Takes of Marine Mammals Incidental to Specified Activities; Taking Marine Mammals Incidental to the Mukilteo Multimodal Project-Season 3, 43849-43855 [2018-18609]
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Federal Register / Vol. 83, No. 167 / Tuesday, August 28, 2018 / Notices
Compliance, Office IV, International
Trade Administration, U.S. Department
of Commerce, 1401 Constitution Avenue
NW, Washington, DC 20230.
SUPPLEMENTARY INFORMATION:
Background
On July 10, 2018, the Department of
Commerce (Commerce) initiated a
countervailing duty (CVD) investigation
of imports of steel racks from the
People’s Republic of China.1 Currently,
the preliminary determination is due no
later than September 13, 2018.
daltland on DSKBBV9HB2PROD with NOTICES
Postponement of Preliminary
Determination
Section 703(b)(1) of the Tariff Act of
1930, as amended (the Act), requires
Commerce to issue the preliminary
determination in a CVD investigation
within 65 days after the date on which
Commerce initiated the investigation.
However, section 703(c)(1) of the Act
permits Commerce to postpone the
preliminary determination until no later
than 130 days after the date on which
Commerce initiated the investigation if:
(A) the petitioner 2 makes a timely
request for a postponement; or (B)
Commerce concludes that the parties
concerned are cooperating, and
determines that the investigation is
extraordinarily complicated, and that
additional time is necessary to make a
preliminary determination. Under 19
CFR 351.205(e), the petitioner must
submit a request for postponement 25
days or more before the scheduled date
of the preliminary determination and
must state the reasons for the request.
Commerce will grant the request unless
it finds compelling reasons to deny the
request.
On August 9, 2018, the petitioner
submitted a timely request that
Commerce postpone the preliminary
determination.3 The petitioner states
that it requests postponement of the
preliminary determination because the
scope of the investigation does not
coincide exactly with any particular
HTS category, it has been timeconsuming for Commerce to identify the
largest producers of subject imports,
1 See Certain Steel Racks from the People’s
Republic: Initiation of Countervailing Duty
Investigation, 83 FR 33201 (July 17, 2018)
(Initiation Notice).
2 The petitioner is the Coalition of Fair Rack
Imports and its individual members are Bulldog
Rack Company, Hannibal Industries, Inc., Husky
Rack and Wire, Ridg-U-Rak, Inc., SpaceRAK, a
Division of Heartland Steel Products, Inc.,
Speedrack Products Group, Ltd., Steel King
Industries, Inc., Tri-Boro Shelving & Partition Corp.,
and UNARCO Material Handling, Inc.
3 Letter from the petitioner, ‘‘Re: Certain Steel
Racks from the People’s Republic of China: Request
to Postpone Preliminary Determination,’’ dated
August 9, 2018.
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and, at the time of the petitioner’s
request, Commerce had not yet been
able to designate mandatory
respondents.4 The petitioner states that
the postponement would allow
sufficient time for Commerce to conduct
a full investigation regarding the
subsidy benefits received by Chinese
producers and exporters of subject
racks.
In accordance with 19 CFR
351.205(e), the petitioner has stated the
reasons for requesting a postponement
of the preliminary determination, and
Commerce finds no compelling reason
to deny the request. Therefore, in
accordance with section 703(c)(1)(A) of
the Act, Commerce is postponing the
deadline for the preliminary
determination to no later than 130 days
after the date on which the investigation
was initiated, i.e., November 19, 2018.5
Pursuant to section 705(a)(1) of the Act
and 19 CFR 351.210(b)(1), the deadline
for the final determination of this
investigation will continue to be 75 days
after the date of the preliminary
determination, unless postponed at a
later date.
This notice is issued and published
pursuant to section 703(c)(2) of the Act
and 19 CFR 351.205(f)(1).
Dated: August 22, 2018.
Gary Taverman,
Deputy Assistant Secretary for Antidumping
and Countervailing Duty Operations,
performing the non-exclusive functions and
duties of the Assistant Secretary for
Enforcement and Compliance.
[FR Doc. 2018–18611 Filed 8–27–18; 8:45 am]
BILLING CODE 3510–DS–P
DEPARTMENT OF COMMERCE
National Institute of Standards and
Technology
Change of Publication Manner for
Invention Licenses
National Institute of Standards
and Technology, Department of
Commerce.
ACTION: Notice.
AGENCY:
Currently, the National
Institute of Standards and Technology
(NIST) publishes notices of prospective
SUMMARY:
4 Id.
5 Postponing the preliminary determination to
130 days after initiation would place the deadline
on Saturday, November 17, 2018. Commerce’s
practice dictates that where a deadline falls on a
weekend or federal holiday, the appropriate
deadline is the next business day. See Notice of
Clarification: Application of ‘‘Next Business Day’’
Rule for Administrative Determination Deadlines
Pursuant to the Tariff Act of 1930, As Amended, 70
FR 24533 (May 10, 2005).
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43849
exclusive, co-exclusive or partially
exclusive domestic or foreign licenses of
Government owned inventions in the
Federal Register. NIST is announcing
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www.fbo.gov/), providing opportunity
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ADDRESSES: Questions related to this
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phone at 301–975–2573.
SUPPLEMENTARY INFORMATION: Pursuant
to 37 CFR 404.7(a)(1)(i), an exclusive,
co-exclusive or partially exclusive
domestic license, and, pursuant to 37
CFR 404.7(b)(1)(i), an exclusive, coexclusive or partially exclusive foreign
license, may be granted on Government
owned inventions only if notice of a
prospective license has been published
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appropriate manner, providing
opportunity for filing written objections
within at least a 15-day period.
NIST provides notice that it will
publish future notices of prospective
exclusive, co-exclusive or partially
exclusive domestic or foreign licenses in
FEDBIZOPPS.GOV (https://
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for filing written objections within at
least a 15-day period.
Authority: 35 U.S.C. 200 et seq.
Phillip Singerman,
Associate Director for Innovation and
Industry Services.
[FR Doc. 2018–18551 Filed 8–27–18; 8:45 am]
BILLING CODE 3510–13–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
RIN 0648–XG205
Takes of Marine Mammals Incidental to
Specified Activities; Taking Marine
Mammals Incidental to the Mukilteo
Multimodal Project—Season 3
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Notice; issuance of incidental
harassment authorization.
AGENCY:
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Federal Register / Vol. 83, No. 167 / Tuesday, August 28, 2018 / Notices
In accordance with the
regulations implementing the Marine
Mammal Protection Act (MMPA) as
amended, notification is hereby given
that NMFS has issued an incidental
harassment authorization (IHA) to the
Washington Department of
Transportation (WSDOT) Ferries
Division (WSF) to incidentally take, by
Level A and B harassment, marine
mammals during construction activities
associated with the Mukilteo
Multimodal Project, Puget Sound,
Washington.
SUMMARY:
This Authorization is effective
from October 1, 2018, through
September 30, 2019.
FOR FURTHER INFORMATION CONTACT:
Jaclyn Daly, Office of Protected
Resources, NMFS, (301) 427–8401.
Electronic copies of the application,
IHA, and supporting documents, as well
as a list of the references cited in this
document, may be obtained online at:
https://www.fisheries.noaa.gov/node/
23111. In case of problems accessing
these documents, please call the contact
listed above.
SUPPLEMENTARY INFORMATION:
DATES:
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Background
Sections 101(a)(5)(A) and (D) of the
MMPA (16 U.S.C. 1361 et seq.) direct
the Secretary of Commerce (as delegated
to NMFS) 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, a notice of a
proposed authorization is provided to
the public for review.
An authorization for incidental
takings shall be granted if NMFS finds
that the taking will have a negligible
impact on the species or stock(s), will
not have an unmitigable adverse impact
on the availability of the species or
stock(s) for subsistence uses (where
relevant), and if the permissible
methods of taking and requirements
pertaining to the mitigation, monitoring
and reporting of such takings 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.
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The MMPA states that the term ‘‘take’’
means to harass, hunt, capture, kill or
attempt to harass, hunt, capture, or kill
any marine mammal.
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).
Summary of Request
On April 7, 2016, WSDOT submitted
a request to NMFS requesting an IHA for
the possible harassment of small
numbers of marine mammals incidental
to construction associated with Phase 2
of the Mukilteo Multimodal Project in
Mukilteo, Washington, between August
1, 2017, and July 31, 2018. NMFS issued
the requested IHA on August 3, 2017,
which covered Phase 2 of the project in
its entirety; the IHA expired on July 31,
2018 (82 FR 44164; September 21,
2017). On January 9, 2018, we received
a request from WSDOT for a subsequent
authorization to take marine mammals
incidental to the project because all of
the Phase 2 work would not be able to
be completed under the existing IHA. A
final version of the application, which
we deemed adequate and complete, was
submitted on March 1, 2018.
On June 28, 2018, NMFS published its
proposed IHA in the Federal Register
for public comment (83 FR 30421).
NMFS has issued an IHA to WSDOT for
the take, by Level A and B harassment,
of 12 species of marine mammals
incidental to pile driving and removal
associated with the Mukilteo
Multimodal Project.
Description of the Specified Activity
and Anticipated Impacts
WSDOT operates and maintains 19
ferry terminals and one maintenance
facility, all of which are located in Puget
Sound or the San Juan Islands (Georgia
Basin) (Figure 1–1 in WSDOT’s
application). The Mukilteo Multimodal
Project is a multi-year construction
project designed to improve the
operations and facilities serving the
mainland terminus of the MukilteoClinton ferry route in Washington State.
The 2017 IHA covered the installation
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of 661 piles of various sizes over an
estimated 175 days of pile driving and
removal (Table 1). WSDOT did not
complete all the work; therefore the
issued IHA covers take incidental to the
installation of the remaining piles
(Table 1). The 2017 IHA authorized
Level A and B harassment of two
species of marine mammals and Level B
harassment of seven species of marine
mammals. NMFS has issued an IHA to
harass these same species and an
additional three species based on recent
marine mammal monitoring near the
project area (Table 2).
We refer to the notice of proposed
IHA (83 FR 30421, June 28, 2018) and
documents related to the previously
issued 2017 IHA and discuss any new
or changed information here. Previous
documents include the Federal Register
notice of the proposed 2017 IHA (82 FR
29713; May 10, 2017), Federal Register
notice of issuance of the 2017 IHA (82
FR 44164, September 21, 2017), and all
associated references and documents.
We also refer the reader to WSDOT’s
previous and current applications and
monitoring reports. All of these
documents may be found at https://
www.fisheries.noaa.gov/node/23111.
Detailed Description of the Action—A
detailed description of the vibratory and
impact pile driving and removal
activities at the Mukilteo Terminal is
found in the aforementioned
documents. The location, timing, and
nature of the pile driving operations,
including the type and size of piles and
the methods of pile driving, are
identical to those described in the
previous notices, except that only a
subset of the type and number of piles
are to be driven because some of the
work was completed under the 2017
IHA. Under the issued IHA (2018–2019),
116 piles would be installed with a
vibratory hammer. Of those, sixty-five
24-inch (in) piles would also be proofed
with an impact hammer and then
removed.
WSDOT anticipates piles equal to or
less than 36-in would be installed at a
rate of 3 per day for a total of 38 days.
Removing the 65 24-in temporary piles
may also occur at a rate of 3 pile per day
for a total of 22 days. An additional two
days is needed to install the 78-in piles
and 120-in pile. In total, up to 62 days
of pile driving and removal may occur.
WSDOT anticipates pile driving and
removal could occur over a seven month
in-water work window (July 15–
February 15).
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TABLE 1—DESCRIPTION OF WORK PLANNED, ANALYZED, AND COMPLETED UNDER THE 2017 IHA AND REMAINING WORK
PLANNED FOR 2018–2019
Method
Pile size
(in)
Vibratory Driving ......................
12 .................
24 .................
24 .................
30 .................
36 .................
78 .................
120 ...............
sheet ............
24 .................
30 .................
sheet ............
24 .................
30 .................
Vibratory Removal ...................
Impact Driving ..........................
Season 2
planned
(2017 IHA)
Season 2
completed
139
69
48
40
6
2
1
90
69
9
90
69
30
Season 3
planned
(2018 IHA)
134
4
0
25
0
0
0
0
4
0
0
4
25
Number of
days
0
0
22
9
5
2
1
1
0
22
0
0
2 22
0
1 65
26
16
6
2
1
0
1 65
0
0
1 65
0
Comment
Fewer needed, complete.
Up to 69 temporary.
Fewer needed, permanent.
Permanent.
Permanent.
Permanent.
Permanent.
Design change, not needed.
Temporary.
Delayed.
Design change, not needed.
Proofed for load-bearing.
Fewer needed, complete.
1 These 65 piles represent the same 65 temporary 24″ piles driven with a vibratory hammer. The temporary piles would be installed, proofed,
and removed.
2 Impact hammering would be conducted on same day as vibratory pile driving so these are not additional days.
Description of Marine Mammals—A
description of the marine mammals in
the area of the activities is found in the
notice of proposed IHA (83 FR 30421,
June 28, 2018). This information
remains valid so we do not repeat it
here but provide a summary table with
marine mammal species and stock
details.
TABLE 2—SPECIES AND STOCKS EXPECTED TO OCCUR IN PROJECT AREA
Common name
Scientific name
ESA/
MMPA
status;
strategic
(Y/N) 1
Stock
Stock
abundance
(CV, Nmin, most
recent
abundance
survey) 2
Annual
M/SI 3
PBR
Order Cetartiodactyla—Cetacea—Superfamily Mysticeti (baleen whales)
Family Eschrichtiidae:
Gray whale .......................
Family Balaenopteridae
(rorquals):
Humpback whale ..............
Minke whale * ...................
Eschrichtius robustus .............
Eastern North Pacific .............
N
20,990 (0.05, 20,125, 2014) ..
624
132
Megaptera novaeangliae ........
Balaenoptera acutorostrata ....
California/Oregon/Washington
California/Oregon/Washington
Y
N
1,918 (0.03, 1,876, 2017) ......
636 (0.72, 369, 2016) ............
11.0
3.5
9.2
1.3
Superfamily Odontoceti (toothed whales, dolphins, and porpoises)
Family Delphinidae:
Killer whale .......................
Bottlenose dolphin * .........
Long-beaked common
dolphin *.
Family Phocoenidae (porpoises):
Harbor porpoise ...............
Dall’s porpoise ..................
Y
76 (n/a, 76, 2017) 4 ................
0
0.14
Tursiops truncatus ..................
Delphinus delphis bairdii ........
Eastern North Pacific Southern Resident.
West coast transient ..............
California coastal ....................
California ................................
N
N
N
unk (unk, 243 2013) ...............
453 (0.06, 346, 2016) ............
101,305 (0.49, 68,432, 2016)
2.4
2.7
657
0
≥2
35.4
Phocoena ...............................
Phocoenoides dalli .................
Washington inland waters ......
California/Oregon/Washington
N
N
11,233 (0.37, 8,308, 2016) ....
25,750 (0.45, 17,954, 2016) ..
66
172
7.2
0.3
Orcinus orca ...........................
Order Carnivora—Superfamily Pinnipedia
Family Otariidae (eared seals
and sea lions):
California sea lion ............
Steller sea lion .................
Family Phocidae (earless
seals):
Harbor seal .......................
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Elephant seal ...................
Zalophus californianus ...........
Eumetopias jubatus ................
U.S. ........................................
Eastern U.S. ...........................
N
N
296,750 (n/a, 153,337, 2014)
52,139 (n/a, 41,638, 2015) ....
9,200
2,498
389
108
Phoca vitulina .........................
Washington northern inland
waters.
California breeding .................
N
11,036 (0.15, 1999) ................
1,641
43
N
179,000 (n/a, 81,368, 2014) ..
2,882
8.8
Mirounga angustirostris ..........
1 Endangered
Species Act (ESA) status: Endangered (E), Threatened (T)/MMPA status: Depleted (D). A dash (-) indicates that the species is not listed under the
ESA or designated as depleted under the MMPA. Under the MMPA, a strategic stock is one for which the level of direct human-caused mortality exceeds PBR or
which is determined to be declining and likely to be listed under the ESA within the foreseeable future. Any species or stock listed under the ESA is automatically
designated under the MMPA as depleted and as a strategic stock.
2 NMFS marine mammal stock assessment reports online at: www.nmfs.noaa.gov/pr/sars/. CV is coefficient of variation; Nmin is the minimum estimate of stock
abundance.
3 These values, found in NMFS’s SARs, represent annual levels of human-caused mortality plus serious injury from all sources combined (e.g., commercial fisheries, ship strike). Annual M/SI often cannot be determined precisely and is in some cases presented as a minimum value or range. A CV associated with estimated
mortality due to commercial fisheries is presented in some cases.
4 SRWK population abundance as of December 31, 2017 according to the Center for Whale Research.
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5 Harbor
seal estimate is based on data that are greater than 8 years old, but this is the best available information for use here.
* Indicates species added.
Harassment Zones—The harassment
threshold distances and areas provided
in the Federal Register notice of
proposed IHA (83 FR 30421, June 28,
2018) remain unchanged. Please refer to
that document documents for details;
we provide a summary tables here
(Table 3 and 4).
TABLE 3—LEVEL A HARASSMENT DISTANCES CONSIDERING PILE DRIVING DURATION PER 24 HOURS
Method
Vibratory ...........................
24
30
36
78
120
24
Impact ...............................
Level A (meters)
Source level
(dB)
Pile size
166
174
177
180
180
178
LF 1
rms 2 ....................................
rms 3 ....................................
rms 3 ....................................
rms 4 ....................................
rms 4 ....................................
SEL (single strike)/193 rms 5
MF 1
30.6
104.5
165.6
200.3
126.2
432.1
2.7
9.3
14.7
17.8
11.2
15.4
HF 1
PH 1
45.3
154.5
244.9
296.2
186.6
514.7
Level B
(m)
OT 1
18.6
63.5
100.7
121.8
76.7
231.2
1.3
4.5
7.1
8.5
5.4
16.8
6 8,000
6 8,000
7 8,700
8 20,000
....................
1,585
1 The
abbreviatation mean: LF = low frequency cetacean, MF = mid-frequency cetacean, HF = high-frequency cetacean, PH = phocid, OT = otariid.
assume vibratory removal and vibratory driving the same size pile would result in equal sound levels. Source level for 24″ piles is based on direct measurements during the Manette Bridge project (Loughlin, 2010a).
3 Source levels for 30-in and 36-in piles is based on direct measurements during the Port Townsend Project (Loughlin, 2010b).
4 WSDOT does not have noise data for 78 and 120-in piles; therefore, we used data from Caltrans (2015).
5 Single strike SEL and rms values for impact driving 24-in piles is based on direct measurements during pile driving using a bubble curtain (i.e., source levels are
attenuated) at the Coupeville Terminal (WSDOT, 2017).
6 Measurements during 30″ vibratory pile driving at Mukilteo in 2017 indicate pile driving was not detected at range of 7.9 km (Laughlin, 2017a). This equates to 66
km2.
7 At the Coleman Terminal, vibratory installation of two 36″ piles driven simultaneously was not detectable at 8.69 km (5.4 miles) (Laughlin 2017b). This equates to
69 km2.
8 The calculated Level B zone using a practical spreading loss model is 100,000 m; however, land is reached at a maximum of 20,000 m (Lowell Point on Camano
Island). This equates to 107 km2.
2 We
TABLE 4—CORRESPONDING HARASSMENT THRESHOLD ENSONIFIED AREAS
Level A (km2) 1
Method
HF
Vibratory ...............................................................................
24
30
36
78
120
24
Impact ..................................................................................
1 Level
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2 Level
OT
Level B
(km2) 2
<0.01
........................
........................
........................
........................
........................
66
66
69
107
........................
4
Pile size
PH
<0.01
<0.01
0.06
0.01
0.01
0.4
<0.01
<0.01
0.06
0.01
0.01
0.4
A harassment areas are provided for species hearing groups for which Level A take is authorized.
B harassment areas are germane to all species.
Estimated Take—A description of the
methods used to estimate take
anticipated to occur from the project is
found in the project’s aforementioned
documents. The methods (i.e.,
equations) and rational for estimating
take in the proposed IHA (83 FR 30421,
June 28, 2018) for all species remains
unchanged; however, we adjusted the
number of days of pile driving factored
into the takes estimates in the issued
IHA. For harbor porpoise and harbor
seals, as described below, we also made
additional small adjustments to the final
take estimates based on other factors, as
recommended in comments made by the
Commission (see Comments and
Responses). Densities presented in the
proposed IHA (83 FR 30421, June 28,
2018) remain unchanged (Table 5). For
density based estimates, the equation
used is density × area ensonified above
the threshold × number of pile driving
days summed across all piles types. For
harbor porpoise, we calculated take
using the density identified in Table 5.
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For 24-in and 30-in piles: 0.75 × 66 km2
× 58 days (vibratory installation and
removal) equals 2,871 animals. For 36in piles: 0.75 × 69 km2 × 2 days equals
104 animals. For 78-in and 120-in piles:
0.75 × 107 km2 × 2 days = 161 animals.
In total, we calculated 3,136 harbor
porpoise could be taken. However,
marine mammal monitoring conducted
under the 2017 IHA yielded only 85
harbor porpoise sightings of which 28
were taken by harassment. In the notice
of proposed IHA (83 FR 30421, June 28,
2018), we proposed authorizing 10
percent of the calculated take (which
incorrectly considered an additional
two days of pile driving) as the raw
calculated take greatly exceeded
expected take based on previous marine
mammal monitoring efforts around the
terminal (e.g., WSDOT, 2018). However,
the Commission was concerned this
approach may yield an underestimate of
potential take. Therefore, we increased
the number of takes to 25 percent of the
total calculated take for a total of 784
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Level B harassment takes. The
Commission was also concerned the
calculated number of Level A
harassment takes using the full density
provided in Smultea et al. (2017) (n=7)
would also be an underestimate. Based
on the Commission’s recommendation
to assume one group of three harbor
porpoise could be within the Level A
harassment area on half of the pile
driving days where the potential for
Level A harassment exists, (13 of the 26
days) we issued 39 Level A harassment
takes for harbor porpoise.
We repeated these calculations using
the approach above for Dall’s porpoise,
minke whales, humpback whales, gray
whales, and Steller sea lions; however,
we are not authorizing Level A
harassment take for the latter three
species as the potential for Level A
harassment of these species is
discountable due to high visibility of
these species, small Level A harassment
zones, and implementation of mitigation
measures (e.g., shut downs). We
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considered Dall’s porpoise to have the
same potential to be taken by Level A
harassment as harbor porpoise due to
similar size and sightibility; therefore,
we issued the same amount of Level A
take for both species (n=39).
We also used the same method and
rational for estimates utilizing direct
counts instead of density estimates as in
the proposed IHA (83 FR 30421, June
28, 2018), but again, adjusted the
number of days considered. Over 51
days of marine mammal monitoring
during the 2017/18 Mukilteo project,
1,525 harbor seals were observed or 30
harbor seals per day. Using the equation
# of animals/day * # of days, we
authorized 1860 Level B harassment
takes (30 animals/day * 62 days). As
described in the notice of proposed IHA
(83 FR 30421, June 28, 2018), we
consider five percent of that amount
could be animals taken by Level A
harassment (n=93). Based on previous
marine mammal monitoring data
(WSDOT, 2018), we estimated 14
California sea lions per day could be
taken on the 62 days of pile driving for
a total of 868 Level B harassment takes.
As described in the notice of proposed
IHA (83 FR 30421, June 28, 2018), we
did not authorize Level A harassment
because the Level A harassment zones
are very small based on one to three
hours of pile driving and no California
sea lions were taken by Level A
harassment under the 2017 IHA. The
method used to estimate take for
transient killer whales also remained
unchanged from the proposed IHA (83
FR 30421, June 28, 2018); however, we
adjusted the number of days in the
equation and authorized 19 takes of
transient killer whales (0.3 whales/km2
× 62 days). No change was necessary to
the methods, rational, and amount of
take identified in the proposed IHA (83
FR 30421, June 28, 2018) for humpback
whales, gray whales, Northern elephant
seals, bottlenose dolphins, and longbeaked common dolphins because
number of days was not a component of
the take estimation process. See Table 6
for all authorized take numbers, by
species, and the respective amount of
the population that take represents.
TABLE 6—AUTHORIZED TAKE AMOUNT, PER SPECIES, RELATIVE TO POPULATION SIZE
Level A
Harbor seal ......................................................................................................
California sea lion ............................................................................................
N. elephant seal ...............................................................................................
Killer whale-transient .......................................................................................
SSL ..................................................................................................................
Gray whale .......................................................................................................
Humpback whale .............................................................................................
Dall’s porpoise .................................................................................................
Harbor porpoise ...............................................................................................
Minke whale .....................................................................................................
Bottlenose dolphin ...........................................................................................
Long-beaked common dolphin ........................................................................
Description of Mitigation, Monitoring
and Reporting Measures—A description
of mitigation, monitoring, and reporting
measures is found in the previous
documents, and we have included
additional details based on the
Commission’s comments (see Comments
Level B
93
0
0
0
0
0
0
39
39
0
0
0
Total take
1,860
868
7
19
154
2
6
163
784
7
49
49
and Responses section). In summary,
mitigation includes use of an
unconfined bubble curtain (with
operational standards set by the U.S.
Fish and Wildlife Service), soft start
techniques during impact pile driving in
greater than 2 ft of water, a minimum 10
1953
868
7
19
154
2
6
202
823
7
49
49
% Population
18
0.3
>0.1
8
0.2
0.02
0.3
0.8
7.3
1.3
10.8
0.04
m shut down zone, and speciesdependent shut down zones as
described in Table 7. Some of these shut
down zones fully encompass the Level
A harassment zone; however, for species
where we propose Level A take, this
might not always be the case.
TABLE 7—SHUT-DOWN ZONES
Level A (meters)
Method
MF
HF
PH
OT
Level B 1
(m)
10
10
20
........................
........................
........................
50
150
200
........................
........................
........................
20
60
........................
........................
........................
........................
10
........................
........................
........................
........................
20
8,000
8,000
8,690
20,000
........................
1,585
Pile size
LF
Vibratory .......................
Impact ..........................
24
30
36
78
120
24
35
105
170
205
130
435
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1 The Level B harassment shutdown zone applies to only those species for which take is not authorized (e.g., southern resident killer whales)
or when take for a given species is exceeded.
Monitoring requirements would be
similar to the 2017 IHA requirements
(see an updated Marine Mammal
Monitoring Plan available at https://
www.fisheries.noaa.gov/node/23111);
however, we have added additional
reporting requirements (see Comments
and Responses section). The number
and location of Protected Species
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Observers (PSOs) is dependent upon
activity and weather conditions and are
as follows:
(i) Three land-based PSOs during
impact driving of 24-in piles;
(ii) four land-based and one ferrybased PSOs during 24-, 30-, 36-in steel
vibratory driving/removal;
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Fmt 4703
Sfmt 4703
(iii) five land-based and one ferrybased PSOs during 78- and 120 in steel
vibratory driving/removal; and
(iv) two ferry-based PSOs in addition
to land-based PSOs when weather
conditions are poor.
In April, 2018, WSDOT submitted a
monitoring report for construction that
had been completed under the 2017
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IHA. WSDOT complied with all
mitigation, monitoring, and reporting
protocols. Recorded takes were below
the number authorized for the
corresponding amount of work. The
monitoring report can be viewed on
NMFS’s website at https://
www.fisheries.noaa.gov/node/23111.
WSDOT will conduct acoustic
monitoring during impact pile driving
of 24-in piles per the acoustic
monitoring plan submitted for the
previous IHA. WSDOT will also
conduct acoustic monitoring during
vibratory driving 78-in and 120-in piles.
Both the impact and vibratory acoustic
monitoring plans are available at
https://www.fisheries.noaa.gov/node/
23111.
Comments and Responses
A notice of NMFS’ proposal to issue
an IHA was published in the Federal
Register on June 28, 2018 (83 FR 30421).
During the 30-day public comment
period, the Marine Mammal
Commission (Commission) submitted a
letter, providing comments as described
below.
Comment 1: The Commission
recommends that NMFS issue the IHA,
subject to inclusion of modified
mitigation, monitoring and reporting
measures. Specifically, the Commission
recommended WSDOT submit more
detailed marine mammal monitoring
reports that include observer location,
the extent of zones for each activity, the
distances/bearing from the PSO to the
animal and from the animal to the
source for each sighting, whether
mitigation was implemented. The
Commission also suggested the acoustic
monitoring report should include both
medians and means for peak and rootmean-square sound pressure levels and
single-strike and cumulative sound
exposure levels.
NMFS Response: NMFS has included
the Commission’s recommended marine
mammal monitoring and acoustic
monitoring data in the IHA.
Comment 2: The Commission
recommends increasing the amount of
take authorized for harbor porpoises to
39 Level A takes and 3,135 Level B
takes. The premise for this comment is
that the estimated density of harbor
porpoise of 0.75 (Smultea et al., 2017)
should be used to calculate Level B
harassment takes in absence of
considering the amount of harbor
porpoise takes identified during marine
mammal monitoring the previous work
year. During informal discussion prior
to submitting their letter, the
Commission indicated that previous
monitoring should not be considered
because the Level B harassment area is
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large and some harbor porpoise could
have been missed during monitoring. In
contrast, the Commission recommended
the estimated harbor porpoise density
(Smultea et al., 2017) not be used to
estimate Level A harassment take but
should be increased to consider a group
of three harbor porpoise entering the
Level A harassment zone on half of the
days pile driving would occur (i.e., 31
out of 62 days).
NMFS Response: As described in the
notice of proposed IHA (83 FR 30421,
June 28, 2018), marine mammal
monitoring conducted under the 2017
IHA yielded 85 harbor porpoise
sightings of which 28 were taken by
harassment (i.e., observed within the
harassment zones during pile work).
Further, during informal
correspondence with the Commission
on this matter, NMFS indicated WSDOT
employed no fewer than five PSOs
during pile driving with additional
PSOs placed on vessels under various
circumstances (e.g., inclement weather,
impact pile driving). The PSOs were
stationed, per the IHA, in various
locations at and around the harassment
zones. Therefore, there was good
observer coverage of the harassment
area and the likelihood of harbor
porpoise being undetected was low.
Considering the number of piles driven
under this IHA is less than last year’s
IHA, to use the density of harbor
porpoise reported in Smultea et al.
(2017) without consideration of these
monitoring data would be a gross
overestimate of take.
In the proposed IHA (83 FR 30421,
June 28, 2018), NMFS calculated the
number of harbor porpoise potentially
taken by Level B harassment using the
Smultea et al. (2017) density (i.e., 0.75
harbor porpoise) but then reduced the
resulting take to 10 percent of that
number in consideration of the previous
marine mammal monitoring results.
While NMFS continues to believe a
reduction factor is appropriate, we have
modified it to 25 percent of the original
calculation given the concerns of the
Commission. As a result, and in
consideration of the corrected number
of pile driving days (reduced from 65
days to 62 days for Level B harassment),
NMFS has issued 784 Level B
harassment takes (see Estimated Take
section for more details on these
calculations). In the proposed IHA (83
FR 30421, June 28, 2018), we also used
density to estimate the number of harbor
porpoise potentially taken by Level A
harassment but did not apply a
correction factor due to the low results
(n=7). Although the potential for Level
A harassment of harbor porpoise is low,
we accepted the Commission’s
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Fmt 4703
Sfmt 4703
recommendation and adjusted take
numbers to reflect group size in lieu of
using density, authorizing 39 Level A
harassment takes (see Estimated Take
section).
Comment 3: The Commission
recommended NMFS modify the
number of takes of marine mammals
based on agreements made during
informal correspondence. Specially, the
Commission reiterated NMFS
commitment to not use a reduction
factor for harbor seals and correct the
number of pile driving days used in the
take estimates.
NMFS Response: As indicated during
informal correspondence with the
Commission, NMFS has revised the
number of takes in a manner consistent
with the methods identified in the
Commission’s letter.
Comment 4: The Commission
requested clarification regarding certain
issues associated with NMFS’ notice
that one-year renewals could be issued
in certain limited circumstances and
expressed concern that the process
would bypass the public notice and
comment requirements. The
Commission also suggested that NMFS
should discuss the possibility of
renewals through a more general route,
such as a rulemaking, instead of notice
in a specific authorization. The
Commission further recommended that
if NMFS did not pursue a more general
route, that the agency provide the
Commission and the public with a legal
analysis supporting our conclusion that
this process is consistent with the
requirements of section 101(a)(5)(D) of
the MMPA. The Commission also noted
that NMFS had recently begun utilizing
abbreviated notices, referencing relevant
documents, to solicit public input and
suggested that NMFS use these notices
and solicit review in lieu of the renewal
process.
NMFS Response: The process of
issuing a renewal IHA does not bypass
the public notice and comment
requirements of the MMPA. The notice
of the proposed IHA (83 FR 30421, June
28, 2018) expressly notifies the public
that under certain, limited conditions an
applicant could seek a renewal IHA for
an additional year. The notice describes
the conditions under which such a
renewal request could be considered
and expressly seeks public comment in
the event such a renewal is sought.
Additional reference to this solicitation
of public comment has recently been
added at the beginning of the FR notices
that consider renewals, requesting input
specifically on the possible renewal
itself. NMFS appreciates the
streamlining achieved by the use of
abbreviated FR notices and intends to
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continue using them for proposed IHAs
that include minor changes from
previously issued IHAs, but which do
not satisfy the renewal requirements.
However, we believe our method for
issuing renewals meets statutory
requirements and maximizes efficiency.
Importantly, such renewals would be
limited to circumstances where: The
activities are identical or nearly
identical to those analyzed in the
proposed IHA; monitoring does not
indicate impacts that were not
previously analyzed and authorized;
and, the mitigation and monitoring
requirements remain the same, all of
which allow the public to comment on
the appropriateness and effects of a
renewal at the same time the public
provides comments on the initial IHA.
NMFS has, however, modified the
language for future proposed IHAs to
clarify that all IHAs, including renewal
IHAs, are valid for no more than one
year and that the agency would consider
only one renewal for a project at this
time. In addition, notice of issuance or
denial of a renewal IHA would be
published in the Federal Register, as
they are for all IHAs. The option for
issuing renewal IHAs has been in
NMFS’s incidental take regulations
since 1996. We will provide any
additional information to the
Commission and consider posting a
description of the renewal process on
our website before any renewal is issued
utilizing this process.
Negligible Impact Analysis and
Determination
WSDOT proposes to conduct a subset
of activities identical to those covered in
the previous 2017 IHA. We have
included take for three new species
noting these are precautionary as these
species are not common in the action
area and these species were not
observed during previous construction.
We also believe the potential behavioral
reactions and effects on the cetacean
species previously analyzed is
applicable to these species, if not to
some lesser extent due to lower
probability of occurrence.
When issuing the 2017 IHA, NMFS
found Phase 2 of the Mukilteo
Multimodal Project, in its entirety,
would have a negligible impact to
species or stocks’ rates of recruitment
and survival and the amount of taking
would be small relative to the
population size of such species or stock
(less than 15 percent). As described
above, the number of estimated takes of
the same stocks are less than takes
authorized in the 2017 IHA and the
anticipated impacts from the project are
similar to those previously analyzed.
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20:00 Aug 27, 2018
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The amount of take for the additional
three species is also small (less than 11
percent of each stock). In conclusion,
there is no new information suggesting
that our analysis or findings should
change.
In this year’s IHA, we have also
included more mitigation with respect
to operating the bubble curtains (to
ensure effectiveness; thereby,
potentially reducing impact pile driving
received levels), and required WSDOT
to report more details pertaining to
monitoring (see Mitigation, Monitoring,
and Reporting section). WSDOT will
also conduct vibratory pile driving
acoustic monitoring which will allow
for verification of estimated source
levels.
Based on the information contained
here and in the referenced documents,
NMFS has determined the following: (1)
The required mitigation measures will
effect the least practicable impact on
marine mammal species or stocks and
their habitat; (2) the authorized takes
will have a negligible impact on the
affected marine mammal species or
stocks; (3) the authorized takes
represent small numbers of marine
mammals relative to the affected stock
abundances; and (4) WSDOT’s activities
will not have an unmitigable adverse
impact on taking for subsistence
purposes as no relevant subsistence uses
of marine mammals are implicated by
this action.
Endangered Species Act
Section 7(a)(2) of the Endangered
Species Act of 1973 (ESA: 16 U.S.C.
1531 et seq.) requires that each Federal
agency insure that any action it
authorizes, funds, or carries out is not
likely to jeopardize the continued
existence of any endangered or
threatened species or result in the
destruction or adverse modification of
designated critical habitat. To ensure
ESA compliance for the issuance of
IHAs, NMFS consults internally, in this
case with the West Coast Region
Protected Resources Division Office,
whenever we propose to authorize take
for endangered or threatened species.
The only species listed under the ESA
with the potential to be present in the
action area is the Mexico Distinct
Population Segment (DPS) of humpback
whales. The effects of this proposed
Federal action were adequately
analyzed in NMFS’ Biological Opinion
for the Mukilteo Multimodal Project,
Snohomish, Washington, dated August
1, 2017, which concluded that issuance
of an IHA would not jeopardize the
continued existence of any endangered
or threatened species or destroy or
adversely modify any designated critical
PO 00000
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Fmt 4703
Sfmt 4703
43855
habitat. NMFS West Coast Region has
confirmed the Incidental Take
Statement (ITS) issued in 2017 is
applicable for the IHA. That ITS
authorizes the take of six humpback
whales from the Mexico DPS.
National Environmental Policy Act
To comply with the National
Environmental Policy Act of 1969
(NEPA; 42 U.S.C. 4321 et seq.) and
NOAA Administrative Order (NAO)
216–6A, NMFS must review our
proposed action (i.e., the issuance of an
incidental harassment authorization)
with respect to potential impacts on the
human environment.
This action is consistent with
categories of activities identified in
Categorical Exclusion B4 (incidental
harassment authorizations with no
anticipated serious injury or mortality)
of the Companion Manual for NOAA
Administrative Order 216–6A, which do
not individually or cumulatively have
the potential for significant impacts on
the quality of the human environment
and for which we have not identified
any extraordinary circumstances that
would preclude this categorical
exclusion. Accordingly, NMFS has
determined that issuance of the IHA
qualifies to be categorically excluded
from further NEPA review. We have
reviewed all comments submitted in
response to the proposed IHA Federal
Register notice (83 FR 30421, June 28,
2018) prior to concluding our NEPA
process and making a final decision on
the IHA request.
Authorization
As a result of these determinations,
NMFS has issued an IHA to WSDOT for
the harassment of small numbers of
marine mammals incidental to
construction activities related to the
Mukilteo Multimodal Project, Puget
Sound, Washington, provided the
previously mentioned mitigation,
monitoring, and reporting requirements
are incorporated.
Dated: August 23, 2018.
Cathryn E. Tortorici,
Acting Director, Office of Protected Resources,
National Marine Fisheries Service.
[FR Doc. 2018–18609 Filed 8–27–18; 8:45 am]
BILLING CODE 3510–22–P
COMMODITY FUTURES TRADING
COMMISSION
Agency Information Collection
Activities Under OMB Review
Commodity Futures Trading
Commission.
AGENCY:
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[Federal Register Volume 83, Number 167 (Tuesday, August 28, 2018)]
[Notices]
[Pages 43849-43855]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2018-18609]
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
RIN 0648-XG205
Takes of Marine Mammals Incidental to Specified Activities;
Taking Marine Mammals Incidental to the Mukilteo Multimodal Project--
Season 3
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Notice; issuance of incidental harassment authorization.
-----------------------------------------------------------------------
[[Page 43850]]
SUMMARY: In accordance with the regulations implementing the Marine
Mammal Protection Act (MMPA) as amended, notification is hereby given
that NMFS has issued an incidental harassment authorization (IHA) to
the Washington Department of Transportation (WSDOT) Ferries Division
(WSF) to incidentally take, by Level A and B harassment, marine mammals
during construction activities associated with the Mukilteo Multimodal
Project, Puget Sound, Washington.
DATES: This Authorization is effective from October 1, 2018, through
September 30, 2019.
FOR FURTHER INFORMATION CONTACT: Jaclyn Daly, Office of Protected
Resources, NMFS, (301) 427-8401. Electronic copies of the application,
IHA, and supporting documents, as well as a list of the references
cited in this document, may be obtained online at: https://www.fisheries.noaa.gov/node/23111. In case of problems accessing these
documents, please call the contact listed above.
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 (as delegated to NMFS) 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, a notice of a proposed
authorization is provided to the public for review.
An authorization for incidental takings shall be granted if NMFS
finds that the taking will have a negligible impact on the species or
stock(s), will not have an unmitigable adverse impact on the
availability of the species or stock(s) for subsistence uses (where
relevant), and if the permissible methods of taking and requirements
pertaining to the mitigation, monitoring and reporting of such takings
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. The MMPA states that the term ``take'' means to harass, hunt,
capture, kill or attempt to harass, hunt, capture, or kill any marine
mammal.
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).
Summary of Request
On April 7, 2016, WSDOT submitted a request to NMFS requesting an
IHA for the possible harassment of small numbers of marine mammals
incidental to construction associated with Phase 2 of the Mukilteo
Multimodal Project in Mukilteo, Washington, between August 1, 2017, and
July 31, 2018. NMFS issued the requested IHA on August 3, 2017, which
covered Phase 2 of the project in its entirety; the IHA expired on July
31, 2018 (82 FR 44164; September 21, 2017). On January 9, 2018, we
received a request from WSDOT for a subsequent authorization to take
marine mammals incidental to the project because all of the Phase 2
work would not be able to be completed under the existing IHA. A final
version of the application, which we deemed adequate and complete, was
submitted on March 1, 2018.
On June 28, 2018, NMFS published its proposed IHA in the Federal
Register for public comment (83 FR 30421). NMFS has issued an IHA to
WSDOT for the take, by Level A and B harassment, of 12 species of
marine mammals incidental to pile driving and removal associated with
the Mukilteo Multimodal Project.
Description of the Specified Activity and Anticipated Impacts
WSDOT operates and maintains 19 ferry terminals and one maintenance
facility, all of which are located in Puget Sound or the San Juan
Islands (Georgia Basin) (Figure 1-1 in WSDOT's application). The
Mukilteo Multimodal Project is a multi-year construction project
designed to improve the operations and facilities serving the mainland
terminus of the Mukilteo-Clinton ferry route in Washington State. The
2017 IHA covered the installation of 661 piles of various sizes over an
estimated 175 days of pile driving and removal (Table 1). WSDOT did not
complete all the work; therefore the issued IHA covers take incidental
to the installation of the remaining piles (Table 1). The 2017 IHA
authorized Level A and B harassment of two species of marine mammals
and Level B harassment of seven species of marine mammals. NMFS has
issued an IHA to harass these same species and an additional three
species based on recent marine mammal monitoring near the project area
(Table 2).
We refer to the notice of proposed IHA (83 FR 30421, June 28, 2018)
and documents related to the previously issued 2017 IHA and discuss any
new or changed information here. Previous documents include the Federal
Register notice of the proposed 2017 IHA (82 FR 29713; May 10, 2017),
Federal Register notice of issuance of the 2017 IHA (82 FR 44164,
September 21, 2017), and all associated references and documents. We
also refer the reader to WSDOT's previous and current applications and
monitoring reports. All of these documents may be found at https://www.fisheries.noaa.gov/node/23111.
Detailed Description of the Action--A detailed description of the
vibratory and impact pile driving and removal activities at the
Mukilteo Terminal is found in the aforementioned documents. The
location, timing, and nature of the pile driving operations, including
the type and size of piles and the methods of pile driving, are
identical to those described in the previous notices, except that only
a subset of the type and number of piles are to be driven because some
of the work was completed under the 2017 IHA. Under the issued IHA
(2018-2019), 116 piles would be installed with a vibratory hammer. Of
those, sixty-five 24-inch (in) piles would also be proofed with an
impact hammer and then removed.
WSDOT anticipates piles equal to or less than 36-in would be
installed at a rate of 3 per day for a total of 38 days. Removing the
65 24-in temporary piles may also occur at a rate of 3 pile per day for
a total of 22 days. An additional two days is needed to install the 78-
in piles and 120-in pile. In total, up to 62 days of pile driving and
removal may occur. WSDOT anticipates pile driving and removal could
occur over a seven month in-water work window (July 15-February 15).
[[Page 43851]]
Table 1--Description of Work Planned, Analyzed, and Completed Under the 2017 IHA and Remaining Work Planned for 2018-2019
--------------------------------------------------------------------------------------------------------------------------------------------------------
Season 2 Season 3
Method Pile size (in) planned Season 2 planned Number of Comment
(2017 IHA) completed (2018 IHA) days
--------------------------------------------------------------------------------------------------------------------------------------------------------
Vibratory Driving............... 12.................. 139 134 0 0 Fewer needed, complete.
24.................. 69 4 \1\ 65 22 Up to 69 temporary.
24.................. 48 0 26 9 Fewer needed, permanent.
30.................. 40 25 16 5 Permanent.
36.................. 6 0 6 2 Permanent.
78.................. 2 0 2 1 Permanent.
120................. 1 0 1 1 Permanent.
sheet............... 90 0 0 0 Design change, not needed.
Vibratory Removal............... 24.................. 69 4 \1\ 65 22 Temporary.
30.................. 9 0 0 0 Delayed.
sheet............... 90 0 0 0 Design change, not needed.
Impact Driving.................. 24.................. 69 4 \1\ 65 \2\ 22 Proofed for load-bearing.
30.................. 30 25 0 0 Fewer needed, complete.
--------------------------------------------------------------------------------------------------------------------------------------------------------
\1\ These 65 piles represent the same 65 temporary 24'' piles driven with a vibratory hammer. The temporary piles would be installed, proofed, and
removed.
\2\ Impact hammering would be conducted on same day as vibratory pile driving so these are not additional days.
Description of Marine Mammals--A description of the marine mammals
in the area of the activities is found in the notice of proposed IHA
(83 FR 30421, June 28, 2018). This information remains valid so we do
not repeat it here but provide a summary table with marine mammal
species and stock details.
Table 2--Species and Stocks Expected To Occur in Project Area
--------------------------------------------------------------------------------------------------------------------------------------------------------
ESA/MMPA status; Stock abundance (CV,
Common name Scientific name Stock strategic (Y/N) Nmin, most recent PBR Annual M/
\1\ abundance survey) \2\ SI \3\
--------------------------------------------------------------------------------------------------------------------------------------------------------
Order Cetartiodactyla--Cetacea--Superfamily Mysticeti (baleen whales)
--------------------------------------------------------------------------------------------------------------------------------------------------------
Family Eschrichtiidae:
Gray whale...................... Eschrichtius robustus.. Eastern North Pacific.. N 20,990 (0.05, 20,125, 624 132
2014).
Family Balaenopteridae (rorquals):
Humpback whale.................. Megaptera novaeangliae. California/Oregon/ Y 1,918 (0.03, 1,876, 11.0 9.2
Washington. 2017).
Minke whale *................... Balaenoptera California/Oregon/ N 636 (0.72, 369, 2016). 3.5 1.3
acutorostrata. Washington.
--------------------------------------------------------------------------------------------------------------------------------------------------------
Superfamily Odontoceti (toothed whales, dolphins, and porpoises)
--------------------------------------------------------------------------------------------------------------------------------------------------------
Family Delphinidae:
Killer whale.................... Orcinus orca........... Eastern North Pacific Y 76 (n/a, 76, 2017) \4\ 0 0.14
Southern Resident.
West coast transient... N unk (unk, 243 2013)... 2.4 0
Bottlenose dolphin *............ Tursiops truncatus..... California coastal..... N 453 (0.06, 346, 2016). 2.7 >=2
Long-beaked common dolphin *.... Delphinus delphis California............. N 101,305 (0.49, 68,432, 657 35.4
bairdii. 2016).
Family Phocoenidae (porpoises):
Harbor porpoise................. Phocoena............... Washington inland N 11,233 (0.37, 8,308, 66 7.2
waters. 2016).
Dall's porpoise................. Phocoenoides dalli..... California/Oregon/ N 25,750 (0.45, 17,954, 172 0.3
Washington. 2016).
--------------------------------------------------------------------------------------------------------------------------------------------------------
Order Carnivora--Superfamily Pinnipedia
--------------------------------------------------------------------------------------------------------------------------------------------------------
Family Otariidae (eared seals and
sea lions):
California sea lion............. Zalophus californianus. U.S.................... N 296,750 (n/a, 153,337, 9,200 389
2014).
Steller sea lion................ Eumetopias jubatus..... Eastern U.S............ N 52,139 (n/a, 41,638, 2,498 108
2015).
Family Phocidae (earless seals):
Harbor seal..................... Phoca vitulina......... Washington northern N 11,036 (0.15, 1999)... 1,641 43
inland waters.
Elephant seal................... Mirounga angustirostris California breeding.... N 179,000 (n/a, 81,368, 2,882 8.8
2014).
--------------------------------------------------------------------------------------------------------------------------------------------------------
\1\ Endangered Species Act (ESA) status: Endangered (E), Threatened (T)/MMPA status: Depleted (D). A dash (-) indicates that the species is not listed
under the ESA or designated as depleted under the MMPA. Under the MMPA, a strategic stock is one for which the level of direct human-caused mortality
exceeds PBR or which is determined to be declining and likely to be listed under the ESA within the foreseeable future. Any species or stock listed
under the ESA is automatically designated under the MMPA as depleted and as a strategic stock.
\2\ NMFS marine mammal stock assessment reports online at: www.nmfs.noaa.gov/pr/sars/. CV is coefficient of variation; Nmin is the minimum estimate of
stock abundance.
\3\ These values, found in NMFS's SARs, represent annual levels of human-caused mortality plus serious injury from all sources combined (e.g.,
commercial fisheries, ship strike). Annual M/SI often cannot be determined precisely and is in some cases presented as a minimum value or range. A CV
associated with estimated mortality due to commercial fisheries is presented in some cases.
\4\ SRWK population abundance as of December 31, 2017 according to the Center for Whale Research.
[[Page 43852]]
\5\ Harbor seal estimate is based on data that are greater than 8 years old, but this is the best available information for use here.
* Indicates species added.
Harassment Zones--The harassment threshold distances and areas
provided in the Federal Register notice of proposed IHA (83 FR 30421,
June 28, 2018) remain unchanged. Please refer to that document
documents for details; we provide a summary tables here (Table 3 and
4).
Table 3--Level A Harassment Distances Considering Pile Driving Duration per 24 Hours
--------------------------------------------------------------------------------------------------------------------------------------------------------
Level A (meters)
Method Pile size Source level (dB) ----------------------------------------------------------------- Level B (m)
LF \1\ MF \1\ HF \1\ PH \1\ OT \1\
--------------------------------------------------------------------------------------------------------------------------------------------------------
Vibratory........................... 24 166 rms \2\............ 30.6 2.7 45.3 18.6 1.3 \6\ 8,000
30 174 rms \3\............ 104.5 9.3 154.5 63.5 4.5 \6\ 8,000
36 177 rms \3\............ 165.6 14.7 244.9 100.7 7.1 \7\ 8,700
78 180 rms \4\............ 200.3 17.8 296.2 121.8 8.5 \8\ 20,000
120 180 rms \4\............ 126.2 11.2 186.6 76.7 5.4 ...........
Impact.............................. 24 178 SEL (single strike)/ 432.1 15.4 514.7 231.2 16.8 1,585
193 rms \5\.
--------------------------------------------------------------------------------------------------------------------------------------------------------
\1\ The abbreviatation mean: LF = low frequency cetacean, MF = mid-frequency cetacean, HF = high-frequency cetacean, PH = phocid, OT = otariid.
\2\ We assume vibratory removal and vibratory driving the same size pile would result in equal sound levels. Source level for 24'' piles is based on
direct measurements during the Manette Bridge project (Loughlin, 2010a).
\3\ Source levels for 30-in and 36-in piles is based on direct measurements during the Port Townsend Project (Loughlin, 2010b).
\4\ WSDOT does not have noise data for 78 and 120-in piles; therefore, we used data from Caltrans (2015).
\5\ Single strike SEL and rms values for impact driving 24-in piles is based on direct measurements during pile driving using a bubble curtain (i.e.,
source levels are attenuated) at the Coupeville Terminal (WSDOT, 2017).
\6\ Measurements during 30'' vibratory pile driving at Mukilteo in 2017 indicate pile driving was not detected at range of 7.9 km (Laughlin, 2017a).
This equates to 66 km\2\.
\7\ At the Coleman Terminal, vibratory installation of two 36'' piles driven simultaneously was not detectable at 8.69 km (5.4 miles) (Laughlin 2017b).
This equates to 69 km\2\.
\8\ The calculated Level B zone using a practical spreading loss model is 100,000 m; however, land is reached at a maximum of 20,000 m (Lowell Point on
Camano Island). This equates to 107 km\2\.
Table 4--Corresponding Harassment Threshold Ensonified Areas
----------------------------------------------------------------------------------------------------------------
Level A (km\2\) \1\
Method Pile size ------------------------------------------------ Level B
HF PH OT (km\2\) \2\
----------------------------------------------------------------------------------------------------------------
Vibratory....................... 24 <0.01 <0.01 <0.01 66
30 <0.01 <0.01 .............. 66
36 0.06 0.06 .............. 69
78 0.01 0.01 .............. 107
120 0.01 0.01 .............. ..............
Impact.......................... 24 0.4 0.4 .............. 4
----------------------------------------------------------------------------------------------------------------
\1\ Level A harassment areas are provided for species hearing groups for which Level A take is authorized.
\2\ Level B harassment areas are germane to all species.
Estimated Take--A description of the methods used to estimate take
anticipated to occur from the project is found in the project's
aforementioned documents. The methods (i.e., equations) and rational
for estimating take in the proposed IHA (83 FR 30421, June 28, 2018)
for all species remains unchanged; however, we adjusted the number of
days of pile driving factored into the takes estimates in the issued
IHA. For harbor porpoise and harbor seals, as described below, we also
made additional small adjustments to the final take estimates based on
other factors, as recommended in comments made by the Commission (see
Comments and Responses). Densities presented in the proposed IHA (83 FR
30421, June 28, 2018) remain unchanged (Table 5). For density based
estimates, the equation used is density x area ensonified above the
threshold x number of pile driving days summed across all piles types.
For harbor porpoise, we calculated take using the density identified in
Table 5. For 24-in and 30-in piles: 0.75 x 66 km\2\ x 58 days
(vibratory installation and removal) equals 2,871 animals. For 36-in
piles: 0.75 x 69 km\2\ x 2 days equals 104 animals. For 78-in and 120-
in piles: 0.75 x 107 km\2\ x 2 days = 161 animals. In total, we
calculated 3,136 harbor porpoise could be taken. However, marine mammal
monitoring conducted under the 2017 IHA yielded only 85 harbor porpoise
sightings of which 28 were taken by harassment. In the notice of
proposed IHA (83 FR 30421, June 28, 2018), we proposed authorizing 10
percent of the calculated take (which incorrectly considered an
additional two days of pile driving) as the raw calculated take greatly
exceeded expected take based on previous marine mammal monitoring
efforts around the terminal (e.g., WSDOT, 2018). However, the
Commission was concerned this approach may yield an underestimate of
potential take. Therefore, we increased the number of takes to 25
percent of the total calculated take for a total of 784 Level B
harassment takes. The Commission was also concerned the calculated
number of Level A harassment takes using the full density provided in
Smultea et al. (2017) (n=7) would also be an underestimate. Based on
the Commission's recommendation to assume one group of three harbor
porpoise could be within the Level A harassment area on half of the
pile driving days where the potential for Level A harassment exists,
(13 of the 26 days) we issued 39 Level A harassment takes for harbor
porpoise.
We repeated these calculations using the approach above for Dall's
porpoise, minke whales, humpback whales, gray whales, and Steller sea
lions; however, we are not authorizing Level A harassment take for the
latter three species as the potential for Level A harassment of these
species is discountable due to high visibility of these species, small
Level A harassment zones, and implementation of mitigation measures
(e.g., shut downs). We
[[Page 43853]]
considered Dall's porpoise to have the same potential to be taken by
Level A harassment as harbor porpoise due to similar size and
sightibility; therefore, we issued the same amount of Level A take for
both species (n=39).
We also used the same method and rational for estimates utilizing
direct counts instead of density estimates as in the proposed IHA (83
FR 30421, June 28, 2018), but again, adjusted the number of days
considered. Over 51 days of marine mammal monitoring during the 2017/18
Mukilteo project, 1,525 harbor seals were observed or 30 harbor seals
per day. Using the equation # of animals/day * # of days, we authorized
1860 Level B harassment takes (30 animals/day * 62 days). As described
in the notice of proposed IHA (83 FR 30421, June 28, 2018), we consider
five percent of that amount could be animals taken by Level A
harassment (n=93). Based on previous marine mammal monitoring data
(WSDOT, 2018), we estimated 14 California sea lions per day could be
taken on the 62 days of pile driving for a total of 868 Level B
harassment takes. As described in the notice of proposed IHA (83 FR
30421, June 28, 2018), we did not authorize Level A harassment because
the Level A harassment zones are very small based on one to three hours
of pile driving and no California sea lions were taken by Level A
harassment under the 2017 IHA. The method used to estimate take for
transient killer whales also remained unchanged from the proposed IHA
(83 FR 30421, June 28, 2018); however, we adjusted the number of days
in the equation and authorized 19 takes of transient killer whales (0.3
whales/km\2\ x 62 days). No change was necessary to the methods,
rational, and amount of take identified in the proposed IHA (83 FR
30421, June 28, 2018) for humpback whales, gray whales, Northern
elephant seals, bottlenose dolphins, and long-beaked common dolphins
because number of days was not a component of the take estimation
process. See Table 6 for all authorized take numbers, by species, and
the respective amount of the population that take represents.
Table 6--Authorized Take Amount, per Species, Relative to Population Size
----------------------------------------------------------------------------------------------------------------
Level A Level B Total take % Population
----------------------------------------------------------------------------------------------------------------
Harbor seal..................................... 93 1,860 1953 18
California sea lion............................. 0 868 868 0.3
N. elephant seal................................ 0 7 7 >0.1
Killer whale-transient.......................... 0 19 19 8
SSL............................................. 0 154 154 0.2
Gray whale...................................... 0 2 2 0.02
Humpback whale.................................. 0 6 6 0.3
Dall's porpoise................................. 39 163 202 0.8
Harbor porpoise................................. 39 784 823 7.3
Minke whale..................................... 0 7 7 1.3
Bottlenose dolphin.............................. 0 49 49 10.8
Long-beaked common dolphin...................... 0 49 49 0.04
----------------------------------------------------------------------------------------------------------------
Description of Mitigation, Monitoring and Reporting Measures--A
description of mitigation, monitoring, and reporting measures is found
in the previous documents, and we have included additional details
based on the Commission's comments (see Comments and Responses
section). In summary, mitigation includes use of an unconfined bubble
curtain (with operational standards set by the U.S. Fish and Wildlife
Service), soft start techniques during impact pile driving in greater
than 2 ft of water, a minimum 10 m shut down zone, and species-
dependent shut down zones as described in Table 7. Some of these shut
down zones fully encompass the Level A harassment zone; however, for
species where we propose Level A take, this might not always be the
case.
Table 7--Shut-Down Zones
--------------------------------------------------------------------------------------------------------------------------------------------------------
Level A (meters)
Method Pile size -------------------------------------------------------------------------------- Level B \1\
LF MF HF PH OT (m)
--------------------------------------------------------------------------------------------------------------------------------------------------------
Vibratory............................... 24 35 10 50 20 10 8,000
30 105 10 150 60 .............. 8,000
36 170 20 200 .............. .............. 8,690
78 205 .............. .............. .............. .............. 20,000
120 130 .............. .............. .............. .............. ..............
Impact.................................. 24 435 .............. .............. .............. 20 1,585
--------------------------------------------------------------------------------------------------------------------------------------------------------
\1\ The Level B harassment shutdown zone applies to only those species for which take is not authorized (e.g., southern resident killer whales) or when
take for a given species is exceeded.
Monitoring requirements would be similar to the 2017 IHA
requirements (see an updated Marine Mammal Monitoring Plan available at
https://www.fisheries.noaa.gov/node/23111); however, we have added
additional reporting requirements (see Comments and Responses section).
The number and location of Protected Species Observers (PSOs) is
dependent upon activity and weather conditions and are as follows:
(i) Three land-based PSOs during impact driving of 24-in piles;
(ii) four land-based and one ferry-based PSOs during 24-, 30-, 36-
in steel vibratory driving/removal;
(iii) five land-based and one ferry-based PSOs during 78- and 120
in steel vibratory driving/removal; and
(iv) two ferry-based PSOs in addition to land-based PSOs when
weather conditions are poor.
In April, 2018, WSDOT submitted a monitoring report for
construction that had been completed under the 2017
[[Page 43854]]
IHA. WSDOT complied with all mitigation, monitoring, and reporting
protocols. Recorded takes were below the number authorized for the
corresponding amount of work. The monitoring report can be viewed on
NMFS's website at https://www.fisheries.noaa.gov/node/23111.
WSDOT will conduct acoustic monitoring during impact pile driving
of 24-in piles per the acoustic monitoring plan submitted for the
previous IHA. WSDOT will also conduct acoustic monitoring during
vibratory driving 78-in and 120-in piles. Both the impact and vibratory
acoustic monitoring plans are available at https://www.fisheries.noaa.gov/node/23111.
Comments and Responses
A notice of NMFS' proposal to issue an IHA was published in the
Federal Register on June 28, 2018 (83 FR 30421). During the 30-day
public comment period, the Marine Mammal Commission (Commission)
submitted a letter, providing comments as described below.
Comment 1: The Commission recommends that NMFS issue the IHA,
subject to inclusion of modified mitigation, monitoring and reporting
measures. Specifically, the Commission recommended WSDOT submit more
detailed marine mammal monitoring reports that include observer
location, the extent of zones for each activity, the distances/bearing
from the PSO to the animal and from the animal to the source for each
sighting, whether mitigation was implemented. The Commission also
suggested the acoustic monitoring report should include both medians
and means for peak and root-mean-square sound pressure levels and
single-strike and cumulative sound exposure levels.
NMFS Response: NMFS has included the Commission's recommended
marine mammal monitoring and acoustic monitoring data in the IHA.
Comment 2: The Commission recommends increasing the amount of take
authorized for harbor porpoises to 39 Level A takes and 3,135 Level B
takes. The premise for this comment is that the estimated density of
harbor porpoise of 0.75 (Smultea et al., 2017) should be used to
calculate Level B harassment takes in absence of considering the amount
of harbor porpoise takes identified during marine mammal monitoring the
previous work year. During informal discussion prior to submitting
their letter, the Commission indicated that previous monitoring should
not be considered because the Level B harassment area is large and some
harbor porpoise could have been missed during monitoring. In contrast,
the Commission recommended the estimated harbor porpoise density
(Smultea et al., 2017) not be used to estimate Level A harassment take
but should be increased to consider a group of three harbor porpoise
entering the Level A harassment zone on half of the days pile driving
would occur (i.e., 31 out of 62 days).
NMFS Response: As described in the notice of proposed IHA (83 FR
30421, June 28, 2018), marine mammal monitoring conducted under the
2017 IHA yielded 85 harbor porpoise sightings of which 28 were taken by
harassment (i.e., observed within the harassment zones during pile
work). Further, during informal correspondence with the Commission on
this matter, NMFS indicated WSDOT employed no fewer than five PSOs
during pile driving with additional PSOs placed on vessels under
various circumstances (e.g., inclement weather, impact pile driving).
The PSOs were stationed, per the IHA, in various locations at and
around the harassment zones. Therefore, there was good observer
coverage of the harassment area and the likelihood of harbor porpoise
being undetected was low. Considering the number of piles driven under
this IHA is less than last year's IHA, to use the density of harbor
porpoise reported in Smultea et al. (2017) without consideration of
these monitoring data would be a gross overestimate of take.
In the proposed IHA (83 FR 30421, June 28, 2018), NMFS calculated
the number of harbor porpoise potentially taken by Level B harassment
using the Smultea et al. (2017) density (i.e., 0.75 harbor porpoise)
but then reduced the resulting take to 10 percent of that number in
consideration of the previous marine mammal monitoring results. While
NMFS continues to believe a reduction factor is appropriate, we have
modified it to 25 percent of the original calculation given the
concerns of the Commission. As a result, and in consideration of the
corrected number of pile driving days (reduced from 65 days to 62 days
for Level B harassment), NMFS has issued 784 Level B harassment takes
(see Estimated Take section for more details on these calculations). In
the proposed IHA (83 FR 30421, June 28, 2018), we also used density to
estimate the number of harbor porpoise potentially taken by Level A
harassment but did not apply a correction factor due to the low results
(n=7). Although the potential for Level A harassment of harbor porpoise
is low, we accepted the Commission's recommendation and adjusted take
numbers to reflect group size in lieu of using density, authorizing 39
Level A harassment takes (see Estimated Take section).
Comment 3: The Commission recommended NMFS modify the number of
takes of marine mammals based on agreements made during informal
correspondence. Specially, the Commission reiterated NMFS commitment to
not use a reduction factor for harbor seals and correct the number of
pile driving days used in the take estimates.
NMFS Response: As indicated during informal correspondence with the
Commission, NMFS has revised the number of takes in a manner consistent
with the methods identified in the Commission's letter.
Comment 4: The Commission requested clarification regarding certain
issues associated with NMFS' notice that one-year renewals could be
issued in certain limited circumstances and expressed concern that the
process would bypass the public notice and comment requirements. The
Commission also suggested that NMFS should discuss the possibility of
renewals through a more general route, such as a rulemaking, instead of
notice in a specific authorization. The Commission further recommended
that if NMFS did not pursue a more general route, that the agency
provide the Commission and the public with a legal analysis supporting
our conclusion that this process is consistent with the requirements of
section 101(a)(5)(D) of the MMPA. The Commission also noted that NMFS
had recently begun utilizing abbreviated notices, referencing relevant
documents, to solicit public input and suggested that NMFS use these
notices and solicit review in lieu of the renewal process.
NMFS Response: The process of issuing a renewal IHA does not bypass
the public notice and comment requirements of the MMPA. The notice of
the proposed IHA (83 FR 30421, June 28, 2018) expressly notifies the
public that under certain, limited conditions an applicant could seek a
renewal IHA for an additional year. The notice describes the conditions
under which such a renewal request could be considered and expressly
seeks public comment in the event such a renewal is sought. Additional
reference to this solicitation of public comment has recently been
added at the beginning of the FR notices that consider renewals,
requesting input specifically on the possible renewal itself. NMFS
appreciates the streamlining achieved by the use of abbreviated FR
notices and intends to
[[Page 43855]]
continue using them for proposed IHAs that include minor changes from
previously issued IHAs, but which do not satisfy the renewal
requirements. However, we believe our method for issuing renewals meets
statutory requirements and maximizes efficiency.
Importantly, such renewals would be limited to circumstances where:
The activities are identical or nearly identical to those analyzed in
the proposed IHA; monitoring does not indicate impacts that were not
previously analyzed and authorized; and, the mitigation and monitoring
requirements remain the same, all of which allow the public to comment
on the appropriateness and effects of a renewal at the same time the
public provides comments on the initial IHA. NMFS has, however,
modified the language for future proposed IHAs to clarify that all
IHAs, including renewal IHAs, are valid for no more than one year and
that the agency would consider only one renewal for a project at this
time. In addition, notice of issuance or denial of a renewal IHA would
be published in the Federal Register, as they are for all IHAs. The
option for issuing renewal IHAs has been in NMFS's incidental take
regulations since 1996. We will provide any additional information to
the Commission and consider posting a description of the renewal
process on our website before any renewal is issued utilizing this
process.
Negligible Impact Analysis and Determination
WSDOT proposes to conduct a subset of activities identical to those
covered in the previous 2017 IHA. We have included take for three new
species noting these are precautionary as these species are not common
in the action area and these species were not observed during previous
construction. We also believe the potential behavioral reactions and
effects on the cetacean species previously analyzed is applicable to
these species, if not to some lesser extent due to lower probability of
occurrence.
When issuing the 2017 IHA, NMFS found Phase 2 of the Mukilteo
Multimodal Project, in its entirety, would have a negligible impact to
species or stocks' rates of recruitment and survival and the amount of
taking would be small relative to the population size of such species
or stock (less than 15 percent). As described above, the number of
estimated takes of the same stocks are less than takes authorized in
the 2017 IHA and the anticipated impacts from the project are similar
to those previously analyzed. The amount of take for the additional
three species is also small (less than 11 percent of each stock). In
conclusion, there is no new information suggesting that our analysis or
findings should change.
In this year's IHA, we have also included more mitigation with
respect to operating the bubble curtains (to ensure effectiveness;
thereby, potentially reducing impact pile driving received levels), and
required WSDOT to report more details pertaining to monitoring (see
Mitigation, Monitoring, and Reporting section). WSDOT will also conduct
vibratory pile driving acoustic monitoring which will allow for
verification of estimated source levels.
Based on the information contained here and in the referenced
documents, NMFS has determined the following: (1) The required
mitigation measures will effect the least practicable impact on marine
mammal species or stocks and their habitat; (2) the authorized takes
will have a negligible impact on the affected marine mammal species or
stocks; (3) the authorized takes represent small numbers of marine
mammals relative to the affected stock abundances; and (4) WSDOT's
activities will not have an unmitigable adverse impact on taking for
subsistence purposes as no relevant subsistence uses of marine mammals
are implicated by this action.
Endangered Species Act
Section 7(a)(2) of the Endangered Species Act of 1973 (ESA: 16
U.S.C. 1531 et seq.) requires that each Federal agency insure that any
action it authorizes, funds, or carries out is not likely to jeopardize
the continued existence of any endangered or threatened species or
result in the destruction or adverse modification of designated
critical habitat. To ensure ESA compliance for the issuance of IHAs,
NMFS consults internally, in this case with the West Coast Region
Protected Resources Division Office, whenever we propose to authorize
take for endangered or threatened species.
The only species listed under the ESA with the potential to be
present in the action area is the Mexico Distinct Population Segment
(DPS) of humpback whales. The effects of this proposed Federal action
were adequately analyzed in NMFS' Biological Opinion for the Mukilteo
Multimodal Project, Snohomish, Washington, dated August 1, 2017, which
concluded that issuance of an IHA would not jeopardize the continued
existence of any endangered or threatened species or destroy or
adversely modify any designated critical habitat. NMFS West Coast
Region has confirmed the Incidental Take Statement (ITS) issued in 2017
is applicable for the IHA. That ITS authorizes the take of six humpback
whales from the Mexico DPS.
National Environmental Policy Act
To comply with the National Environmental Policy Act of 1969 (NEPA;
42 U.S.C. 4321 et seq.) and NOAA Administrative Order (NAO) 216-6A,
NMFS must review our proposed action (i.e., the issuance of an
incidental harassment authorization) with respect to potential impacts
on the human environment.
This action is consistent with categories of activities identified
in Categorical Exclusion B4 (incidental harassment authorizations with
no anticipated serious injury or mortality) of the Companion Manual for
NOAA Administrative Order 216-6A, which do not individually or
cumulatively have the potential for significant impacts on the quality
of the human environment and for which we have not identified any
extraordinary circumstances that would preclude this categorical
exclusion. Accordingly, NMFS has determined that issuance of the IHA
qualifies to be categorically excluded from further NEPA review. We
have reviewed all comments submitted in response to the proposed IHA
Federal Register notice (83 FR 30421, June 28, 2018) prior to
concluding our NEPA process and making a final decision on the IHA
request.
Authorization
As a result of these determinations, NMFS has issued an IHA to
WSDOT for the harassment of small numbers of marine mammals incidental
to construction activities related to the Mukilteo Multimodal Project,
Puget Sound, Washington, provided the previously mentioned mitigation,
monitoring, and reporting requirements are incorporated.
Dated: August 23, 2018.
Cathryn E. Tortorici,
Acting Director, Office of Protected Resources, National Marine
Fisheries Service.
[FR Doc. 2018-18609 Filed 8-27-18; 8:45 am]
BILLING CODE 3510-22-P