2289, ext
137, or Monica DeAngelis, NMFS, (562)
980–3232.
SUPPLEMENTARY INFORMATION:
Background
Sections 101(a)(5)(A) and (D) of the
MMPA (16 U.S.C. 1361 et seq.) direct
the Secretary of Commerce to allow,
upon request, the incidental, but not
intentional, taking of small numbers of
marine mammals by U.S. citizens who
engage in a specified activity (other than
commercial fishing) within a specified
geographical region if certain findings
are made and either regulations are
issued or, if the taking is limited to
harassment, notice of a proposed
authorization is provided to the public
for review.
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Permission shall be granted if NMFS
finds that the taking will have no more
than a negligible impact on the species
or stock(s) and will not have an
unmitigable adverse impact on the
availability of the species or stock(s) for
subsistence uses and that the
permissible methods of taking and
requirements pertaining to the
mitigation, monitoring, and reporting of
such taking are set forth. NMFS has
defined ‘‘negligible impact’’ in 50 CFR
216.103 as ’’...an impact resulting from
the specified activity that cannot be
reasonably expected to, and is not
reasonably likely to, adversely affect the
species or stock through effects on
annual rates of recruitment or survival.’’
Section 101(a)(5)(D) of the MMPA
established an expedited process by
which citizens of the United States can
apply for an authorization to
incidentally take small numbers of
marine mammals by harassment. Except
with respect to certain activities not
pertinent here, the MMPA defines
‘‘harassment’’ as:
any act of pursuit, torment, or annoyance
which (i) has the potential to injure a marine
mammal or marine mammal stock in the wild
[Level A harassment]; or (ii) has the potential
to disturb a marine mammal or marine
mammal stock in the wild by causing
disruption of behavioral patterns, including,
but not limited to, migration, breathing,
nursing, breeding, feeding, or sheltering
[Level B harassment].
Section 101(a)(5)(D) establishes a 45–
day time limit for NMFS review of an
application followed by a 30–day public
notice and comment period on any
proposed authorizations for the
incidental harassment of small numbers
of marine mammals. Within 45 days of
the close of the comment period, NMFS
must either issue or deny issuance of
the authorization.
Summary of Request
On October 16, 2006, CALTRANS
sumbitted a request to NOAA requesting
renewal of an IHA for the possible
harassment of small numbers of
California sea lions (Zalophus
californianus), Pacific harbor seals
(Phoca vitulina richardsii), harbor
porpoises (Phocoena phocoena), and
gray whales (Eschrichtius robustus)
incidental to construction of a
replacement bridge for the East Span of
the SF-OBB, in San Francisco Bay (SFB
or the Bay), California. An IHA was
issued to CALTRANS for this activity on
April 30, 2006 and it will expire on
April 29, 2007 (71 FR 26750). A detailed
description of the SF-OBB project and
background information on the issuance
of this IHA were provided in the
November 14, 2003 (68 FR 64595)
Federal Register notice and are not
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repeated here. Please refer to that
Federal Register notice.
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Description of the Marine Mammals
Potentially Affected by the Activity
General information on the marine
mammal species found in California
waters can be found in Caretta et al.
(2006), which is available at the
following URL: https://
www.nmfs.noaa.gov/pr/pdfs/sars/
po2005.pdf. Refer to that document for
information on these species.
The marine mammals most likely to
be found in the SF-OBB area are the
California sea lion, Pacific harbor seal,
and harbor porpoise. From December
through May gray whales may also be
present in the SF-OBB area. Information
on California sea lion, harbor seal, and
gray whale was provided in the
November 14, 2003 (68 FR 64595),
Federal Register notice; information on
harbor porpoise was provided in the
January 26, 2006 (71 FR 4352), Federal
Register notice.
Potential Effects on Marine Mammals
and Their Habitat
CALTRANS and NMFS have
determined that open-water pile
driving, as outlined in the project
description, has the potential to result
in behavioral harassment of California
sea lions, Pacific harbor seals, harbor
porpoises, and gray whales that may be
swimming, foraging, or resting in the
project vicinity while pile driving is
being conducted. Pile driving could
potentially harass those few pinnipeds
that are in the water close to the project
site, whether their heads are above or
below the surface.
Based on airborne noise levels
measured and on-site monitoring
conducted during 2004 under the
previous IHA, noise levels from the East
Span project did not result in the
harassment of harbor seals hauled out
on Yerba Buena Island (YBI). Also,
noise levels from the East Span project
are not expected to result in harassment
of the sea lions hauled out at Pier 39 as
airborne and waterborne sound pressure
levels (SPLs) would attenuate to below
harassment levels by the time they reach
that haul-out site, 5.7 km (3.5 miles)
from the project site.
For reasons provided in greater detail
in NMFS’ November 14, 2003 (68 FR
64595) Federal Register notice and in
CALTRANS’ June 2004, January 2005
annual monitoring reports, and marine
mammal observation memoranda
between February and September, 2006,
the East Span Project was resulting in
only small numbers of harbor seals.
Therefore, it is not expected to result in
more than a negligible impact on marine
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mammal stocks and will not have a
significant impact on their habitat. No
pile driving has been commenced since
September 15, 2006. Short-term impacts
to habitat may include minimal
disturbance of the sediment where the
channels are dredged for barge access
and where individual bridge piers are
constructed. Long-term impacts to
marine mammal habitat will be limited
to the footprint of the piles and the
obstruction they will create following
installation. However, this impact is not
considered significant as the marine
mammals can easily swim around the
piles of the new bridge, as they
currently swim around the existing
bridge piers.
Mitigation
The following mitigation measures are
currently required under the existing
IHA to reduce impacts to marine
mammals to the lowest extent
practicable. NMFS proposes to continue
these mitigation measures under a new
IHA, if issued.
Barrier Systems
An air bubble curtain system is
required to be used only when driving
the permanent open-water piles. While
the bubble curtain is required
specifically as a method to reduce
impacts to endangered and threatened
fish species in SFB, it may also provide
some benefit for marine mammals. The
NMFS’ Biological Opinion and the
California Department of Fish and
Game’s (CDFG) 2001 Incidental Take
Permit also allow for the use of other
equally effective methods, such as
cofferdams, as an alternative to the air
bubble curtain system to attenuate the
effects of sound pressure waves on fish
during driving of permanent in-Bay
piles (NMFS 2001; CDFG, 2001). Piers
E–16 through E–7 for both the
eastbound and westbound structures of
the Skyway will be surrounded by
sheet-pile cofferdams, which will be dewatered before the start of pile driving.
De-watered cofferdams are generally
effective sound attenuation devices. For
Piers E3 through E6 of the Skyway and
Pier 1 the Self-Anchored Suspension
span, it is anticipated that cofferdams
will not be used; therefore, a bubble
curtain will surround the piles.
Sound Attenuation
As a result of the determinations
made during the Pile Installation
Demonstration Project (PIDP) restrike
and the investigation at the BeniciaMartinez Bridge, NMFS determined in
2003 that CALTRANS must install an
air bubble curtain for pile driving for the
open-water piles without cofferdams
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located at the SF-OBB. This
specification and configuration of the
air bubble curtain system is described in
pervious Federal Register notice (71 FR
4352, January 26, 2006), and is not
repeated here.
Establishment of Safety/Buffer Zones
A safety zone is to be established and
monitored to include all areas where the
underwater SPLs are anticipated to
equal or exceed 190 dB re 1 microPa
rms (impulse) for pinnipeds. Also, a
180–dB re 1 microPa rms (impulse)
safety zone for gray whales and harbor
porpoises must be established for pile
driving occurring during the gray whale
migration season from December
through May. Prior to commencement of
any pile driving, a preliminary 500–m
(1,640–ft) radius safety zone for
pinnipeds (California sea lions and
Pacific harbor seals) will be established
around the pile driving site, as it was for
the PIDP. Once pile driving begins,
either new safety zones can be
established for the 500 kJ and 1,700 kJ
hammers or the 500 m (1,640 ft) safety
zone can be retained. If new safety
zones are established based on SPL
measurements, NMFS requires that each
new safety zone be based on the most
conservative measurement (i.e., the
largest safety zone configuration). SPLs
will be recorded at the 500–m (1,640–
ft) contour. The safety zone radius for
pinnipeds will then be enlarged or
reduced, depending on the actual
recorded SPLs.
Observers on boats will survey the
safety zone to ensure that no marine
mammals are seen within the zone
before pile driving of a pile segment
begins. If marine mammals are found
within the safety zone, pile driving of
the segment will be delayed until they
move out of the area. If a marine
mammal is seen above water and then
dives below, the contractor will wait 15
minutes and if no marine mammals are
seen by the observer in that time it will
be assumed that the animal has moved
beyond the safety zone. This 15–minute
criterion is based on scientific evidence
that harbor seals in San Francisco Bay
dive for a mean time of 0.50 minutes to
3.33 minutes (Harvey and Torok, 1994),
and the mean diving duration for harbor
porpoises ranges from 44 to 103 seconds
(Westgate et al., 1995). However, due to
the limitations of monitoring from a
boat, there can be no assurance that the
zone will be devoid of all marine
mammals at all times.
Once the pile driving of a segment
begins it cannot be stopped until that
segment has reached its predetermined
depth due to the nature of the sediments
underlying the Bay. If pile driving stops
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and then resumes, it would potentially
have to occur for a longer time and at
increased energy levels. In sum, this
would simply amplify impacts to
marine mammals, as they would endure
potentially higher SPLs for longer
periods of time. Pile segment lengths
and wall thickness have been specially
designed so that when work is stopped
between segments (but not during a
single segment), the pile tip is never
resting in highly resistant sediment
layers. Therefore, because of this
operational situation, if seals, sea lions,
or harbor porpoises enter the safety zone
after pile driving of a segment has
begun, pile driving will continue and
marine mammal observers will monitor
and record marine mammal numbers
and behavior. However, if pile driving
of a segment ceases for 30 minutes or
more and a marine mammal is sighted
within the designated safety zone prior
to commencement of pile driving, the
observer(s) must notify the Resident
Engineer (or other authorized
individual) immediately and follow the
mitigation requirements as outlined
previously in this document.
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Soft Start
It should be recognized that although
marine mammals will be protected from
Level A harassment by establishment of
an air-bubble curtain and marine
mammal observers monitoring a 190–dB
safety zone for pinipeds and 180–dB
safety zone for cetaceans, mitigation
may not be 100 percent effective at all
times in locating marine mammals.
Therefore, in order to provide additional
protection to marine mammals near the
project area by allowing marine
mammals to vacate the area prior to
receiving a potential injury, CALTRANS
will also ‘‘soft start’’ the hammer prior
to operating at full capacity.
CALTRANS typically implements a
‘‘soft start’’ with several initial hammer
strikes at less than full capacity (i.e.,
approximately 40–60 percent energy
levels) with no less than a 1 minute
interval between each strike. Similar
levels of noise reduction are expected
underwater. Therefore, the contractor
will initiate hammering of both the 500–
kJ and the 1,700–kJ hammers with this
procedure in order to allow pinnipeds
or cetaceans in the area to voluntarily
move from the area, this should expose
fewer animals to loud sounds both
underwater and above water noise. This
would also ensure that, although not
expected, any pinnipeds and cetaceans
that are missed during safety zone
monitoring will not be injured.
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Compliance with Equipment Noise
Standards
To mitigate noise levels and,
therefore, impacts to California sea
lions, Pacific harbor seals, harbor
porpoises, and gray whales, all
construction equipment will comply as
much as possible with applicable
equipment noise standards of the U.S.
Environmental Protection Agency, and
all construction equipment will have
noise control devices no less effective
than those provided on the original
equipment.
Monitoring
The following monitoring measures
are currently required under the IHA to
reduce impacts to marine mammals to
the lowest extent practicable. Unless, as
noted, the work has been completed,
NMFS proposes to continue those
monitoring measures under a new IHA
(if issued).
Visual Observations
The area-wide baseline monitoring
and the aerial photo survey to estimate
the fraction of pinnipeds that might be
missed by visual monitoring have been
completed under the current IHA and
do not need to be continued.
Safety zone monitoring will be
conducted during driving of all openwater, permanent piles without
cofferdams and with cofferdams when
underwater SPLs reach 190 dB RMS or
greater. Monitoring of the pinniped and
cetacean safety zones will be conducted
by a minimum of three qualified NMFSapproved observers for each safety zone.
One three-observer team will be
required for the safety zones around
each pile driving site, so that multiple
teams will be required if pile driving is
occurring at multiple locations at the
same time. The observers will begin
monitoring at least 30 minutes prior to
startup of the pile driving. Most likely
observers will conduct the monitoring
from small boats, as observations from
a higher vantage point (such as the SFOBB) is not practical. Pile driving will
not begin until the safety zone is clear
of marine mammals. However, as
described in the Mitigation section,
once pile driving of a segment begins,
operations will continue uninterrupted
until the segment has reached its
predetermined depth. However, if pile
driving of a segment ceases for 30
minutes or more and a marine mammal
is sighted within the designated safety
zone prior to commencement of pile
driving, the observer(s) must notify the
Resident Engineer (or other authorized
individual) immediately and follow the
mitigation requirements as outlined
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previously (see Mitigation). Monitoring
will continue through the pile driving
period and will end approximately 30
minutes after pile driving has been
completed. Biological observations will
be made using binoculars during
daylight hours.
In addition to monitoring from boats,
during open-water pile driving,
monitoring at one control site (harbor
seal haul-out sites and the waters
surrounding such sites not impacted by
the East Span Project’s pile driving
activities, i.e. Mowry Slough) will be
designated and monitored for
comparison. Monitoring will be
conducted twice a week at the control
site whenever open-water pile driving is
being conducted. Data on all
observations will be recorded and will
include items such as species, numbers,
behavior, details of any observed
disturbances, time of observation,
location, and weather. The reactions of
marine mammals will be recorded based
on the following classifications that are
consistent with the Richmond Bridge
Harbor Seal survey methodology (for
information on the Richmond Bridge
authorization, see 68 FR 66076,
November 25, 2003): (1) No response,
(2) head alert (looks toward the source
of disturbance), (3) approach water (but
not leave), and (4) flush (leaves haul-out
site). The number of marine mammals
under each disturbance reaction will be
recorded, as well as the time when seal
re-haul after a flush.
Acoustical Observations
Airborne noise level measurements
have been completed and underwater
environmental noise levels will
continue to be measured as part of the
East Span Project. The purpose of the
underwater sound monitoring is to
establish the safety zone of 190 dB re 1
micro-Pa RMS (impulse) for pinnipeds
and the safety zone of 180 dB re 1
micro-Pa RMS (impulse) for cetaceans.
Monitoring will be conducted during
the driving of the last half (deepest pile
segment) for any given open-water pile.
One pile in every other pair of pier
groups will be monitored. One reference
location will be established at a distance
of 100 m (328 ft) from the pile driving.
Sound measurements will be taken at
the reference location at two depths (a
depth near the mid-water column and a
depth near the bottom of the water
column but at least 1 m (3 ft) above the
bottom) during the driving of the last
half (deepest pile segment) for any given
pile. Two additional in-water spot
measurements will be conducted at
appropriate depths (near mid water
column), generally 500 m (1,640 ft) in
two directions either west, east, south or
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north of the pile driving site will be
conducted at the same two depths as the
reference location measurements. In
cases where such measurements cannot
be obtained due to obstruction by land
mass, structures or navigational hazards,
measurements will be conducted at
alternate spot measurement locations.
Measurements will be made at other
locations either nearer or farther as
necessary to establish the approximate
distance for the safety zones. Each
measuring system shall consist of a
hydrophone with an appropriate signal
conditioning connected to a sound level
meter and an instrument grade digital
audiotape recorder (DAT). Overall SPLs
shall be measured and reported in the
field in dB re 1 micro-Pa rms (impulse).
An infrared range finder will be used to
determine distance from the monitoring
location to the pile. The recorded data
will be analyzed to determine the
amplitude, time history and frequency
content of the impulse.
Reporting
Under the current IHA, CALTRANS
has submitted weekly marine mammal
monitoring reports during when pile
driving is commenced. In August 2006,
CALTRANS submitted its
Hydroacoustic Measurement at Piers T1
and E2 report. This report is available
by contacting NMFS (see ADDRESSES) or
on the Web at https://biomitigation.org.
Under the proposed IHA,
coordination with NMFS will occur on
a weekly basis, or more often as
necessary. During periods with openwater pile driving activity, weekly
monitoring reports will be made
available to NMFS and the public at
https://biomitigation.org. These weekly
reports will include a summary of the
previous week’s monitoring activities
and an estimate of the number of seals
and sea lions that may have been
disturbed as a result of pile driving
activities.
In addition, CALTRANS proposes to
provide NMFS’ Southwest Regional
Administrator with a draft final report
within 90 days after completion of the
westbound Skyway contract and 90
days after completion of the Suspension
Span foundations contract. This report
should detail the monitoring protocol,
summarize the data recorded during
monitoring, and estimate the number of
marine mammals that may have been
harassed due to pile driving. If
comments are received from the
Regional Administrator on the draft
final report, a final report must be
submitted to NMFS within 30 days
thereafter. If no comments are received
from NMFS, the draft final report will
be considered to be the final report.
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National Environmental Policy Act
(NEPA)
NMFS has prepared an Environmental
Assessment (EA) and made a Finding of
No Significant Impact (FONSI).
Therefore, preparation of an
environmental impact statement on this
action is not required by section 102(2)
of the NEPA or its implementing
regulations. A copy of the EA and
FONSI are available upon request (see
ADDRESSES).
Endangered Species Act (ESA)
On October 30, 2001, NMFS
completed consultation under section 7
of the ESA with the Federal Highway
Administration (FHWA) on the
CALTRANS’ construction of a
replacement bridge for the East Span of
the SF-OBB in California. The finding
contained in the Biological Opinion was
that the proposed action at the East
Span of the SF-OBB is not likely to
jeopardize the continued existence of
listed anadromous salmonids, or result
in the destruction or adverse
modification of designated critical
habitat for these species. Listed marine
mammals are not expected to be in the
area of the action and thus would not be
affected. However, the proposed
issuance of an IHA to CALTRANS
constitutes an agency action that
authorizes an activity that may affect
ESA-listed species and, therefore, is
subject to section 7 of the ESA.
Moreover, as the effects of the activities
on listed salmonids were analyzed
during a formal consultation between
the FHWA and NMFS, and as the
underlying action has not changed from
that considered in the consultation, the
discussion of effects that are contained
in the Biological Opinion issued to the
FHWA on October 30, 2001, pertains
also to this action. NMFS has
determined that issuance of an IHA for
this activity does not lead to any effects
to listed species apart from those that
were considered in the consultation on
FHWA’s action.
Preliminary Determinations
For the reasons discussed in this
document and in previously identified
supporting documents, NMFS has
preliminarily determined that the
impact of pile driving and other
activities associated with construction
of the East Span Project should result,
at worst, in the Level B harassment of
small numbers of California sea lions,
Pacific harbor seals, harbor porpoises,
and potentially gray whales that inhabit
or visit SFB in general and the vicinity
of the SF-OBB in particular. While
behavioral modifications, including
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535
temporarily vacating the area around the
construction site, may be made by these
species to avoid the resultant visual and
acoustic disturbance, the availability of
alternate areas within SFB and haul-out
sites (including pupping sites) and
feeding areas within the Bay has led
NMFS to preliminarily determine that
this action will have a negligible impact
on California sea lion, Pacific harbor
seal, harbor porpoises, and gray whale
populations along the California coast.
In addition, no take by Level A
harassment (injury) or death is
anticipated and harassment takes
should be at the lowest level practicable
due to incorporation of the mitigation
measures mentioned previously in this
document.
Proposed Authorization
NMFS proposes to issue an IHA to
CALTRANS for the potential
harassment of small numbers of harbor
seals, California sea lions, harbor
porpoises, and gray whales incidental to
construction of a replacement bridge for
the East Span of the San FrancisoOakland Bay Bridge in California,
provided the previously mentioned
mitigation, monitoring, and reporting
requirements are incorporated. NMFS
has preliminarily determined that the
proposed activity would result in the
harassment of only small numbers of
harbor seals, California sea lions, harbor
porpoises, and possibly gray whales and
will have no more than a negligible
impact on these marine mammal stocks.
Information Solicited
NMFS requests interested persons to
submit comments, information, and
suggestions concerning this request (see
ADDRESSES). Prior to submitting
comments, NMFS recommends
reviewers of this document read NMFS’
November 14, 2003 (68 FR 64595) and
May 8, 2006 (71 FR 26750) Federal
Register notices on this action,
especially responses to comments made
previously, as NMFS does not intend to
address these issues further without the
submission of additional scientific
information relevant to the comment.
Dated: December 28, 2006.
James H. Lecky,
Director, Office of Protected Resources,
National Marine Fisheries Service.
[FR Doc. E6–22615 Filed 1–4–07; 8:45 am]
BILLING CODE 3510–22–S
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Agencies
[Federal Register Volume 72, Number 3 (Friday, January 5, 2007)]
[Notices]
[Pages 532-535]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E6-22615]
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
[I.D. 113006A]
Taking of Marine Mammals Incidental to Specified Activities;
Construction of the East Span of the San Francisco-Oakland Bay Bridge
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Notice; proposed authorization for an incidental take
authorization; request for comments.
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SUMMARY: NMFS has received a request from the California Department of
Transportation (CALTRANS) for renewal of an authorization to take small
numbers of California sea lions, Pacific harbor seals, harbor
porpoises, and gray whales, by harassment, incidental to construction
of a replacement bridge for the East Span of the San Francisco-Oakland
Bay Bridge (SF-OBB) in California. Under the Marine Mammal Protection
Act (MMPA), NMFS is requesting comments on its proposal to issue an
authorization to CALTRANS to incidentally take, by harassment, small
numbers of these species of pinnipeds and cetaceans during the next 12
months.
DATES: Comments and information must be received no later than February
5, 2007.
ADDRESSES: Comments on the application should be addressed to P.
Michael Payne, Chief, Permits, Conservation and Education Division,
Office of Protected Resources, National Marine Fisheries Service, 1315
East-West Highway, Silver Spring, MD 20910-3225, or by telephoning the
contact listed here. The mailbox address for providing email comments
is PR1.113006A@noaa.gov. Comments sent via e-mail, including all
attachments, must not exceed a 10-megabyte file size. A copy of the
2001 application, the 2006 renewal request, the January 2005 Marine
Mammal and Acoustic Monitoring report, and the August 2006
Hydroacoustic Measurements report may be obtained by writing to this
address or by telephoning one of the contacts listed here.
FOR FURTHER INFORMATION CONTACT: Shane Guan, NMFS, (301) 713-2289, ext
137, or Monica DeAngelis, NMFS, (562) 980-3232.
SUPPLEMENTARY INFORMATION:
Background
Sections 101(a)(5)(A) and (D) of the MMPA (16 U.S.C. 1361 et seq.)
direct the Secretary of Commerce to allow, upon request, the
incidental, but not intentional, taking of small numbers of marine
mammals by U.S. citizens who engage in a specified activity (other than
commercial fishing) within a specified geographical region if certain
findings are made and either regulations are issued or, if the taking
is limited to harassment, notice of a proposed authorization is
provided to the public for review.
Permission shall be granted if NMFS finds that the taking will have
no more than a negligible impact on the species or stock(s) and will
not have an unmitigable adverse impact on the availability of the
species or stock(s) for subsistence uses and that the permissible
methods of taking and requirements pertaining to the mitigation,
monitoring, and reporting of such taking are set forth. NMFS has
defined ``negligible impact'' in 50 CFR 216.103 as ''...an impact
resulting from the specified activity that cannot be reasonably
expected to, and is not reasonably likely to, adversely affect the
species or stock through effects on annual rates of recruitment or
survival.''
Section 101(a)(5)(D) of the MMPA established an expedited process
by which citizens of the United States can apply for an authorization
to incidentally take small numbers of marine mammals by harassment.
Except with respect to certain activities not pertinent here, the MMPA
defines ``harassment'' as:
any act of pursuit, torment, or annoyance which (i) has the
potential to injure a marine mammal or marine mammal stock in the
wild [Level A harassment]; or (ii) has the potential to disturb a
marine mammal or marine mammal stock in the wild by causing
disruption of behavioral patterns, including, but not limited to,
migration, breathing, nursing, breeding, feeding, or sheltering
[Level B harassment].
Section 101(a)(5)(D) establishes a 45-day time limit for NMFS
review of an application followed by a 30-day public notice and comment
period on any proposed authorizations for the incidental harassment of
small numbers of marine mammals. Within 45 days of the close of the
comment period, NMFS must either issue or deny issuance of the
authorization.
Summary of Request
On October 16, 2006, CALTRANS sumbitted a request to NOAA
requesting renewal of an IHA for the possible harassment of small
numbers of California sea lions (Zalophus californianus), Pacific
harbor seals (Phoca vitulina richardsii), harbor porpoises (Phocoena
phocoena), and gray whales (Eschrichtius robustus) incidental to
construction of a replacement bridge for the East Span of the SF-OBB,
in San Francisco Bay (SFB or the Bay), California. An IHA was issued to
CALTRANS for this activity on April 30, 2006 and it will expire on
April 29, 2007 (71 FR 26750). A detailed description of the SF-OBB
project and background information on the issuance of this IHA were
provided in the November 14, 2003 (68 FR 64595) Federal Register notice
and are not
[[Page 533]]
repeated here. Please refer to that Federal Register notice.
Description of the Marine Mammals Potentially Affected by the Activity
General information on the marine mammal species found in
California waters can be found in Caretta et al. (2006), which is
available at the following URL: https://www.nmfs.noaa.gov/pr/pdfs/sars/
po2005.pdf. Refer to that document for information on these species.
The marine mammals most likely to be found in the SF-OBB area are
the California sea lion, Pacific harbor seal, and harbor porpoise. From
December through May gray whales may also be present in the SF-OBB
area. Information on California sea lion, harbor seal, and gray whale
was provided in the November 14, 2003 (68 FR 64595), Federal Register
notice; information on harbor porpoise was provided in the January 26,
2006 (71 FR 4352), Federal Register notice.
Potential Effects on Marine Mammals and Their Habitat
CALTRANS and NMFS have determined that open-water pile driving, as
outlined in the project description, has the potential to result in
behavioral harassment of California sea lions, Pacific harbor seals,
harbor porpoises, and gray whales that may be swimming, foraging, or
resting in the project vicinity while pile driving is being conducted.
Pile driving could potentially harass those few pinnipeds that are in
the water close to the project site, whether their heads are above or
below the surface.
Based on airborne noise levels measured and on-site monitoring
conducted during 2004 under the previous IHA, noise levels from the
East Span project did not result in the harassment of harbor seals
hauled out on Yerba Buena Island (YBI). Also, noise levels from the
East Span project are not expected to result in harassment of the sea
lions hauled out at Pier 39 as airborne and waterborne sound pressure
levels (SPLs) would attenuate to below harassment levels by the time
they reach that haul-out site, 5.7 km (3.5 miles) from the project
site.
For reasons provided in greater detail in NMFS' November 14, 2003
(68 FR 64595) Federal Register notice and in CALTRANS' June 2004,
January 2005 annual monitoring reports, and marine mammal observation
memoranda between February and September, 2006, the East Span Project
was resulting in only small numbers of harbor seals. Therefore, it is
not expected to result in more than a negligible impact on marine
mammal stocks and will not have a significant impact on their habitat.
No pile driving has been commenced since September 15, 2006. Short-term
impacts to habitat may include minimal disturbance of the sediment
where the channels are dredged for barge access and where individual
bridge piers are constructed. Long-term impacts to marine mammal
habitat will be limited to the footprint of the piles and the
obstruction they will create following installation. However, this
impact is not considered significant as the marine mammals can easily
swim around the piles of the new bridge, as they currently swim around
the existing bridge piers.
Mitigation
The following mitigation measures are currently required under the
existing IHA to reduce impacts to marine mammals to the lowest extent
practicable. NMFS proposes to continue these mitigation measures under
a new IHA, if issued.
Barrier Systems
An air bubble curtain system is required to be used only when
driving the permanent open-water piles. While the bubble curtain is
required specifically as a method to reduce impacts to endangered and
threatened fish species in SFB, it may also provide some benefit for
marine mammals. The NMFS' Biological Opinion and the California
Department of Fish and Game's (CDFG) 2001 Incidental Take Permit also
allow for the use of other equally effective methods, such as
cofferdams, as an alternative to the air bubble curtain system to
attenuate the effects of sound pressure waves on fish during driving of
permanent in-Bay piles (NMFS 2001; CDFG, 2001). Piers E-16 through E-7
for both the eastbound and westbound structures of the Skyway will be
surrounded by sheet-pile cofferdams, which will be de-watered before
the start of pile driving. De-watered cofferdams are generally
effective sound attenuation devices. For Piers E3 through E6 of the
Skyway and Pier 1 the Self-Anchored Suspension span, it is anticipated
that cofferdams will not be used; therefore, a bubble curtain will
surround the piles.
Sound Attenuation
As a result of the determinations made during the Pile Installation
Demonstration Project (PIDP) restrike and the investigation at the
Benicia-Martinez Bridge, NMFS determined in 2003 that CALTRANS must
install an air bubble curtain for pile driving for the open-water piles
without cofferdams located at the SF-OBB. This specification and
configuration of the air bubble curtain system is described in pervious
Federal Register notice (71 FR 4352, January 26, 2006), and is not
repeated here.
Establishment of Safety/Buffer Zones
A safety zone is to be established and monitored to include all
areas where the underwater SPLs are anticipated to equal or exceed 190
dB re 1 microPa rms (impulse) for pinnipeds. Also, a 180-dB re 1
microPa rms (impulse) safety zone for gray whales and harbor porpoises
must be established for pile driving occurring during the gray whale
migration season from December through May. Prior to commencement of
any pile driving, a preliminary 500-m (1,640-ft) radius safety zone for
pinnipeds (California sea lions and Pacific harbor seals) will be
established around the pile driving site, as it was for the PIDP. Once
pile driving begins, either new safety zones can be established for the
500 kJ and 1,700 kJ hammers or the 500 m (1,640 ft) safety zone can be
retained. If new safety zones are established based on SPL
measurements, NMFS requires that each new safety zone be based on the
most conservative measurement (i.e., the largest safety zone
configuration). SPLs will be recorded at the 500-m (1,640-ft) contour.
The safety zone radius for pinnipeds will then be enlarged or reduced,
depending on the actual recorded SPLs.
Observers on boats will survey the safety zone to ensure that no
marine mammals are seen within the zone before pile driving of a pile
segment begins. If marine mammals are found within the safety zone,
pile driving of the segment will be delayed until they move out of the
area. If a marine mammal is seen above water and then dives below, the
contractor will wait 15 minutes and if no marine mammals are seen by
the observer in that time it will be assumed that the animal has moved
beyond the safety zone. This 15-minute criterion is based on scientific
evidence that harbor seals in San Francisco Bay dive for a mean time of
0.50 minutes to 3.33 minutes (Harvey and Torok, 1994), and the mean
diving duration for harbor porpoises ranges from 44 to 103 seconds
(Westgate et al., 1995). However, due to the limitations of monitoring
from a boat, there can be no assurance that the zone will be devoid of
all marine mammals at all times.
Once the pile driving of a segment begins it cannot be stopped
until that segment has reached its predetermined depth due to the
nature of the sediments underlying the Bay. If pile driving stops
[[Page 534]]
and then resumes, it would potentially have to occur for a longer time
and at increased energy levels. In sum, this would simply amplify
impacts to marine mammals, as they would endure potentially higher SPLs
for longer periods of time. Pile segment lengths and wall thickness
have been specially designed so that when work is stopped between
segments (but not during a single segment), the pile tip is never
resting in highly resistant sediment layers. Therefore, because of this
operational situation, if seals, sea lions, or harbor porpoises enter
the safety zone after pile driving of a segment has begun, pile driving
will continue and marine mammal observers will monitor and record
marine mammal numbers and behavior. However, if pile driving of a
segment ceases for 30 minutes or more and a marine mammal is sighted
within the designated safety zone prior to commencement of pile
driving, the observer(s) must notify the Resident Engineer (or other
authorized individual) immediately and follow the mitigation
requirements as outlined previously in this document.
Soft Start
It should be recognized that although marine mammals will be
protected from Level A harassment by establishment of an air-bubble
curtain and marine mammal observers monitoring a 190-dB safety zone for
pinipeds and 180-dB safety zone for cetaceans, mitigation may not be
100 percent effective at all times in locating marine mammals.
Therefore, in order to provide additional protection to marine mammals
near the project area by allowing marine mammals to vacate the area
prior to receiving a potential injury, CALTRANS will also ``soft
start'' the hammer prior to operating at full capacity. CALTRANS
typically implements a ``soft start'' with several initial hammer
strikes at less than full capacity (i.e., approximately 40-60 percent
energy levels) with no less than a 1 minute interval between each
strike. Similar levels of noise reduction are expected underwater.
Therefore, the contractor will initiate hammering of both the 500-kJ
and the 1,700-kJ hammers with this procedure in order to allow
pinnipeds or cetaceans in the area to voluntarily move from the area,
this should expose fewer animals to loud sounds both underwater and
above water noise. This would also ensure that, although not expected,
any pinnipeds and cetaceans that are missed during safety zone
monitoring will not be injured.
Compliance with Equipment Noise Standards
To mitigate noise levels and, therefore, impacts to California sea
lions, Pacific harbor seals, harbor porpoises, and gray whales, all
construction equipment will comply as much as possible with applicable
equipment noise standards of the U.S. Environmental Protection Agency,
and all construction equipment will have noise control devices no less
effective than those provided on the original equipment.
Monitoring
The following monitoring measures are currently required under the
IHA to reduce impacts to marine mammals to the lowest extent
practicable. Unless, as noted, the work has been completed, NMFS
proposes to continue those monitoring measures under a new IHA (if
issued).
Visual Observations
The area-wide baseline monitoring and the aerial photo survey to
estimate the fraction of pinnipeds that might be missed by visual
monitoring have been completed under the current IHA and do not need to
be continued.
Safety zone monitoring will be conducted during driving of all
open-water, permanent piles without cofferdams and with cofferdams when
underwater SPLs reach 190 dB RMS or greater. Monitoring of the pinniped
and cetacean safety zones will be conducted by a minimum of three
qualified NMFS-approved observers for each safety zone. One three-
observer team will be required for the safety zones around each pile
driving site, so that multiple teams will be required if pile driving
is occurring at multiple locations at the same time. The observers will
begin monitoring at least 30 minutes prior to startup of the pile
driving. Most likely observers will conduct the monitoring from small
boats, as observations from a higher vantage point (such as the SF-OBB)
is not practical. Pile driving will not begin until the safety zone is
clear of marine mammals. However, as described in the Mitigation
section, once pile driving of a segment begins, operations will
continue uninterrupted until the segment has reached its predetermined
depth. However, if pile driving of a segment ceases for 30 minutes or
more and a marine mammal is sighted within the designated safety zone
prior to commencement of pile driving, the observer(s) must notify the
Resident Engineer (or other authorized individual) immediately and
follow the mitigation requirements as outlined previously (see
Mitigation). Monitoring will continue through the pile driving period
and will end approximately 30 minutes after pile driving has been
completed. Biological observations will be made using binoculars during
daylight hours.
In addition to monitoring from boats, during open-water pile
driving, monitoring at one control site (harbor seal haul-out sites and
the waters surrounding such sites not impacted by the East Span
Project's pile driving activities, i.e. Mowry Slough) will be
designated and monitored for comparison. Monitoring will be conducted
twice a week at the control site whenever open-water pile driving is
being conducted. Data on all observations will be recorded and will
include items such as species, numbers, behavior, details of any
observed disturbances, time of observation, location, and weather. The
reactions of marine mammals will be recorded based on the following
classifications that are consistent with the Richmond Bridge Harbor
Seal survey methodology (for information on the Richmond Bridge
authorization, see 68 FR 66076, November 25, 2003): (1) No response,
(2) head alert (looks toward the source of disturbance), (3) approach
water (but not leave), and (4) flush (leaves haul-out site). The number
of marine mammals under each disturbance reaction will be recorded, as
well as the time when seal re-haul after a flush.
Acoustical Observations
Airborne noise level measurements have been completed and
underwater environmental noise levels will continue to be measured as
part of the East Span Project. The purpose of the underwater sound
monitoring is to establish the safety zone of 190 dB re 1 micro-Pa RMS
(impulse) for pinnipeds and the safety zone of 180 dB re 1 micro-Pa RMS
(impulse) for cetaceans. Monitoring will be conducted during the
driving of the last half (deepest pile segment) for any given open-
water pile. One pile in every other pair of pier groups will be
monitored. One reference location will be established at a distance of
100 m (328 ft) from the pile driving. Sound measurements will be taken
at the reference location at two depths (a depth near the mid-water
column and a depth near the bottom of the water column but at least 1 m
(3 ft) above the bottom) during the driving of the last half (deepest
pile segment) for any given pile. Two additional in-water spot
measurements will be conducted at appropriate depths (near mid water
column), generally 500 m (1,640 ft) in two directions either west,
east, south or
[[Page 535]]
north of the pile driving site will be conducted at the same two depths
as the reference location measurements. In cases where such
measurements cannot be obtained due to obstruction by land mass,
structures or navigational hazards, measurements will be conducted at
alternate spot measurement locations. Measurements will be made at
other locations either nearer or farther as necessary to establish the
approximate distance for the safety zones. Each measuring system shall
consist of a hydrophone with an appropriate signal conditioning
connected to a sound level meter and an instrument grade digital
audiotape recorder (DAT). Overall SPLs shall be measured and reported
in the field in dB re 1 micro-Pa rms (impulse). An infrared range
finder will be used to determine distance from the monitoring location
to the pile. The recorded data will be analyzed to determine the
amplitude, time history and frequency content of the impulse.
Reporting
Under the current IHA, CALTRANS has submitted weekly marine mammal
monitoring reports during when pile driving is commenced. In August
2006, CALTRANS submitted its Hydroacoustic Measurement at Piers T1 and
E2 report. This report is available by contacting NMFS (see ADDRESSES)
or on the Web at https://biomitigation.org.
Under the proposed IHA, coordination with NMFS will occur on a
weekly basis, or more often as necessary. During periods with open-
water pile driving activity, weekly monitoring reports will be made
available to NMFS and the public at https://biomitigation.org. These
weekly reports will include a summary of the previous week's monitoring
activities and an estimate of the number of seals and sea lions that
may have been disturbed as a result of pile driving activities.
In addition, CALTRANS proposes to provide NMFS' Southwest Regional
Administrator with a draft final report within 90 days after completion
of the westbound Skyway contract and 90 days after completion of the
Suspension Span foundations contract. This report should detail the
monitoring protocol, summarize the data recorded during monitoring, and
estimate the number of marine mammals that may have been harassed due
to pile driving. If comments are received from the Regional
Administrator on the draft final report, a final report must be
submitted to NMFS within 30 days thereafter. If no comments are
received from NMFS, the draft final report will be considered to be the
final report.
National Environmental Policy Act (NEPA)
NMFS has prepared an Environmental Assessment (EA) and made a
Finding of No Significant Impact (FONSI). Therefore, preparation of an
environmental impact statement on this action is not required by
section 102(2) of the NEPA or its implementing regulations. A copy of
the EA and FONSI are available upon request (see ADDRESSES).
Endangered Species Act (ESA)
On October 30, 2001, NMFS completed consultation under section 7 of
the ESA with the Federal Highway Administration (FHWA) on the CALTRANS'
construction of a replacement bridge for the East Span of the SF-OBB in
California. The finding contained in the Biological Opinion was that
the proposed action at the East Span of the SF-OBB is not likely to
jeopardize the continued existence of listed anadromous salmonids, or
result in the destruction or adverse modification of designated
critical habitat for these species. Listed marine mammals are not
expected to be in the area of the action and thus would not be
affected. However, the proposed issuance of an IHA to CALTRANS
constitutes an agency action that authorizes an activity that may
affect ESA-listed species and, therefore, is subject to section 7 of
the ESA. Moreover, as the effects of the activities on listed salmonids
were analyzed during a formal consultation between the FHWA and NMFS,
and as the underlying action has not changed from that considered in
the consultation, the discussion of effects that are contained in the
Biological Opinion issued to the FHWA on October 30, 2001, pertains
also to this action. NMFS has determined that issuance of an IHA for
this activity does not lead to any effects to listed species apart from
those that were considered in the consultation on FHWA's action.
Preliminary Determinations
For the reasons discussed in this document and in previously
identified supporting documents, NMFS has preliminarily determined that
the impact of pile driving and other activities associated with
construction of the East Span Project should result, at worst, in the
Level B harassment of small numbers of California sea lions, Pacific
harbor seals, harbor porpoises, and potentially gray whales that
inhabit or visit SFB in general and the vicinity of the SF-OBB in
particular. While behavioral modifications, including temporarily
vacating the area around the construction site, may be made by these
species to avoid the resultant visual and acoustic disturbance, the
availability of alternate areas within SFB and haul-out sites
(including pupping sites) and feeding areas within the Bay has led NMFS
to preliminarily determine that this action will have a negligible
impact on California sea lion, Pacific harbor seal, harbor porpoises,
and gray whale populations along the California coast.
In addition, no take by Level A harassment (injury) or death is
anticipated and harassment takes should be at the lowest level
practicable due to incorporation of the mitigation measures mentioned
previously in this document.
Proposed Authorization
NMFS proposes to issue an IHA to CALTRANS for the potential
harassment of small numbers of harbor seals, California sea lions,
harbor porpoises, and gray whales incidental to construction of a
replacement bridge for the East Span of the San Franciso-Oakland Bay
Bridge in California, provided the previously mentioned mitigation,
monitoring, and reporting requirements are incorporated. NMFS has
preliminarily determined that the proposed activity would result in the
harassment of only small numbers of harbor seals, California sea lions,
harbor porpoises, and possibly gray whales and will have no more than a
negligible impact on these marine mammal stocks.
Information Solicited
NMFS requests interested persons to submit comments, information,
and suggestions concerning this request (see ADDRESSES). Prior to
submitting comments, NMFS recommends reviewers of this document read
NMFS' November 14, 2003 (68 FR 64595) and May 8, 2006 (71 FR 26750)
Federal Register notices on this action, especially responses to
comments made previously, as NMFS does not intend to address these
issues further without the submission of additional scientific
information relevant to the comment.
Dated: December 28, 2006.
James H. Lecky,
Director, Office of Protected Resources, National Marine Fisheries
Service.
[FR Doc. E6-22615 Filed 1-4-07; 8:45 am]
BILLING CODE 3510-22-S