Document headings vary by document type but may contain
                    the following: the agency or agencies that issued and signed a document
the number of the CFR title and the number of each part
                      the document amends, proposes to amend, or is directly
                      related to
the agency docket number / agency internal file number
the RIN which identifies each regulatory action listed in
                      the Unified Agenda of Federal Regulatory and Deregulatory
                      Actions See the
                    Document Drafting Handbook
                    for more details.
 Department of Commerce National Oceanic and Atmospheric Administration RIN 0648-XF340
 AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and Atmospheric Administration (NOAA), Commerce.
 ACTION: Notice; issuance of an incidental harassment authorization.
 SUMMARY: In accordance with the regulations implementing the Marine Mammal Protection Act (MMPA) as amended, notification is hereby given that we have issued an incidental harassment authorization (IHA) to Washington State Department of Transportation (WSDOT) to take small numbers of marine mammals, by harassment, incidental to Mukilteo Multimodal Construction Project in Washington State.
 DATES: This authorization is effective from August 1, 2017, through July 31, 2018.
 FOR FURTHER INFORMATION CONTACT: Shane Guan, Office of Protected Resources, NMFS, (301) 427-8401. Electronic copies of the application and supporting documents, as well as the issued IHA, may be obtained online at: 
                        *www.nmfs.noaa.gov/​pr/​permits/​incidental/​construction.htm.*
                         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). National Environmental Policy Act Issuance of an MMPA 101(a)(5) authorization requires compliance with the National Environmental Policy Act. NMFS determined the issuance of the IHA is consistent with categories of activities identified in CE B4 (issuance of incidental harassment authorizations under section 101(a)(5)(A) and (D) of the MMPA for which no serious injury or mortality is anticipated) of the Companion Manual for NAO 216-6A and we have not identified any extraordinary circumstances listed in Chapter 4 of the Companion Manual for NAO 216-6A that would preclude this categorical exclusion. Summary of Request NMFS received a request from WSDOT for an IHA to take marine mammals incidental to Mukilteo Multimodal Project in Mukilteo, Washington. WSDOT's request was for harassment only and NMFS concurs that serious injury or mortality is not expected to result from this activity. Therefore, an IHA is appropriate. On April 7, 2016, WSDOT submitted a request to NMFS requesting an IHA for the possible harassment of small numbers of marine mammal species incidental to construction associated with the Mukilteo Multimodal Project in Mukilteo, Washington, between August 1, 2017, and July 31, 2018. WSDOT subsequently updated its project scope and submitted a revised IHA application on April 10, 2017. NMFS determined the IHA application was complete on April 14, 2017. NMFS is proposing to authorize the take by Level A and Level B harassment of the following marine mammal species: Harbor seal (
                    *Phoca vitulina*), California sea lion (
                    *Zalophus californianus*), Steller sea lion (
                    *Eumetopias jubatus*), northern elephant seal (
                    *Mirounga angustirostris*), killer whale (
                    *Orcinus orca*), gray whale (
                    *Eschrichtius robustus*), humpback whale (
                    *Megaptera novaeangliae*), harbor porpoise (
                    *Phocoena phocoena*), and Dall's porpoise (
                    *P. dalli*). Description of Proposed Activity Overview The purpose of the Mukilteo Multimodal Project is to provide safe, reliable, and effective service and connection for general-purpose transportation, transit, high occupancy vehicles (HOV), pedestrians, and bicyclists traveling between Island County and the Seattle/Everett metropolitan area and beyond by constructing a new ferry terminal. The current Mukilteo Ferry Terminal has not had significant improvements for almost 30 years and needs key repairs. The existing facility is deficient in a number of aspects, such as safety, multimodal connectivity, capacity, and the ability to support the goals of local and regional long-range transportation and comprehensive plans. The project is intended to: Reduce conflicts, congestion, and safety concerns for pedestrians, bicyclists, and motorists by improving local traffic and safety at the terminal and the surrounding area that serves these transportation needs.
                Provide a terminal and supporting facilities with the infrastructure and operating characteristics needed to improve the safety, security, quality, reliability, efficiency, and effectiveness of multimodal transportation.( print page 44165)
                Accommodate future demand projected for transit, HOV, pedestrian, bicycle, and general-purpose traffic. The proposed Mukilteo Multimodal Project would involve in-water impact and vibratory pile driving and vibratory pile removal. Details of the proposed construction project are provided below. Dates and Duration Due to NMFS and the U.S. Fish and Wildlife Service (USFWS) in-water work timing restrictions to protect ESA-listed salmonids, planned WSDOT in-water construction is limited each year to July 16 through February 15. For this project, in-water construction is planned to take place between August 1, 2017 and February 15, 2018. The total worst-case time for pile installation and removal is 175 days (Table 1). Specified Geographic Region The Mukilteo Ferry Terminal is located in the City of Mukilteo, Snohomish County, Washington. The terminal is located in Township 28 North, Range 4 East, Section 3, in Possession Sound. The new terminal will be approximately 1,700 feet (ft) east of the existing terminal in Township 28 North, Range 4 East, Section 33 (Figure 1-2 of the IHA application). Land use in the Mukilteo area is a mix of residential, commercial, industrial, and open space and/or undeveloped lands. Detailed Description of In-Water Pile Driving Associated With Mukilteo Multimodal Project The proposed project has two elements involving noise production that may affect marine mammals: Vibratory hammer driving and removal, and impact hammer driving. Details of the pile driving and pile removal activities are provided in the 
                    **Federal Register**
                     notice (82 FR 21793; May 10, 2017) for the proposed IHA and is summarized in Table 1 below. Table 1—Summary of In-Water Pile Driving Durations
Method
Pile type
Pile size
                             (inch)
Pile number
Duration
                             (min./sec.) 
                             per pile (vib.) or 
                             strikes per pile 
                             (impact)
Duration
                             (days)Vibratory driving
Steel
24
117
60/3,600
39Vibratory removal
Steel
24
69
15/900
23Vibratory driving
Steel
30
40
60/3,600
14Vibratory removal
Steel
30
2
30/1,800
1Vibratory removal
Steel
30
7
15/1,800
1Vibratory driving
Steel
36
6
60/3,600
2Vibratory driving
Steel shaft
78
2
60/3,600
2Vibratory driving
Steel shaft
120
1
60/3,600
1Vibratory driving
Steel H-pile
12
139
30/1,800
14Vibratory driving
Steel sheet

90
30/1,800
30Vibratory removal
Steel sheet

90
15/900
15Impact proofing
Steel
24
68
300
23Impact driving
Steel
30
25
3,000
9Impact proofing
Steel
30
5
300
1Total


661

175
 Comments and Responses A notice of NMFS' proposal to issue an IHA was published in the 
                    **Federal Register**
                     on May 10, 2017 (82 FR 21793). During the 30-day public comment period, NMFS received a comment letter from the Marine Mammal Commission (Commission). No other comments were received. Specific comments and responses are provided below. *Comment 1:*
                     The Commission noted several typographic errors in the 
                    **Federal Register**
                     notice for the proposed IHA. Specifically, Level B harassment for Steller sea lion, gray whales, harbor porpoise, and Dall's porpoise should be 320, 44, 6,650, and 414, instead of 323, 45, 6,698, and 417, respectively. Further, the Commission recommends that NMFS issue the incidental harassment authorization, subject to the inclusion of the proposed mitigation, monitoring, and reporting measures. *Response:*
                     NMFS agrees with the Commission's assessment and made corrections to these errors. Specifically, Level B harassment for Steller sea lion, gray whales, harbor porpoise, and Dall's porpoise are changed to 320, 44, 6,650, and 414, from the previous 323, 45, 6,698, and 417, respectively. All these corrections are included in this document in the Estimated Takes section. The reduced takes do not affect our analysis of negligible impact determination and small number conclusion as discussed later in this document. *Comment 2:*
                     The Commission had questions about the method used to estimate the numbers of takes during the proposed activities, which summed fractions of takes for each species across project days. The Commission had concerns that this method does not account for and negates the intent of NMFS's 24-hour reset policy. *Response:*
                     While for certain projects NMFS has rounded to the whole number for daily takes, for projects like this one, when the objective of take estimation is to provide more accurate assessments of potential impacts to marine mammals for the entire project, rounding in the middle of a calculation would introduce large errors into the process. In addition, while NMFS uses a 24-hour reset for its take calculation to ensure that individual animals are not counted as a take more than once per day, that fact does not make the calculation of take across the entire activity period inherently incorrect. There is no need for daily (24-hour) rounding in this case because there is no daily limit of takes, as long as total authorized takes of marine mammal are not exceeded. Description of Marine Mammals in the Area of Specified Activities The marine mammal species under NMFS jurisdiction that have the potential to occur in the proposed construction area include Pacific harbor seal (
                    *Phoca vitulina*), California sea lion (
                    *Zalophus californianus*), northern elephant seal (
                    *Mirounga angustirostris*), Steller sea lion (
                    *Eumetopias jubatus*), killer whale (
                    *Orcinus orca*), gray whale (
                    *Eschrichtius robustus*), humpback 
                    ( print page 44166)
                    whale (
                    *Megaptera novaeangliae*), harbor porpoise (
                    *Phocoena phocoena*), and Dall's porpoise (
                    *P. dalli*). A list of marine mammals that have the potential to occur in the vicinity of the action and their legal status under the MMPA and ESA are provided in Table 2. Table 2—Marine Mammals With Potential Presence Within the Proposed Project Area
Common name
Scientific name
Stock
ESA/MMPA
                             status; 
                             strategic 
                             
                                (Y/N) 1
Stock
                             abundance 
                             
                                (CV, N
                                min
                                ,
                             
                             most recent 
                             abundance 
                             
                                survey) 2
PBR
Annual
                             
                                M/SI 3**Order Cetartiodactyla—Cetacea—Superfamily Mysticeti (baleen whales)****Family Eschrichtiidae**Gray whale
*Eschrichtius robustus*
Eastern North Pacific
N
20,990
624
132**Family Balaenopteridae (rorquals)**Humpback whale
*Megaptera novaeangliae*
California/Oregon/Washington
Y
1,918
11.0
6.5**Superfamily Odontoceti (toothed whales, dolphins, and porpoises)****Family Delphinidae**Killer whale
*Orcinus orca*
Eastern North Pacific Southern Resident
Y
78
0
0West coast transient
N
243
2.4
0**Family Phocoenidae (porpoises)**Harbor porpoise
*Phocoena phocoena*
Washington inland waters
N
11,233
66
7.2Dall's porpoise
*P. dalli*
California/Oregon/Washington
N
25,750
172
0.3**Order Carnivora—Superfamily Pinnipedia****Family Otariidae (eared seals and sea lions)**California sea lion
*Zalophus californianus*
U.S
N
296,750
9,200
389Steller sea lion
*Eumetopias jubatus*
Eastern U.S
N
71,562
2,498
108**Family Phocidae (earless seals)**Harbor seal
*Phoca vitulina*
Washington northern inland waters
N
4
                             11,036
1,641
43Elephant seal
*Mirounga angustirostris*
California breeding
N
179,000
2,882
8.81
                         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; N
                        min
                         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
                         Harbor seal estimate is based on data that are 8 years old, but this is the best available information for use here.
 General information on the marine mammal species found in Washington coastal waters can be found in Caretta 
                    *et al.*
                     (2016), which is available online at: 
                    *http://www.nmfs.noaa.gov/​pr/​sars/​pdf/​pacific2015_​final.pdf.*
                     Refer to that document for information on these species. Specific information concerning these species in the vicinity of the proposed action area is provided in detail in the WSDOT's IHA application and in the 
                    **Federal Register**
                     notice for the proposed IHA (82 FR 21793; May 10, 2017). Marine Mammal Hearing Hearing is the most important sensory modality for marine mammals underwater, and exposure to anthropogenic sound can have deleterious effects. To appropriately assess the potential effects of exposure to sound, it is necessary to understand the frequency ranges marine mammals are able to hear. Current data indicate that not all marine mammal species have equal hearing capabilities (
                    *e.g.,*
                     Richardson 
                    *et al.,*
                     1995; Wartzok and Ketten 1999; Au and Hastings 2008). To reflect this, Southall 
                    *et al.*
                     (2007) recommended that marine mammals be divided into functional hearing groups based on directly measured or estimated hearing ranges on the basis of available behavioral response data, audiograms derived using auditory evoked potential techniques, anatomical modeling, and other data. Note that no direct measurements of hearing ability have been successfully completed for mysticetes (
                    *i.e.,*
                     low-frequency cetaceans). Subsequently, NMFS (2016) described generalized hearing ranges for these marine mammal hearing groups. Generalized hearing ranges were chosen based on the approximately 65 decibels (dB) threshold from the normalized composite audiograms, with the exception for lower limits for low-frequency cetaceans where the lower bound was deemed to be biologically implausible and the lower bound from Southall 
                    *et al.*
                     (2007) retained. The functional groups and the associated frequencies are indicated below (note that these frequency ranges correspond to the range for the composite group, with the entire range not necessarily reflecting the capabilities of every species within that group): Low-frequency cetaceans (mysticetes): Generalized hearing is estimated to occur between( print page 44167)
                    approximately 7 hertz (Hz) and 35 kilohertz (kHz), with best hearing estimated to be from 100 Hz to 8 kHz;
                Mid-frequency cetaceans (larger toothed whales, beaked whales, and most delphinids): Generalized hearing is estimated to occur between approximately 150 Hz and 160 kHz, with best hearing from 10 to less than 100 kHz;
                High-frequency cetaceans (porpoises, river dolphins, and members of the genera Kogia and Cephalorhynchus; including two members of the genus Lagenorhynchus, on the basis of recent echolocation data and genetic data): Generalized hearing is estimated to occur between approximately 275 Hz and 160 kHz.
                Pinnipeds in water; Phocidae (true seals): Generalized hearing is estimated to occur between approximately 50 Hz to 86 kHz, with best hearing between 1-50 kHz;
                Pinnipeds in water; Otariidae (eared seals): Generalized hearing is estimated to occur between 60 Hz and 39 kHz, with best hearing between 2-48 kHz. The pinniped functional hearing group was modified from Southall 
                    *et al.*
                     (2007) on the basis of data indicating that phocid species have consistently demonstrated an extended frequency range of hearing compared to otariids, especially in the higher frequency range (Hemilä 
                    *et al.,*
                     2006; Kastelein 
                    *et al.,*
                     2009; Reichmuth and Holt, 2013). For more detail concerning these groups and associated frequency ranges, please see NMFS (2016) for a review of available information. Nine marine mammal species (5 cetacean and 4 pinniped (2 otariid and 2 phocid) species) have the reasonable potential to co-occur with the proposed construction activities. Please refer to Table 2. Of the cetacean species that may be present, 2 are classified as low-frequency cetaceans (
                    *i.e.,*
                     all mysticete species), 1 is classified as mid-frequency cetaceans (
                    *i.e.,*
                     killer whale), and 2 are classified as high-frequency cetaceans (
                    *i.e.,*
                     harbor porpoise and Dall's porpoise). Potential Effects of Specified Activities on Marine Mammals and Their Habitat This section includes a summary and discussion of the ways that components of the specified activity may impact marine mammals and their habitat. The “Estimated Take by Incidental Harassment” section later in this document includes a quantitative analysis of the number of individuals that are expected to be taken by this activity. The “Negligible Impact Analysis and Determination” section considers the content of this section, the “Estimated Take by Incidental Harassment” section, and the “Mitigation” section, to draw conclusions regarding the likely impacts of these activities on the reproductive success or survivorship of individuals and how those impacts on individuals are likely to impact marine mammal species or stocks. The WSDOT's Mukilteo Multimodal construction work using in-water pile driving and pile removal could adversely affect marine mammal species and stocks by exposing them to elevated noise levels in the vicinity of the activity area. Exposure to high intensity sound for a sufficient duration may result in auditory effects such as a noise-induced threshold shift—an increase in the auditory threshold after exposure to noise (Finneran 
                    *et al.,*
                     2005). Factors that influence the amount of threshold shift include the amplitude, duration, frequency content, temporal pattern, and energy distribution of noise exposure. The magnitude of hearing threshold shift normally decreases over time following cessation of the noise exposure. The amount of threshold shift just after exposure is the initial threshold shift. If the threshold shift eventually returns to zero (
                    *i.e.,*
                     the threshold returns to the pre-exposure value), it is a temporary threshold shift (Southall 
                    *et al.,*
                     2007). *Threshold Shift (noise-induced loss of hearing)*
                    —When animals exhibit reduced hearing sensitivity (
                    *i.e.,*
                     sounds must be louder for an animal to detect them) following exposure to an intense sound or sound for long duration, it is referred to as a noise-induced threshold shift (TS). An animal can experience temporary threshold shift (TTS) or permanent threshold shift (PTS). TTS can last from minutes or hours to days (
                    *i.e.,*
                     there is complete recovery), can occur in specific frequency ranges (
                    *i.e.,*
                     an animal might only have a temporary loss of hearing sensitivity between the frequencies of 1 and 10 kHz), and can be of varying amounts (for example, an animal's hearing sensitivity might be reduced initially by only 6 dB or reduced by 30 dB). PTS is permanent, but some recovery is possible. PTS can also occur in a specific frequency range and amount as mentioned above for TTS. For marine mammals, published data are limited to the captive bottlenose dolphin, beluga, harbor porpoise, and Yangtze finless porpoise (Finneran 
                    *et al.,*
                     2000, 2002, 2003, 2005, 2007, 2010a, 2010b; Finneran and Schlundt, 2010; Lucke 
                    *et al.,*
                     2009; Mooney 
                    *et al.,*
                     2009a, 2009b; Popov 
                    *et al.,*
                     2011a, 2011b; Kastelein 
                    *et al.,*
                     2012a; Schlundt 
                    *et al.,*
                     2000; Nachtigall 
                    *et al.,*
                     2003, 2004). For pinnipeds in water, data are limited to measurements of TTS in harbor seals, an elephant seal, and California sea lions (Kastak 
                    *et al.,*
                     1999, 2005; Kastelein 
                    *et al.,*
                     2012b). Lucke 
                    *et al.*
                     (2009) found a TS of a harbor porpoise after exposing it to airgun noise with a received sound pressure level (SPL) at 200.2 dB (peak-to-peak) re: 1 micropascal (μPa), which corresponds to a sound exposure level of 164.5 dB re: 1 μPa2
                     s after integrating exposure. Because the airgun noise is a broadband impulse, one cannot directly determine the equivalent of rms SPL from the reported peak-to-peak SPLs. However, applying a conservative conversion factor of 16 dB for broadband signals from seismic surveys (McCauley, 
                    *et al.,*
                     2000) to correct for the difference between peak-to-peak levels reported in Lucke 
                    *et al.*
                     (2009) and rms SPLs, the rms SPL for TTS would be approximately 184 dB re: 1 μPa, and the received levels associated with PTS (Level A harassment) would be higher. Therefore, based on these studies, NMFS recognizes that TTS of harbor porpoises is lower than other cetacean species empirically tested (Finneran & Schlundt, 2010; Finneran 
                    *et al.,*
                     2002; Kastelein and Jennings, 2012). Marine mammal hearing plays a critical role in communication with conspecifics, and interpretation of environmental cues for purposes such as predator avoidance and prey capture. Depending on the degree (elevation of threshold in dB), duration (
                    *i.e.,*
                     recovery time), and frequency range of TTS, and the context in which it is experienced, TTS can have effects on marine mammals ranging from discountable to serious (similar to those discussed in auditory masking, below). For example, a marine mammal may be able to readily compensate for a brief, relatively small amount of TTS in a non-critical frequency range that occurs during a time where ambient noise is lower and there are not as many competing sounds present. Alternatively, a larger amount and longer duration of TTS sustained during time when communication is critical for successful mother/calf interactions could have more serious impacts. Also, depending on the degree and frequency range, the effects of PTS on an animal could range in severity, although it is considered generally more serious because it is a permanent condition. Of note, reduced hearing sensitivity as a simple function of aging has been observed in marine mammals, as well as humans and other taxa (Southall 
                    *et al.,*
                     2007), so one can infer that strategies exist for coping with this condition to some degree, though likely not without cost.
                    ( print page 44168) In addition, chronic exposure to excessive, though not high-intensity, noise could cause masking at particular frequencies for marine mammals, which utilize sound for vital biological functions (Clark 
                    *et al.,*
                     2009). Acoustic masking is when other noises such as from human sources interfere with animal detection of acoustic signals such as communication calls, echolocation sounds, and environmental sounds important to marine mammals. Therefore, under certain circumstances, marine mammals whose acoustical sensors or environment are being severely masked could also be impaired from maximizing their performance fitness in survival and reproduction. Masking occurs at the frequency band that the animals utilize. Therefore, since noise generated from vibratory pile driving is mostly concentrated at low frequency ranges, it may have less effect on high frequency echolocation sounds by odontocetes (toothed whales). However, lower frequency man-made noises are more likely to affect detection of communication calls and other potentially important natural sounds such as surf and prey noise. It may also affect communication signals when they occur near the noise band and thus reduce the communication space of animals (
                    *e.g.,*
                     Clark 
                    *et al.,*
                     2009) and cause increased stress levels (
                    *e.g.,*
                     Foote 
                    *et al.,*
                     2004; Holt 
                    *et al.,*
                     2009). Unlike TS, masking, which can occur over large temporal and spatial scales, can potentially affect the species at population, community, or even ecosystem levels, as well as individual levels. Masking affects both senders and receivers of the signals and could have long-term chronic effects on marine mammal species and populations. Recent science suggests that low frequency ambient sound levels have increased by as much as 20 dB (more than three times in terms of sound pressure level) in the world's ocean from pre-industrial periods, and most of these increases are from distant shipping (Hildebrand 2009). For WSDOT's Mukilteo Multimodal construction activities, noises from vibratory pile driving and pile removal contribute to the elevated ambient noise levels in the project area, thus increasing potential for or severity of masking. Baseline ambient noise levels in the vicinity of project area are high due to ongoing shipping, construction and other activities in the Puget Sound. Finally, marine mammals' exposure to certain sounds could lead to behavioral disturbance (Richardson 
                    *et al.,*
                     1995), such as: Changing durations of surfacing and dives, number of blows per surfacing, or moving direction and/or speed; reduced/increased vocal activities; changing/cessation of certain behavioral activities (such as socializing or feeding); visible startle response or aggressive behavior (such as tail/fluke slapping or jaw clapping); avoidance of areas where noise sources are located; and/or flight responses (
                    *e.g.,*
                     pinnipeds flushing into water from haulouts or rookeries). The onset of behavioral disturbance from anthropogenic noise depends on both external factors (characteristics of noise sources and their paths) and the receiving animals (hearing, motivation, experience, demography) and is also difficult to predict (Southall 
                    *et al.,*
                     2007). Currently NMFS uses a received level of 160 dB re 1 μPa (root mean squared (rms)) to predict the onset of behavioral harassment from impulse noises (such as impact pile driving), and 120 dB re 1 μPa (rms) for continuous noises (such as vibratory pile driving). For the WSDOT's Mukilteo Multimodal construction activities, both of these noise levels are considered for effects analysis because WSDOT plans to use both impact and vibratory pile driving, as well as vibratory pile removal. The biological significance of many of these behavioral disturbances is difficult to predict, especially if the detected disturbances appear minor. However, the consequences of behavioral modification could be biologically significant if the change affects growth, survival, and/or reproduction, which depends on the severity, duration, and context of the effects. Potential Effects on Marine Mammal Habitat The primary potential impacts to marine mammal habitat are associated with elevated sound levels produced by vibratory pile removal and pile driving in the area. However, other potential impacts to the surrounding habitat from physical disturbance are also possible. With regard to fish as a prey source for cetaceans and pinnipeds, fish are known to hear and react to sounds and to use sound to communicate (Tavolga 
                    *et al.,*
                     1981) and possibly avoid predators (Wilson and Dill 2002). Experiments have shown that fish can sense both the strength and direction of sound (Hawkins 1981). Primary factors determining whether a fish can sense a sound signal, and potentially react to it, are the frequency of the signal and the strength of the signal in relation to the natural background noise level. The level of sound at which a fish will react or alter its behavior is usually well above the detection level. Fish have been found to react to sounds when the sound level increased to about 20 dB above the detection level of 120 dB (Ona 1988); however, the response threshold can depend on the time of year and the fish's physiological condition (Engas 
                    *et al.,*
                     1993). In general, fish react more strongly to pulses of sound (such as noise from impact pile driving) rather than continuous signals (such as noise from vibratory pile driving) (Blaxter 
                    *et al.,*
                     1981), and a quicker alarm response is elicited when the sound signal intensity rises rapidly compared to sound rising more slowly to the same level. During the coastal construction only a small fraction of the available habitat would be ensonified at any given time. Disturbance to fish species would be short-term and fish would return to their pre-disturbance behavior once the pile driving activity ceases. Thus, the proposed construction would have little, if any, impact on marine mammals' prey availability in the area where construction work is planned. Finally, the time of the proposed construction activity would avoid the spawning season of the ESA-listed salmonid species. Estimated Take This section provides an estimate of the number of incidental takes authorized through this IHA, which will inform both NMFS' consideration of whether the number of takes is “small” and the negligible impact determination. Harassment is the only type of take expected to result from these activities. Except with respect to certain activities not pertinent here, section 3(18) of 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). Authorized takes would primarily be by Level B harassment, as noise from pile driving and removal has the potential to result in disruption of behavioral patterns for individual marine mammals. There is also some potential for auditory injury (Level A harassment) to result, primarily for high frequency cetaceans and phocids due to larger predicted auditory injury zones. Auditory injury is unlikely to occur for low- and mid-frequency cetaceans and otariids. The prescribed mitigation and monitoring measures are expected to 
                    ( print page 44169)
                    minimize the severity of such taking to the extent practicable. As described previously, no mortality is anticipated or authorized for this activity. Below we describe how the take is estimated. Described in the most basic way, we estimate take by considering: (1) Acoustic thresholds above which NMFS believes the best available science indicates marine mammals will be behaviorally harassed or incur some degree of permanent hearing impairment; (2) the area or volume of water that will be ensonified above these levels in a day; (3) the density or occurrence of marine mammals within these ensonified areas; and, (4) and the number of days of activities. Below, we describe these components in more detail and present the take estimate. Acoustic Thresholds Using the best available science, NMFS has developed acoustic thresholds that identify the received level of underwater sound above which exposed marine mammals would be reasonably expected to be behaviorally harassed (equated to Level B harassment) or to incur PTS of some degree (equated to Level A harassment). Level B Harassment for non-explosive sources—Though significantly driven by received level, the onset of behavioral disturbance from anthropogenic noise exposure is also informed to varying degrees by other factors related to the source (
                    *e.g.,*
                     frequency, predictability, duty cycle), the environment (
                    *e.g.,*
                     bathymetry), and the receiving animals (hearing, motivation, experience, demography, behavioral context) and can be difficult to predict (Southall 
                    *et al.,*
                     2007, Ellison 
                    *et al.,*
                     2011). Based on what the available science indicates and the practical need to use a threshold based on a factor that is both predictable and measurable for most activities, NMFS uses a generalized acoustic threshold based on received level to estimate the onset of behavioral harassment. NMFS predicts that marine mammals are likely to be behaviorally harassed in a manner we consider Level B harassment when exposed to underwater anthropogenic noise above received levels of 120 dB re 1 μPa (rms) for continuous (
                    *e.g.*
                     vibratory pile-driving, drilling) and above 160 dB re 1 μPa (rms) for non-explosive impulsive (
                    *e.g.,*
                     seismic airguns) or intermittent (
                    *e.g.,*
                     scientific sonar) sources. Applicant's proposed activity includes the use of continuous (vibratory pile driving and removal) and impulsive (impact pile driving) sources, and therefore the 120 and 160 
                    *160*
                     dB re 1 μPa (rms) are applicable. Level A harassment for non-explosive sources—NMFS' Technical Guidance for Assessing the Effects of Anthropogenic Sound on Marine Mammal Hearing (Technical Guidance, 2016) identifies dual criteria to assess auditory injury (Level A harassment) to five different marine mammal groups (based on hearing sensitivity) as a result of exposure to noise from two different types of sources (impulsive or non-impulsive). Applicant's proposed activity includes the use of impulsive (impact pile driving) and non-impulsive (vibratory pile driving and pile removal) sources. These thresholds were developed by compiling and synthesizing the best available science and soliciting input multiple times from both the public and peer reviewers to inform the final product, and are provided in the table below. The references, analysis, and methodology used in the development of the thresholds are described in NMFS 2016 Technical Guidance, which may be accessed at: 
                    *http://www.nmfs.noaa.gov/​pr/​acoustics/​guidelines.htm.* Table 3—Current Acoustic Exposure Criteria for Non-Explosive Sound Underwater
Hearing group
PTS onset thresholds
Behavioral thresholdsImpulsive
Non-impulsive
Impulsive
Non-impulsiveLow-Frequency (LF) Cetaceans
*L*pk,flat
                            : 219 dB; 
                            *L*E,LF,24h
                            : 183 dB
*L*E,LF,24h
                            : 199 dB
*L*rms,flat
                            : 160 dB
*L*rms,flat
                            : 120 dB.Mid-Frequency (MF) Cetaceans
*L*pk,flat
                            : 230 dB; 
                            *L*E,MF,24h
                            : 185 dB
*L*E,MF,24h
                            : 198 dBHigh-Frequency (HF) Cetaceans
*L*pk,flat
                            : 202 dB; 
                            *L*E,HF,24h
                            : 155 dB
*L*E,HF,24h
                            : 173 dBPhocid Pinnipeds (PW) (Underwater)
*L*pk,flat
                            : 218 dB; 
                            *L*E,PW,24h
                            : 185 dB
*L*E,PW,24h
                            : 201 dBOtariid Pinnipeds (OW) (Underwater)
*L*pk,flat
                            : 232 dB; 
                            *L*E,OW,24h
                            : 203 dB
*L*E,OW,24h
                            : 219 dB* Dual metric acoustic thresholds for impulsive sounds: Use whichever results in the largest isopleth for calculating PTS onset. If a non-impulsive sound has the potential of exceeding the peak sound pressure level thresholds associated with impulsive sounds, these thresholds should also be considered.**Note:**
                         Peak sound pressure (L
                        pk
                        ) has a reference value of 1 μPa, and cumulative sound exposure level (L
                        E
                        ) has a reference value of 1μPa
                        2
                        s. In this Table, thresholds are abbreviated to reflect American National Standards Institute standards (ANSI 2013). However, peak sound pressure is defined by ANSI as incorporating frequency weighting, which is not the intent for this Technical Guidance. Hence, the subscript “flat” is being included to indicate peak sound pressure should be flat weighted or unweighted within the generalized hearing range. The subscript associated with cumulative sound exposure level thresholds indicates the designated marine mammal auditory weighting function (LF, MF, and HF cetaceans, and PW and OW pinnipeds) and that the recommended accumulation period is 24 hours. The cumulative sound exposure level thresholds could be exceeded in a multitude of ways (
                        *i.e.,*
                         varying exposure levels and durations, duty cycle). When possible, it is valuable for action proponents to indicate the conditions under which these acoustic thresholds will be exceeded.
 Ensonified Area Here, we describe operational and environmental parameters of the activity that will feed into identifying the area ensonified above the acoustic thresholds. Source Levels The project includes vibratory pile driving and removal of 24-, 30-, and 36-inch (in) steel piles, vibratory driving of 78- and 120-in steel shaft, vibratory driving of steel H-piles, vibratory driving and removal of steel sheet piles, and impact pile driving and proofing of 24- and 30-in steel piles. Source levels of the above pile driving activities are based on measurements of the same material types and same or similar dimensions of piles measured at Mukilteo or elsewhere. Specifically, the source level for vibratory pile driving and removal of the 24-in steel pile is based on vibratory test pile driving of the same pile at the Friday Harbor (WSDOT 2010a). The unweighted SPLrms
                     source level at 10 meters (m) from the pile is 162 dB re 1 re 1 μPa. We consider that using vibratory pile installation source level as a proxy for vibratory pile removal is conservative. The source level for vibratory pile driving and removal of the 30-in steel pile is based on vibratory pile driving of the same pile at Port Townsend (WSDOT, 2010b). The unweighted SPLrms
                     source level at 10 m from the pile is 174 dB re 1 re 1 μPa.
                    ( print page 44170) The source level for vibratory pile driving the 36-in steel piles is based on vibratory test pile driving of 36-in steel piles at Port Townsend in 2010 (Laughlin 2011). Recordings of vibratory pile driving were made at a distance of 10 m from the pile. The results show that the unweighted SPLrms
                     for vibratory pile driving of 36-in steel pile was 177 dB re 1 μPa. Source level for vibratory pile driving of the 78- and 120-in steel shaft is based on measurements of 72-in steel piles vibratory driving conducted by CALTRANS. The unweighted SPLrms
                     source level ranged between 170 and 180 dB re 1 μPa at 10 m from the pile (CALTRANS 2012). The value of 180 dB is chosen to be more conservative. The source level for vibratory pile driving of steel H-piles is based on measurements conducted by the California Department of Transportation (CALTRANS). The unweighted SPLrms
                     source level is 150 dB re 1 re 1 μPa at 10 m from the pile (CALTRANS, 2012). The source level for vibratory sheet pile driving and removal is based on measurements at the Elliott Bay Seawall Project. The unweighted SPLrms
                     source level is 164 dB re 1 re 1 μPa at 10 m from the pile (Greenbusch 2015). Source levels for impact pile driving of the 24-in steel piles are based on impact test pile driving of the same steel pile during the Vashon Acoustic Monitoring by WSDOT (Laughlin, 2015). The unweighted back-calculated source levels at 10 m are 174 dB re 1 μPa2
                    -s for single strike SEL (SELss) and 189 dB re 1 μPa for SPLrms. Source levels for impact pile driving of the 30-in steel pile are based on impact test pile driving for the 36-in steel pile at Mukilteo in November 2006. Recordings of the impact pile driving that were made at a distance of 10 m from the pile were analyzed using Matlab. The results show that the unweighted source levels are 178 dB re 1 μPa2
                    -s for SELss
                     and 193 dB re 1 μPa for SPLrms. A summary of source levels from different pile driving and pile removal activities is provided in Table 4. Table 4—Summary of In-Water Pile Driving Source Levels
[At 10 m from source]
Method
Pile type/size 
                             (inch)
SEL (SEL
                            ss
                             for impact pile 
                             
                                driving), dB re 1 μPa2
                                −s
SPL
                            rms
                            , dB re 1 μPa2Vibratory driving/removal
Steel, 24
162
162Vibratory driving/removal
Steel, 30
174
174Vibratory driving
Steel, 36
177
177Vibratory driving
Steel shaft, 78
180
180Vibratory driving
Steel shaft, 120
180
180Vibratory driving
Steel H-pile, 12
150
150Vibratory driving/removal
Steel sheet
164
164Impact driving
Steel, 24
174
189Impact driving
Steel, 30
178
193
 These source levels are used to compute the Level A ensonified zones and to estimate the Level B harassment zones. For Level A harassment zones, zones calculated using cumulative SEL are all larger than those calculated using SPLpeak, therefore, only zones based on cumulative SEL for Level A harassment are used. Source spectrum of the 36-in steel pile recording is used for spectral modeling for the 24-, 30-, and 36-in steel pile vibratory pile driving and removal to calculate Level A exposure distances based on cumulative SEL metric (see below). For other piles where no recording is available, source modeling cannot be performed. In such cases, the weighting factor adjustment (WFA) recommended by NMFS acoustic guidance (NMFS 2016) was used to determine Level A exposure distances. Estimating Injury Zones Calculation and modeling of applicable ensonified zones are based on source measurements of comparable types and sizes of piles driven by different methods (impact vs. vibratory hammers) as described above. When NMFS Technical Guidance (2016) was published, in recognition of the fact that ensonified area/volume could be more technically challenging to predict because of the duration component in the new thresholds, we developed a User Spreadsheet that includes tools to help predict a simple isopleth that can be used in conjunction with marine mammal density or occurrence to help predict takes. We note that because of some of the assumptions included in the methods used for these tools, we anticipate that isopleths produced are typically going to be overestimates of some degree, which will result in some degree of overestimate of Level A take. However, these tools offer the best way to predict appropriate isopleths when more sophisticated 3D modeling methods are not available, and NMFS continues to develop ways to quantitatively refine these tools, and will qualitatively address the output where appropriate. For peak SPL (Lpk), distances to marine mammal injury thresholds were calculated using a simple geometric spreading model using a transmission loss coefficient of 15. For cumulative SEL (
                    *L**E*), distances to marine mammal injury thresholds were computed using spectral modeling that incorporates frequency specific absorption. Isopleths to Level B behavioral zones are based on root-mean-square SPL (SPLrms) that are specific for impulse (impact pile driving) and non-impulse (vibratory pile driving) sources. Distances to marine mammal behavior thresholds were calculated using practical spreading. A summary of the measured and modeled harassment zones is provided in Table 5. The maximum distance is 20,500 m from the source, since this is where landmass intercepts underwater sound propagation.
                    ( print page 44171) Table 5—Distances to Harassment Zones
Pile type, size and pile driving method
Injury zone
                             (m)
Behavior
                             zone 
                             (m)LF cetacean
MF cetacean
HF cetacean
Phocid
OtariidVibratory removal, 24-in steel pile, 3 piles/day
10
10
55
10
10
6,040Vibratory driving, 24-in steel pile, 3 piles/day
175
45
995
85
10
6,040Vibratory removal, 30-in steel pile, 2 piles/day
55
10
345
25
10
* 20,500Vibratory removal, 30-in steel pile, 7 piles/day
125
35
725
55
10
* 20,500Vibratory driving, 30-in steel pile, 3 piles/day
175
45
995
85
10
* 20,500Vibratory driving, 36-in steel pile, 3 piles/day
175
45
995
85
10
* 20,500Vibratory driving, 78-in steel shaft, 1 pile/day
126
11
186
77
5
* 20,500Vibratory driving, 120-in steel shaft, 1 pile/day
126
11
186
77
5
* 20,500Vibratory driving, steel 12-in H-pile, 10 piles/day
4
1
6
2
0
1,000Vibratory driving, steel sheet, 3 piles/day
14
1
21
9
1
8,577Vibratory removal, steel sheet, 6 piles/day
23
2
33
14
1
8,577Impact proofing, 24-in steel pile, 3 piles/day
135
10
75
35
10
875Impact driving, 30-in steel pile, 3 piles/day
1,065
10
505
225
10
1,585Impact proofing, 30-in steel pile, 5 piles/day
355
10
175
75
10
1,585* Landmass intercepts at a distance of 20,500 m from project area.
 Marine Mammal Occurrence In this section we provide the information about the presence, density, or group dynamics of marine mammals that will inform the take calculations. Incidental take is estimated for each species by estimating the likelihood of a marine mammal being present within a Level A or Level B harassment zone during active pile driving or removal. The Level A calculation includes a duration component, along with an assumption (which can lead to overestimates in some cases) that animals within the zone stay in that area for the whole duration of the pile driving activity within a day. For all marine mammal species except harbor seals, California sea lions, and northern elephant seals, estimated takes are calculated based on ensonified area for a specific pile driving activity multiplied by the marine mammal density in the action area, multiplied by the number of pile driving (or removal) days. In most cases, marine mammal density data are from the U.S. Navy Marine Species Density Database (Navy 2015). Harbor porpoise density is based on a recent study by Jefferson 
                    *et al.*
                     (2016) for the Eastern Whidbey area near the Mukilteo Ferry Terminal. Harbor seal, northern elephant seal, and California sea lion takes are based on observations in the Mukilteo area, since these data provide the best information on distribution and presence of these species that are often associated with nearby haulouts (see below). The Level A take total was further adjusted by subtracting animals expected to occur within the exclusion zone, where pile driving activities are suspended when an animal is observed in or approaching the zone (see Mitigation section). Further, the number of Level B takes was adjusted to exclude those already counted for Level A takes. Take Calculation and Estimation Here we describe how the information provided above is brought together to produce a quantitative take estimate. The harbor seal take estimate is based on local seal abundance information from monitoring during the Mukilteo pier removal project. Marine mammal visual monitoring during Mukilteo Ferry Terminal pier removal project showed an average daily observation of 7 harbor seals (WSDOT 2015). Based on a total of 175 pile driving days for the WSDOT Mukilteo Multimodal Phase 2 project, it is estimated that up to 1,225 harbor seals could be exposed to noise levels associated with “take.” Since 9 days would involve impact pile driving of 30-in piles with Level A harassment zones beyond the required shutdown zones (225 m vs 160 m shutdown zone), we consider that 63 harbor seals exposed during these 9 days would experience Level A harassment. The California sea lion take estimate is based on local sea lion abundance information during the Mukilteo Ferry Terminal pier removal project (WSDOT 2015). Marine mammal visual monitoring during the Mukilteo pier removal project indicates on average 7 sea lions were observed in the general area of the Mukilteo Ferry Terminal per day (WSDOT 2015). Based on a total of 175 pile driving days for the WSDOT Mukilteo Multimodal project, it is estimated that up to 1,225 California sea lions could be exposed to noise levels associated with “take”. Since the Level A harassment zones of otarids are all very small (max. 10 m, Table 5), we do not consider it likely that any sea lions would be taken by Level A harassment. Therefore, all California sea lion takes estimated here are expected to be by Level B harassment. Northern elephant seal is not common in the Mukilteo Multimodal Project area, however, their presence has been observed in Edmonds area just south of Mukilteo (Huey, Pers. Comm. April 2017). Therefore, a potential take of 20 animals by Level B harassment during the project period is assessed. Since 
                    ( print page 44172)
                    northern elephant seal is very uncommon in the project area, we do not consider it likely that any elephant seal would be taken by Level A harassment. However, the method used in take estimates does not account for single individuals being taken multiple times during the entire project period of 175 days. Therefore, the percent of marine mammals that are likely to be taken for a given population would be far less than the ratio of numbers of animals taken divided by the population size. For harbor porpoise, the estimated incidences of takes at 6,759 animals would be 60.2 percent of the population, if each single take were a unique individual. However, this is highly unlikely because the results of telemetry and photo-identification studies in Washington waters have demonstrated that harbor porpoise shows site fidelity to small areas for periods of time that can extend between seasons (Hanson 
                    *et al.*
                     1999; Hanson 2007a, 2007b). Based on studies by Jefferson 
                    *et al.*
                     (2016), harbor porpoise abundance in the East Whidbey region, which is adjunct to the Mukilteo Ferry Terminal construction, is 497, and harbor porpoise abundance in the entire surrounding area of North Puget Sound is 1,798. For Southern Resident killer whales, potential takes based on density calculation showed that 4 animals could be exposed to noise levels for Level B harassment. However, mitigation measures prescribed below are expected to prevent such takes. A summary of estimated marine mammal takes is listed in Table 6. Table 6—Estimated Numbers of Marine Mammals That May Be Exposed to Received Noise Levels That Cause Level A or Level B Harassment
Species
Estimated
                             Level A take
Estimated
                             Level B take
Estimated
                             total take
Abundance
PercentagePacific harbor seal
63
1,162
1,225
11,036
11.1California sea lion
0
1,225
1,225
296,750
0.41Northern elephant seal
0
20
20
179,000
0.01Steller sea lion
0
320
320
71,562
0.32Killer whale, transient
0
21
21
243
8.64Killer whale, Southern Resident
0
0
0
78
0Gray whale
0
44
44
20,990
0.21Humpback whale
0
6
6
1,918
0.31Harbor porpoise
61
6,650
6,711
11,233
60.2Dall's porpoise
4
414
418
25,750
1.63
 Mitigation In order to issue an IHA under Section 101(a)(5)(D) of the MMPA, NMFS must set forth the permissible methods of taking pursuant to such activity, “and other means of effecting the least practicable impact on such species or stock and its habitat, paying particular attention to rookeries, mating grounds, and areas of similar significance, and on the availability of such species or stock for taking” for certain subsistence uses (latter not applicable for this action). NMFS regulations require applicants for incidental take authorizations to include information about the availability and feasibility (economic and technological) of equipment, methods, and manner of conducting such activity or other means of effecting the least practicable adverse impact upon the affected species or stocks and their habitat (50 CFR 216.104(a)(11)). In evaluating how mitigation may or may not be appropriate to ensure the least practicable adverse impact on species or stocks and their habitat, as well as subsistence uses where applicable, we carefully consider two primary factors: (1) The manner in which, and the degree to which, the successful implementation of the measure(s) is expected to reduce impacts to marine mammals, marine mammal species or stocks, and their habitat. This considers the nature of the potential adverse impact being mitigated (likelihood, scope, range). It further considers the likelihood that the measure will be effective if implemented (probability of accomplishing the mitigating result if implemented as planned) the likelihood of effective implementation. and; (2) The practicability of the measures for applicant implementation, which may consider such things as cost, impact on operations, and, in the case of a military readiness activity, personnel safety, practicality of implementation, and impact on the effectiveness of the military readiness activity. Mitigation for Marine Mammals and Their Habitat 1. Time Restriction Work would occur only during daylight hours, when visual monitoring of marine mammals can be conducted. In addition, all in-water construction will be limited to the period between August 1, 2017, and February 15, 2018. 2. Use of Noise Attenuation Devices To reduce impact on marine mammals, WSDOT shall use a marine pile driving energy attenuator (
                    *i.e.,*
                     air bubble curtain system), or other equally effective sound attenuation method (
                    *e.g.,*
                     dewatered cofferdam) for all impact pile driving. 3. Establishing and Monitoring Level A, Level B Harassment Zones, and Exclusion Zones Before the commencement of in-water construction activities, which include impact pile driving and vibratory pile driving and pile removal, WSDOT shall establish Level A harassment zones where received underwater SPLs or SELcum
                     could cause PTS (see above). WSDOT shall also establish Level B harassment zones where received underwater SPLs are higher than 160 dBrms
                     and 120 dBrms
                     re 1 μPa for impulse noise sources (impact pile driving) and non-impulses noise sources (vibratory pile driving and pile removal), respectively. WSDOT shall establish a maximum 160-m Level A exclusion zone for all marine mammals except low-frequency baleen whales. For Level A harassment zones that are smaller than 160 m from the source, WSDOT shall establish exclusion zones that correspond to the estimated Level A harassment distances, but shall not be less than 10 m. For low-frequency baleen whales, WSDOT shall establish exclusion zones that correspond to the actual Level A harassment distances, but shall not be less than 10 m.
                    ( print page 44173) A summary of exclusion zones is provided in Table 7. Table 7—Exclusion Zones for Various Pile Driving Activities and Marine Mammal Hearing Groups
Pile type, size and pile driving method
Exclusion zone
                             (m)LF cetacean
MF cetacean
HF cetacean
Phocid
OtariidVibratory removal, 24-in steel pile, 3 piles/day
10
10
55
10
10Vibratory removal, 30-in steel pile, 2 piles/day
55
10
160
25
10Vibratory removal, 30-in steel pile, 7 piles/day
125
35
160
55
10Vibratory driving, 24-, 30- & 36-in steel pile, 3 piles/day
175
45
160
85
10Vibratory driving, 78-, 120-in steel shaft, 1 pile/day
126
11
160
77
10Vibratory driving, steel 12-in H-pile, 10 piles/day
4
1
6
2
1Vibratory driving, steel sheet, 3 piles/day
14
1
21
9
1Vibratory removal, steel sheet, 6 piles/day
23
2
33
14
1Impact proofing, 24-in steel pile, 3 piles/day
135
10
75
35
10Impact driving, 30-in steel pile, 3 piles/day
1,065
10
160
160
10Impact proofing, 30-in steel pile, 5 piles/day
355
10
160
75
10
 NMFS-approved protected species observers (PSO) shall conduct an initial survey of the exclusion zones to ensure that no marine mammals are seen within the zones before pile driving and pile removal of a pile segment begins. If marine mammals are found within the exclusion zone, pile driving of the segment would be delayed until they move out of the area. If a marine mammal is seen above water and then dives below, the contractor would wait 30 minutes. If no marine mammals are seen by the observer in that time it can be assumed that the animal has moved beyond the exclusion zone. If pile driving of a segment ceases for 30 minutes or more and a marine mammal is sighted within the designated exclusion zone prior to commencement of pile driving, the observer(s) must notify the pile driving operator (or other authorized individual) immediately and continue to monitor the exclusion zone. Operations may not resume until the marine mammal has exited the exclusion zone or 30 minutes have elapsed since the last sighting. 4. Soft Start A “soft-start” technique is intended to allow marine mammals to vacate the area before the impact pile driver reaches full power. Whenever there has been downtime of 30 minutes or more without impact pile driving, the contractor will initiate the driving with ramp-up procedures described below. Soft start for impact hammers requires contractors to provide an initial set of three strikes from the impact hammer at 40 percent energy, followed by a 1-minute waiting period, then two subsequent three-strike sets. Each day, WSDOT will use the soft-start technique at the beginning of impact pile driving, or if pile driving has ceased for more than 30 minutes. 5. Shutdown Measures WSDOT shall implement shutdown measures if a marine mammal is detected within an exclusion zone or is about to enter an exclusion zone listed in Table 6. WSDOT shall also implement shutdown measures if southern resident killer whales are sighted within the vicinity of the project area and are approaching the Level B harassment zone (or Zone of Influence, ZOI) during in-water construction activities. If a killer whale approaches the ZOI during pile driving or removal, and it is unknown whether it is a Southern Resident killer whale or a transient killer whale, it shall be assumed to be a Southern Resident killer whale and WSDOT shall implement the shutdown measure. If a Southern Resident killer whale or an unidentified killer whale enters the ZOI undetected, in-water pile driving or pile removal shall be suspended until the whale exits the ZOI to avoid further level B harassment. Further, WSDOT shall implement shutdown measures if the number of authorized takes for any particular species reaches the limit under the IHA (if issued) and if such marine mammals are sighted within the vicinity of the project area and are approaching the Level B harassment zone during in-water construction activities. 6. Coordination With Local Marine Mammal Research Network Prior to the start of pile driving for the day, the Orca Network and/or Center for Whale Research will be contacted by WSDOT to find out the location of the nearest marine mammal sightings. The Orca Sightings Network consists of a list of over 600 (and growing) residents, scientists, and government agency personnel in the U.S. and Canada. Sightings are called or emailed into the Orca Network and immediately distributed to other sighting networks including: The NMFS Northwest Fisheries Science Center, the Center for Whale Research, Cascadia Research, the Whale Museum Hotline and the British Columbia Sightings Network. Sightings information collected by the Orca Network includes detection by hydrophone. The SeaSound Remote Sensing Network is a system of interconnected hydrophones installed in the marine environment of Haro Strait (west side of San Juan Island) to study orca communication, in-water noise, bottom fish ecology and local climatic conditions. A hydrophone at the Port Townsend Marine Science Center measures average in-water sound levels and automatically detects unusual sounds. These passive acoustic devices allow researchers to hear when different marine mammals come into the region. This acoustic network, combined with the volunteer (incidental) visual sighting network allows researchers to document presence and location of various marine mammal species. Based on our evaluation of the required measures, NMFS has determined that the prescribed mitigation measures provide the means effecting the least practicable impact on the affected species or stocks and their habitat, paying particular attention to rookeries, mating grounds, and areas of similar significance. Monitoring and Reporting In order to issue an IHA for an activity, Section 101(a)(5)(D) of the MMPA states that NMFS must set forth, 
                    ( print page 44174)
                    requirements pertaining to the monitoring and reporting of such taking. The MMPA implementing regulations at 50 CFR 216.104(a)(13) indicate that requests for authorizations must include the suggested means of accomplishing the necessary monitoring and reporting that will result in increased knowledge of the species and of the level of taking or impacts on populations of marine mammals that are expected to be present in the proposed action area. Effective reporting is critical both to compliance as well as ensuring that the most value is obtained from the required monitoring. Monitoring and reporting requirements prescribed by NMFS should contribute to improved understanding of one or more of the following: Occurrence of marine mammal species or stocks in the area in which take is anticipated (*e.g.,*
                     presence, abundance, distribution, density).
                Nature, scope, or context of likely marine mammal exposure to potential stressors/impacts (individual or cumulative, acute or chronic), through better understanding of: (1) Action or environment (*e.g.,*
                     source characterization, propagation, ambient noise); (2) affected species (
                    *e.g.,*
                     life history, dive patterns); (3) co-occurrence of marine mammal species with the action; or (4) biological or behavioral context of exposure (
                    *e.g.,*
                     age, calving or feeding areas).
                Individual marine mammal responses (behavioral or physiological) to acoustic stressors (acute, chronic, or cumulative), other stressors, or cumulative impacts from multiple stressors.
                How anticipated responses to stressors impact either: (1) Long-term fitness and survival of individual marine mammals; or (2) populations, species, or stocks.
                Effects on marine mammal habitat (*e.g.,*
                     marine mammal prey species, acoustic habitat, or other important physical components of marine mammal habitat).
                Mitigation and monitoring effectiveness. Monitoring Measures WSDOT shall employ NMFS-approved PSOs to conduct marine mammal monitoring for its Mukilteo Multimodal Project. The PSOs will observe and collect data on marine mammals in and around the project area for 30 minutes before, during, and for 30 minutes after all pile removal and pile installation work. NMFS-approved PSOs shall meet the following requirements: 1. Independent observers (
                    *i.e.,*
                     not construction personnel) are required; 2. At least one observer must have prior experience working as an observer; 3. Other observers may substitute education (undergraduate degree in biological science or related field) or training for experience; 4. Where a team of three or more observers are required, one observer should be designated as lead observer or monitoring coordinator. The lead observer must have prior experience working as an observer; and 5. NMFS will require submission and approval of observer CVs; Monitoring of marine mammals around the construction site shall be conducted using high-quality binoculars (
                    *e.g.,*
                     Zeiss, 10 × 42 power). Due to the different sizes of ZOIs from different pile sizes, several different ZOIs and different monitoring protocols corresponding to a specific pile size will be established. For Level A zones less than 160 m and Level B zones less than 1,000 m (*i.e.,*
                     vibratory 12-in H pile driving, 10 piles/day; impact proofing of 24-in steel piles, 3 piles/day), two land-based PSOs will monitor the exclusion zones and Level B harassment zone.
                For Level A zones between 160 and 500 m, and Level B zones between 1,000 and 10,000 m (*i.e,*
                     vibratory pile driving and removal of 24-in steel piles, 3 piles/day; vibratory driving and removal of steel sheet; and impact proofing of 30-in steel piles, 5 piles/day), 5 land-based PSOs and 1 vessel-based PSO on a ferry will monitor the Level A and Level B harassment zones.
                For the rest of the pile driving and pile removal scenario, 5 land-based PSOs and 2 vessel-based PSOs on ferries will monitor the Level A and Level B harassment zones. Locations of the land-based PSOs and routes of monitoring vessels are shown in WSDOT's Marine Mammal Monitoring Plan, which is available online at 
                    *www.nmfs.noaa.gov/​pr/​permits/​incidental/​construction.htm.* To verify the required monitoring distance, the exclusion zones and ZOIs will be determined by using a range finder or hand-held global positioning system device. Reporting Measures WSDOT is required to submit a draft monitoring report within 90 days after completion of the construction work or the expiration of the IHA, whichever comes earlier. This report would detail the monitoring protocol, summarize the data recorded during monitoring, and estimate the number of marine mammals that may have been harassed. NMFS would have an opportunity to provide comments on the report, and if NMFS has comments, WSDOT would address the comments and submit a final report to NMFS within 30 days. In addition, NMFS would require WSDOT to notify NMFS' Office of Protected Resources and NMFS' West Coast Stranding Coordinator within 48 hours of sighting an injured or dead marine mammal in the construction site. WSDOT shall provide NMFS and the Stranding Network with the species or description of the animal(s), the condition of the animal(s) (including carcass condition, if the animal is dead), location, time of first discovery, observed behaviors (if alive), and photo or video (if available). In the event that WSDOT finds an injured or dead marine mammal that is not in the construction area, WSDOT would report the same information as listed above to NMFS as soon as operationally feasible. Negligible Impact Analysis and Determination NMFS has defined negligible impact 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 (50 CFR 216.103). A negligible impact finding is based on the lack of likely adverse effects on annual rates of recruitment or survival (
                    *i.e.,*
                     population-level effects). An estimate of the number of takes alone is not enough information on which to base an impact determination. In addition to considering estimates of the number of marine mammals that might be “taken” through harassment, NMFS considers other factors, such as the likely nature of any responses (
                    *e.g.,*
                     intensity, duration), the context of any responses (
                    *e.g.,*
                     critical reproductive time or location, migration), as well as effects on habitat, and the likely effectiveness of the mitigation. We also assess the number, intensity, and context of estimated takes by evaluating this information relative to population status. Consistent with the 1989 preamble for NMFS's implementing regulations (54 FR 40338; September 29, 1989), the impacts from other past and ongoing anthropogenic activities are incorporated into this analysis via their impacts on the environmental baseline (
                    *e.g.,*
                     as reflected in the regulatory status of the species, population size and growth rate where known, ongoing sources of human-caused mortality, or ambient noise levels).
                    ( print page 44175) To avoid repetition, this introductory discussion of our analyses applies to all the species listed in Table 6, given that the anticipated effects of WSDOT's Mukilteo Multimodal Project activities involving pile driving and pile removal on marine mammals are expected to be relatively similar in nature. There is no information about the nature or severity of the impacts, or the size, status, or structure of any species or stock that would lead to a different analysis by species for this activity, or else species-specific factors would be identified and analyzed. Although a few marine mammal species (63 harbor seals, 61 harbor porpoises, and 4 Dall's porpoise) are estimated to experience Level A harassment in the form of PTS if they stay within the Level A harassment zone during the entire pile driving for the day, the degree of injury is expected to be mild and is not likely to affect the reproduction or survival of the individual animals because most animals will avoid the area, and thus avoid injury. It is expected that, if hearing impairments occurs, most likely the affected animal would lose a few dB in its hearing sensitivity, which in most cases is not likely to affect its survival and recruitment. Hearing impairment that occur for these individual animals would be limited to the dominant frequency of the noise sources, 
                    *i.e.,*
                     in the low-frequency region below 2 kHz. Therefore, the degree of PTS is not likely to affect the echolocation performance of the two porpoise species, which use frequencies mostly above 100 kHz. Nevertheless, for all marine mammal species, it is known that in general animals avoid areas where sound levels could cause hearing impairment. Therefore, it is not likely that an animal would stay in an area with intense noise that could cause severe levels of hearing damage. For the rest of the three marine mammal species, takes that are anticipated and authorized are expected to be limited to short-term Level B harassment. Marine mammals present in the vicinity of the action area and taken by Level B harassment would most likely show overt brief disturbance (startle reaction) and avoidance of the area from elevated noise levels during pile driving and pile removal and the implosion noise. These behavioral distances are not expected to affect marine mammals' growth, survival, and reproduction due to the limited geographic area that would be affected in comparison to the much larger habitat for marine mammals in the Puget Sound. The project also is not expected to have significant adverse effects on affected marine mammals' habitat, as analyzed in detail in the “Anticipated Effects on Marine Mammal Habitat” section. The project activities would not permanently modify existing marine mammal habitat. The activities may kill some fish and cause other fish to leave the area temporarily, thus impacting marine mammals' foraging opportunities in a limited portion of the foraging range; but, because of the short duration of the activities and the relatively small area of the habitat that may be affected, the impacts to marine mammal habitat are not expected to cause significant or long-term negative consequences. Therefore, given the consideration of potential impacts to marine mammal prey species and their physical environment, WSDOT's proposed construction activity at Mukilteo Ferry Terminal would not adversely affect marine mammal habitat. In summary and as described above, the following factors primarily support our determination that the impacts resulting from this activity are not expected to adversely affect the species or stock through effects on annual rates of recruitment or survival: No mortality is anticipated or authorized;
                Level A harassment is expected in the form of elevated hearing threshold of a few dBs within limited frequency range, and is limited to a few individual animals of three species; and
                The majority of harassment is Level B harassment in the form of short-term behavioral modification. Based on the analysis contained herein of the likely effects of the specified activity on marine mammals and their habitat, and taking into consideration the implementation of the prescribed monitoring and mitigation measures, NMFS finds that the total take from the proposed activity will have a negligible impact on all affected marine mammal species or stocks. Small Numbers As noted above, only small numbers of incidental take may be authorized under Section 101(a)(5)(D) of the MMPA for specified activities other than military readiness activities. The MMPA does not define small numbers and so, in practice, NMFS compares the number of individuals taken to the most appropriate estimation of abundance of the relevant species or stock in our determination of whether an authorization is limited to small numbers of marine mammals. The estimated takes are below 12 percent of the population for all marine mammals except harbor porpoise (Table 6). For harbor porpoise, the estimate of 6,759 incidences of takes would be 60.2 percent of the population, if each single take were a unique individual. However, this is highly unlikely because the harbor porpoise in Washington waters shows site fidelity to small areas for periods of time that can extend between seasons (Hanson 
                    *et al.*
                     1999; Hanson 2007a, 2007b). For example, Hanson 
                    *et al.*
                     (1999) tracked a female harbor porpoise for 215 days, during which it remained exclusively within the southern Strait of Georgia region. Based on studies by Jefferson 
                    *et al.*
                     (2016), harbor porpoise abundance in the East Whidbey region, which is adjunct to the Mukilteo Ferry Terminal construction, is 497, and harbor porpoise abundance in the entire surrounding area of North Puget Sound is 1,798. Therefore, if the estimated incidents of take accrued to all the animals expected to occur in the entire North Puget Sound area (1,798 animals), it would be 16.01 percent of the Washington inland water stock of the harbor porpoise. Based on the analysis contained herein of the proposed activity (including the prescribed mitigation and monitoring measures) and the anticipated take of marine mammals, NMFS finds that small numbers of marine mammals will be taken relative to the population size of the affected species or stocks. Unmitigable Adverse Impact Analysis and Determination There are no relevant subsistence uses of the affected marine mammal stocks or species implicated by this action. Therefore, NMFS has determined that the total taking of affected species or stocks would not have an unmitigable adverse impact on the availability of such species or stocks for taking for subsistence purposes. Endangered Species Act (ESA) 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 West Coast Regional Office Protected Resources Division Office, whenever we propose to authorize take for endangered or threatened species.
                    ( print page 44176) The humpback whale and the killer whale (southern resident distinct population segment (DPS)) are the only marine mammal species listed under the ESA that could occur in the vicinity of WSDOT's proposed construction project. Two DPSs of the humpback whale stock, the Mexico DPS and the Central America DPS, are listed as threatened and endangered under the ESA, respectively. NMFS' Office of Protected Resources has initiated consultation with NMFS' West Coast Regional Office under section 7 of the ESA on the issuance of an IHA to WSDOT under section 101(a)(5)(D) of the MMPA for this activity. In July 2017, NMFS finished conducting its section 7 consultation and issued a Biological Opinion concluding that the issuance of the IHA associated with WSDOT's Mukilteo Multimodal Project is not likely to jeopardize the continued existence of the endangered humpback and the Southern Resident killer whales. Authorization As a result of these determinations, NMFS has issued an IHA to the Washington State Department of Transportation for the Mukilteo Multimodal Construction Project in Washington State, provided the previously described mitigation, monitoring, and reporting requirements are incorporated. Dated: September 18, 2017. Donna S. Wieting, Director, Office of Protected Resources, National Marine Fisheries Service.


[FR Doc. 2017-20144 Filed 9-20-17; 8:45 am] BILLING CODE 3510-22-P