[Federal Register Volume 82, Number 129 (Friday, July 7, 2017)]
[Rules and Regulations]
[Pages 31494-31511]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2017-14313]


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DEPARTMENT OF COMMERCE

National Oceanic and Atmospheric Administration

50 CFR Part 660

[Docket No. 160808696-7010-02]
RIN 0648-BG95


Magnuson-Stevens Act Provisions; Fisheries Off West Coast States; 
Pacific Coast Groundfish Fishery; 2017-2018 Biennial Specifications and 
Management Measures; Inseason Adjustments

AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and 
Atmospheric Administration (NOAA), Commerce.

ACTION: Final rule; inseason adjustments to biennial groundfish 
management measures.

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SUMMARY: This final rule announces inseason changes to management 
measures in the Pacific Coast groundfish fisheries. This action, which 
is authorized by the Pacific Coast Groundfish Fishery Management Plan 
(PCGFMP), is intended to allow fisheries to access more abundant

[[Page 31495]]

groundfish stocks while protecting overfished and depleted stocks.

DATES: This final rule is effective July 3, 2017.

FOR FURTHER INFORMATION CONTACT: Karen Palmigiano, phone: 206-526-4491, 
fax: 206-526-6736, or email: [email protected].

SUPPLEMENTARY INFORMATION: 

Electronic Access

    This rule is accessible via the Internet at the Office of the 
Federal Register Web site at https://www.federalregister.gov. 
Background information and documents are available at the Pacific 
Fishery Management Council's Web site at http://www.pcouncil.org/.

Background

    The PCGFMP and its implementing regulations at title 50 in the Code 
of Federal Regulations (CFR), part 660, subparts C through G, regulate 
fishing for over 90 species of groundfish off the coasts of Washington, 
Oregon, and California. Groundfish specifications and management 
measures are developed by the Pacific Fishery Management Council 
(Council), and are implemented by NMFS.
    The final rule to implement the 2017-2018 harvest specifications 
and management measures for most species of the Pacific coast 
groundfish fishery was published on February 7, 2017 (82 FR 9634).
    The Council, in coordination with Pacific Coast Treaty Indian 
Tribes and the States of Washington, Oregon, and California, 
recommended three changes to current groundfish management measures at 
its June 9-14, 2017 meeting. The changes the Council recommended 
include: (1) Increasing the limited entry (LE) and open access (OA) 
fixed gear trip limits for lingcod both north and south of 40[deg]10' 
North latitude (N. lat.), (2) modifying the shoreward boundary of the 
non-trawl rockfish conservation area (RCA) between 40[deg]10' N. lat. 
and 34[deg]27' N. lat., and (3) distributing the deductions initially 
made from the ACL (i.e. the off-the-top deductions, or ``buffer''), 25 
metric tons (mt) of Pacific ocean perch (POP) and 50 mt of darkblotched 
rockfish, and making it available to the mothership (MS) and catcher/
processor (C/P) sectors of the at-sea Pacific whiting fishery; 12.5 mt 
of POP and 25 mt of darkblotched rockfish, to each sector.

Fishery Management Measures for Lingcod LE and OA Fixed Gear North and 
South of 40[deg]10' N. lat.

    To increase harvest opportunities for LE and OA fixed gear sectors 
north and south of 40[deg]10' N. lat., the Council considered increases 
to lingcod trip limits for all remaining periods in 2017. Trip limits 
for lingcod north and south of 40[deg]10' N. lat. have been designated 
at 50 CFR 660.60(c)(1)(i) and in Section 6.2.1 of the PCGFMP as routine 
management measures.
    Lingcod are distributed coastwide with harvest specifications based 
on two area stock assessments that were conducted in 2009 for the areas 
north and south of the California-Oregon border at 42[deg] N. latitude. 
The stock assessments indicated west coast lingcod stocks are healthy 
with the stock depletion estimated for lingcod off of Washington and 
Oregon to be at 62 percent of its unfished biomass, and lingcod off of 
California estimated to be at 74 percent of its unfished biomass at the 
start of 2009. Trip limit increases, for species such as lingcod, are 
intended to reduce discarding (i.e., turn discards into landed catch 
and thereby improve catch accounting) and increase attainment of the 
non-trawl harvest guideline (HG). This change may result in a small 
increase in the catch of some overfished species, such as yelloweye 
rockfish, but such an increase is very unlikely to result in exceeding 
overfished species ACLs when combined with the harvest from all other 
sources.
    To assist the Council in evaluating increases to lingcod trip 
limits, the Groundfish Management Team (GMT) made model-based landings 
projections for the LE and OA fixed gear sector for north and south of 
40[deg]10' N. lat. for the remainder of the year. For these 
projections, the GMT included four recent updates to the discard 
mortality rates used by the West Coast Groundfish Observer Program 
(WCGOP) to estimate discard mortality each year and, by the GMT, in the 
nearshore model to project future discard mortality. The updates 
included: (1) Updating the gear proportions by depth with recent data; 
(2) calculating regional discard mortality rates to match the WCGOP 
estimate strata (i.e. north and south of 40[deg]10' N. lat.); (3) 
utilizing the Council approved changes to the ``sport-like'' surface 
discard mortality rates; and (4) incorporating a bias modifier to 
calibrate the gear proportions from WCGOP (a sub-sample of landings to 
reflect the gear proportions from fish tickets in the Pacific Fishery 
Information Network (PacFIN)). These landings projections also were 
based on the most recent information available.
    The model, using the new discard mortality rates, predicted a 
projected harvest of 71.2 mt, or 4.2 percent attainment of the 2017 
non-trawl allocation (1,680 mt), of lingcod north of 40[deg]10' N. lat. 
for both OA and LE fixed gear under the current trip limits, and an 
increase in projected harvest to 75 mt, or 4.4 percent attainment of 
the non-trawl allocation, of lingcod north of 40[deg]10' N. lat. for 
both OA and LE fixed gear under the recommended increased trip limits. 
The model also predicted a projected harvest of 91.8 mt, or 13 percent 
attainment of the non-trawl allocation (683 mt), of lingcod south of 
40[deg]10' N. lat. for both OA and LE fixed gear under the current trip 
limits, and an increase in projected harvest to 133.8 mt, or 19.6 
percent attainment of the non-trawl allocation, of lingcod south of 
40[deg]10' N. lat. for both OA and LE fixed gear under the recommended 
increased trip limits. Using the updated discard mortality rates, the 
model also predicted that under the current regulations harvest of 
yelloweye rockfish through the end of the year would be 0.7 mt lower 
(1.4 mt out of a 2.1 mt HG) than was anticipated at the start of this 
year.
    Yelloweye rockfish is an overfished species currently managed under 
a rebuilding plan. The projected impacts to yelloweye rockfish would 
increase under the increased trip limits for lingcod. Based on the 
GMT's analysis, the changes to the trip limits north of 40[deg]10' N. 
lat. are projected to result in an increase in lingcod landings through 
the end of the year of approximately 3.8 mt and a projected increase in 
yelloweye rockfish discard mortality of 0.06 mt. The same GMT analysis 
showed that an increase in trip limits for lingcod south of 40[deg]10' 
N. lat. would result in an increase in projected lingcod landings 
through the end of the year of 55 mt and an increase in yelloweye 
rockfish discard mortality of 0.21 mt. This increase in trip limits, 
and subsequent increase in lingcod landings, does not change total 
projected impacts to co-occurring overfished species from those 
anticipated in the 2017-18 harvest specifications and management 
measures, as the total projected impacts for those species assumes that 
the entire lingcod ACL is harvested.
    Therefore, the Council recommended and NMFS is implementing, by 
modifying Tables 2 (North and South) to part 660, subpart E and Tables 
3 (North and South) to part 660, subpart F in the CFR, trip limit 
changes for the LE and OA fixed gear fisheries north and south of 
40[deg]10' N. lat. The trip limits for lingcod in the LE fixed gear 
fishery north of 40[deg]10' N. lat. are increased from ``1,200 lb (544 
kg) bimonthly'' to ``1,400 lb (635 kg) bimonthly'' during periods 4 
through 5; from ``600 lb (272 kg) per month'' to ``700 lb (318 kg) 
bimonthly'' during the month of November; and

[[Page 31496]]

from ``200 lb (91 kg) per month'' to ``400 lb (181 kg) bimonthly'' 
during the month of December. The trip limits for lingcod in the LE 
fixed gear fishery south of 40[deg]10' N. lat. are increased from ``800 
lb (363 kg) bimonthly'' to ``1,200 lb (544 kg) bimonthly'' during 
periods 4 through 5; from ``400 lb (181 kg) bimonthly'' to ``600 lb 
(272 kg) per month'' during the month of November; and from ``200 lb 
(91 kg) per month'' to ``300 lb (136 kg) bimonthly'' during the month 
of December.
    The trip limits for lingcod in the OA fixed gear fishery north of 
40[deg]10' N. lat. are increased from ``600 lb (272 kg) per month'' to 
``700 lb (318 kg) per month'' during periods 4 through 5 and during the 
month of November; and from ``100 lb (45 kg) per month'' to ``200 lb 
(181 kg) per month'' during the month of December. The trip limits for 
lingcod in the OA fixed gear fishery south of 40[deg]10' N. lat. are 
increased from ``400 lb (181 kg) per month'' to ``600 lb (272 kg) per 
month'' during periods 3 through 5; and are increased from ``100 lb (45 
kg) per month'' to ``150 lb (68 kg) per month'' during the month of 
December.
    For the OA fixed gear fishery south of 40[deg]10' N. lat., the 
Council recommended a ``200 lb (91 kg) per month'' trip limit for 
lingcod during the month of November, which is lower than the current 
lingcod trip limit for November in the OA fixed gear fishery south of 
40[deg]10' N. lat. at ``400 lb (181 kg) per month.'' The Council 
recommended trip limit was based on an error in the GMT report and is 
inconsistent with the report's analysis of the estimated impacts, which 
analyzed a ``600 lb per month'' trip limit for lingcod during the month 
of November. NMFS understands the Council intent with the 
recommendations for changes to lingcod trip limits was to increase trip 
limits from what is currently in regulation to provide additional 
access and harvest a greater proportion of the lingcod ACL. It was not 
the Council's intent to reduce harvesting opportunities by reducing the 
OA fixed gear lingcod trip limits north of 40[deg]10' N. lat. for the 
month of November from 400 lb to 200 lb. Therefore, NMFS is not 
implementing the lower November trip limit for lingcod (200 lb (91 kg) 
per month) in the OA fixed gear fishery south of 40[deg]10' N. lat. for 
the month of November, and the trip limit for that month will remain at 
``400 lb (181 kg) per month.'' This trip limit during the month of 
November would reduce the projected lingcod impacts from those 
presented to the Council (146.7 mt) to 133.8 mt.

Fishery Management Measures for the Non-Trawl RCA between 40[deg]10' N. 
lat. and 34[deg]27' N. lat.

    The non-trawl RCA applies to vessels that take, retain, possess, or 
land groundfish using non-trawl gears, unless they are incidental 
fisheries that are exempt from the non-trawl RCA (e.g. the pink shrimp 
non-groundfish trawl fishery). The seaward and shoreward boundaries of 
the non-trawl RCAs vary along the coast, and are divided at various 
commonly used geographic coordinates, defined in Sec.  660.11, subpart 
C. Modifications to RCAs are designated as a routine management measure 
in Sec.  660.60(c)(3)(i) and section 6.2.1 of the PCGFMP.
    RCAs were originally established in the early 2000s to protect 
bocaccio and canary rockfishes which had recently been declared 
overfished.\1\ These large area closures were intended to close off 
areas to fishing in the main portion of the species' depth range to 
reduce encounters and subsequent mortality. At that same time, 
conservative trip limits, including no retention, were implemented to 
further reduce catches and overall mortality, and ensure the stocks 
would rebuild more quickly. Unfortunately, implementing RCAs also 
greatly reduced access to many healthy target stocks which were found 
in similar depths to overfished species. As a result, an important 
shelf rockfish fishery which used to operate south of 40[deg]10' N lat. 
was severely impacted.
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    \1\ Both canary rockfish and bocaccio were declared rebuilt in 
2015 and 2017, respectively.
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    In 2009, the shoreward boundary of the non-trawl RCA was 
established based on fishery information indicating that fishing in 
some areas in the non-trawl fishery have higher yelloweye rockfish 
catch rates than in others, and the RCA boundaries were adjusted to 
reduce mortality of yelloweye rockfish in these areas.
    Between 40[deg]10' N. lat. and 34[deg]27' N. lat., the non-trawl 
RCA is currently defined by the boundary lines approximating the 30 fm 
and 125 fm depth contours. All fishing with non-trawl gear must occur 
shoreward of the boundary line approximating the 30 fm depth contour, 
or seaward of the boundary line approximating the 125 fm depth contour. 
Changes to the non-trawl RCA shoreward boundary between 40[deg]10' N. 
lat. and 34[deg]27' N. lat., to shift the shoreward boundary deeper and 
open additional fishing area shoreward of the non-trawl RCA, were 
previously recommended by the California Department of Fish and 
Wildlife (CDFW) during the 2017-18 Harvest Specifications and 
Management Measures process. The Council did not ultimately recommend a 
boundary line change, at that time, due to the increased yelloweye 
rockfish projected impacts when fishing was opened in those areas.
    The GMT's recent updates to the discard mortality rates--discussed 
further under the preamble subheading Fishery Management Measures for 
Lingcod LE and OA Fixed Gear North and South of 40[deg]10' N. lat.--
resulted in projected impacts to yelloweye rockfish through the end of 
the year that were lower than anticipated during the development of the 
2017-18 harvest specifications and management measures. The Council has 
recommended modifying the shoreward non-trawl RCA boundary from the 
boundary line approximating the 30 fm depth contour to the boundary 
line approximating the 40 fm depth contour in the area from 40[deg]10' 
N. lat., and 34[deg]27' N. lat. The change to the non-trawl RCA 
shoreward boundary line in this area opens areas that have been closed 
since 2009, and may increase fishing efficiency and reduce gear 
conflicts by spreading the nearshore fleet over a larger fishing area. 
Opening this area is anticipated to increase overall landings of both 
target and non-target groundfish species, but mortality is anticipated 
to remain below the allocations or harvest limits for all species.
    Modifying the shoreward boundary of the non-trawl RCA in this area 
would provide harvest opportunities for many important target stocks, 
specifically deeper nearshore rockfish (blue, brown, copper, and olive 
rockfishes) and shelf rockfish species (chilipepper, greenblotched, 
Mexican, and vermilion rockfishes). Non-trawl harvest of groundfish is 
managed with cumulative trip limits, and any increased attainment is 
expected to remain within allowable harvest limits. Relatively small 
impacts to canary, bocaccio, and yelloweye rockfish are expected. All 
projected bocaccio and canary rockfish impacts would remain within the 
nearshore fishery share of the non-trawl allocations for those species.
    The GMT presented an updated analysis to the Council regarding the 
projected yelloweye rockfish impacts from modifying the shoreward 
boundary of the non-trawl RCA. The GMT assumed that effort would remain 
unchanged within the 0 fm to 10 fm depth bin, and all remaining effort 
would shift into deeper water (30 to 40 fm depth bin) when the boundary 
was modified. Yelloweye rockfish is an overfished species that is 
encountered primarily north of 40[deg]10' N. lat. Few

[[Page 31497]]

encounters occur south of 40[deg]10' N. lat., and no encounters occur 
south of 34[deg]27' N. lat. While some encounters may occur from 
modifying the non-trawl RCA shoreward boundary, they are expected to be 
rare. Projected impacts of yelloweye rockfish through the end of the 
year, including impacts of the increased lingcod trip limits discussed 
above, are within California's nearshore yelloweye rockfish HG share of 
0.7 mt. Based on the GMT's projections, the expected increase in 
yelloweye rockfish impacts is 0.15 mt from what was projected to occur 
in the absence of the inseason adjustments to management measures 
implemented in this action.
    Therefore, based on the new information available regarding the 
discard mortality of yellow-eye rockfish, the Council recommended and 
NMFS is adjusting the shoreward boundary of the non-trawl RCA between 
40[deg]10' N lat. and 34[deg]27' N. lat., by modifying Table 2 (South) 
to part 660, subpart E and Table 3 (South) to part 660, subpart F in 
the CFR, so that the boundary lines approximating the 40 fm and 125 fm 
depth contours, in this area, will define the non-trawl RCA in this 
area.

Transferring POP and Darkblotched Rockfish to the MS and C/P Sectors

    As part of the biennial harvest specifications and management 
measures process, annual ACLs are set for non-whiting groundfish 
species, deductions are made ``off-the-top'' from the ACL for various 
sources of mortality (including non-groundfish fisheries that catch 
groundfish incidentally, also called incidental open access fisheries) 
and the remainder, the fishery HG, is allocated among the groundfish 
fisheries. Regulations at Sec.  660.60(c)(3)(ii) allow NMFS to 
distribute these ``off-the-top'' deductions from the ACL to any sector 
through routine inseason action to make fish that would otherwise go 
unharvested available to other fisheries during the fishery year, and 
after the Council has made the appropriate considerations. Also 
consistent with section 6.5.2 of the PCGFMP, NMFS has the authority to 
implement management measures to reduce bycatch of non-groundfish 
species and, under certain circumstances, the measures may be 
implemented inseason. However, under no circumstances may the intention 
of such management measures be simply to provide more fish to a 
different user group or to achieve other allocation objectives. 
Therefore, distribution of POP and darkblocked rockfish to the at-sea 
sectors meets the criteria specified in regulation at Sec.  
660.60(c)(3)(ii) and the PCGFMP for a routine management measure.
    During development of the 2017-18 harvest specifications and 
management measures, the Council recommended, and NMFS implemented, a 
new category of ``off-the-top'' deduction, known as a ``buffer'' (81 FR 
75266). The buffer consists of an amount of yield that is deducted from 
the ACLs for canary and darkblotched rockfish, and POP, as described at 
Sec.  660.55(b) and specified in the footnotes to Tables 1a and 2a to 
subpart C. This new management measure set the fishery HG at an amount 
after the buffer was subtracted from the ACL. The result was a specific 
amount of yield for each of the three species (25 mt for POP, 50 mt for 
darkblotched rockfish, and 188 mt for canary rockfish) that was 
unallocated at the start of the year, but is held in reserve as a 
buffer, and can be distributed to fisheries in need after an unforeseen 
catch event occurs inseason. Distribution of the buffer must go to a 
sector that has demonstrated a need for receiving such a distribution 
and not for the sole purpose of extending a fishery before a need is 
demonstrated. Additionally, under the buffer approach, all sectors 
received a lower allocation of darkblotched rockfish and POP in 2017 
than they would have if the entire ACL was allocated; thereby, creating 
a potential for foregone yield by most sectors. However, foregone yield 
is expected to be inconsequential because historic attainment of these 
species has been low, with an average attainment from 2011-2014 of 41 
percent of the darkblotched rockfish ACLs and 35 percent of the POP 
ACLs.
    Pacific whiting fisheries encounter Klamath River Chinook salmon 
incidentally, particularly when fishing off the central and southern 
Oregon coast. At its March 2017 meeting, the Council received the most 
recent projections of salmon stock status (Preseason Report I) and 
considered that Klamath River Chinook will not meet escapement goals 
for 2017 by a historically large margin. At its April 2017 meeting, the 
Council recommended complete closure of commercial salmon fisheries off 
southern Oregon and northern California (approximately 44[deg] N. lat. 
to 40[deg]10' N. lat.) and closure of recreational salmon fisheries in 
similar areas (approximately 42[deg]45' N. lat. to 40[deg]10' N. lat.) 
to protect Klamath River Chinook salmon.
    Chinook salmon bycatch in the Pacific whiting fishery varies by 
latitude, with 81 percent of Chinook being taken when fishing between 
Cape Falcon (45[deg]46' N. lat.) and Cape Blanco (42[deg]50' N. lat.). 
This is a similar area in which Klamath River Chinook stocks are 
commonly encountered, where all commercial and recreational salmon 
fishing in 2017 is closed. At-sea processing of Pacific whiting is 
currently prohibited south of 42[deg] N. lat. (the Oregon-California 
border) per regulations at Sec.  660.131(e). Both the MS and C/P 
sectors expressed willingness at the April 2017 Council meeting to 
modify operations to avoid Chinook salmon bycatch, but acknowledged 
that difficulties were likely given their rockfish allocations and 
historically high Pacific whiting allocations. While moving harvesting 
operations north to Washington and northern Oregon has likely reduced 
impacts of the Pacific whiting fishery on Klamath River Chinook, catch 
of POP in the Pacific whiting fisheries has traditionally been highest 
when fishing off Washington.
    The limited availability of overfished species that can be taken as 
incidental catch in the Pacific whiting fisheries, particularly 
darkblotched rockfish and POP, led NMFS to implement sector-specific 
allocations for these species to the Pacific whiting fisheries. If the 
sector-specific allocation for a non-whiting species is reached, NMFS 
may close one or more of the at-sea sectors automatically, per 
regulations at Sec.  660.60(d). At the start of 2017, the MS and C/P 
sectors of the Pacific whiting fishery were allocated 9.0 mt and 12.7 
mt of POP, respectively, per regulations at Sec.  660.55(c)(1)(i)(B).
    At the Council's April meeting, the MS sector requested an increase 
to their POP set-aside to accommodate northern movement of the fleet to 
reduce harvest of Klamath River Chinook and to prevent closure of the 
MS sector prior to harvesting their full allocation of Pacific whiting. 
To accommodate movement of the at-sea fleets farther north, away from 
Klamath River Chinook and into waters with historically higher catch 
rates of POP, the Council recommended, and NMFS implemented a 
distribution of 7 mt of POP, from the off-the-top deductions that were 
made at the start of the 2017-2018 biennium, to the MS and C/P sectors, 
3.5 mt to each sector, to accommodate potential catch of POP as each 
sector prosecutes their 2017 Pacific whiting allocations in areas where 
bycatch of Klamath River Chinook is less likely (May 16, 2017, 82 FR 
22428). The Council's intent in distributing the POP, that would 
otherwise go unharvested, was to maintain 2017 harvest opportunities 
for the MS and C/P sectors of the Pacific whiting fishery,

[[Page 31498]]

while protecting Klamath River Chinook.
    At the June 2017 Council meeting, the MS and C/P sectors requested 
access to the darkblotched rockfish and POP ``buffers'' to continue to 
accommodate the northern movement of the fleet to reduce harvest of 
Klamath River Chinook and to prevent closure of either sector prior to 
harvesting their full allocation of Pacific whiting. In response to 
this request, the GMT analyzed the current attainments of Pacific 
whiting, darkblotched and canary rockfishes, and POP, as well as 
provided some model projections of the estimated needs of the MS and C/
P sectors for the 2017 fishing season.
    Based on the GMT's analysis, as of June 11, 2017, the MS sector had 
attained 7.6 percent of their total darkblotched rockfish allocation 
(0.9 mt out of 11.8 mt), 20.2 percent of their total POP allocation 
(2.5 mt out of 12.5 mt), and 22.2 percent of their total Pacific 
whiting allocation (19,334 mt out of 87,044 mt). Over the past 6 years, 
(2011-2016) by June 11th of each year, the MS sector has harvested an 
average of 0.84 mt of darkblotched rockfish, 1.65 mt of POP, and 
14,689.21 mt of Pacific whiting.
    Based on the GMT's analysis, as of June 11, 2017, the C/P sector 
had attained 26 percent of their total darkblotched rockfish allocation 
(4.3 mt out of 16.4 mt), 51.1 percent of their total POP allocation 
(8.3 mt out of 16.2 mt), and 31.9 percent of their total Pacific 
whiting allocation (39,973.5 mt out of 123,312 mt). Over the past 6 
years, (2011-2016) by June 11th of each year, the C/P sector has 
harvested an average of 1.05 mt of darkblotched rockfish, 1.35 mt of 
POP, and 31,595.85 mt of Pacific whiting.
    On June 20, 2017, NMFS considered additional POP, darkblotched 
rockfish, and Pacific whiting landing information for the C/P and MS 
sectors. As of that date, the C/P sector had harvested 28.6 percent 
(4.69 mt out of 16.4 mt) of their total darkblotched rockfish 
allocation, 89.81 percent (14.55 mt out of 16.2 mt) of their total POP 
allocation, and 37.64 percent (46,413.13 mt out of 123,312 mt) of their 
total Pacific whiting allocation. Additionally, as of the same date, 
the MS sector had harvested 8.56 percent (1.01 mt out of 11.8 mt) of 
their total darkblotched rockfish allocation, 22.64 percent (2.83 mt 
out of 12.5 mt) of their total POP allocation, and 27.48 percent 
(23,921.03 mt out of 87,044 mt) of their total Pacific whiting 
allocation.
    To continue to accommodate movement of the at-sea fleets farther 
north, away from Klamath River Chinook and into waters with 
historically higher catch rates of POP, both sectors would need 
additional darkblotched rockfish and POP quota to prevent their fishery 
from closing due to exceeding their overfished species allocations. The 
Council's intent is to provide fisheries with a demonstrated need 
access to quota that would otherwise go unharvested, maintain 2017 
harvesting opportunities for the MS and C/P sectors of the Pacific 
whiting fishery, and continue protecting Klamath River Chinook.
    Therefore, after reviewing the best available information on 
interactions between the Pacific whiting fleet and salmon, POP, and 
darkblotched rockfish, the Council recommended and NMFS is implementing 
a distribution of 25 mt of POP, from the off-the-top deductions that 
were made at the start of the 2017-2018 biennium, to the MS and C/P 
sectors, 12.5 mt to each sector, to accommodate potential catch of POP 
as each sector prosecutes their 2017 Pacific whiting allocations in 
areas where bycatch of Klamath River Chinook is less likely. 
Additionally, the Council recommended and NMFS is implementing a 
distribution of 50 mt of darkblotched rockfish, from the ``off-the-
top'' deductions that were made at the start of the 2017-2018 biennium, 
to the MS and C/P sectors, 25 mt to each sector, to accommodate 
potential catch of darkblotched rockfish as each sector prosecutes 
their 2017 Pacific whiting harvest in areas where bycatch of Klamath 
River Chinook is less likely. These changes are implemented through 
modifications to the footnotes for Table 1a and Table 1b to Part 660, 
Subpart C of the CFR.
    This rule distributes 25 mt of POP and 50 mt of darkblotched 
rockfish that is anticipated to go unharvested through the end of 2017 
to the MS and C/P sectors, implementing the Council's recommendation 
increases the POP allocations to 25 mt for the MS sector and 28.7 mt 
for the C/P sector and the darkblotched rockfish set-asides to 36.8 mt 
for the MS sector and 41.4 mt for the C/P sector. This rule also 
provides the fleet added flexibility to fish in areas where Klamath 
River Chinook are less likely to be encountered while reducing the risk 
of closure of the MS and C/P sectors prior to full attainment of the 
Pacific whiting allocation if higher catch rates of POP and 
darkblotched rockfish continue for the remainder of the 2017 fishing 
season. Transfer of POP and darkblotched rockfish to the MS and C/P 
sectors, when combined with projected impacts from all other sources, 
is not expected to result in greater impacts to POP, darkblotched 
rockfish, or other overfished species than originally projected through 
the end of the year.

Classification

    This final rule makes routine inseason adjustments to groundfish 
fishery management measures, based on the best available information, 
consistent with the PCGFMP and its implementing regulations.
    This action is taken under the authority of 50 CFR 660.60(c) and is 
exempt from review under Executive Order 12866.
    The aggregate data upon which these actions are based are available 
for public inspection at the Office of the Administrator, West Coast 
Region, NMFS, during business hours.
    NMFS finds good cause to waive prior public notice and comment on 
the revisions to groundfish management measures under 5 U.S.C. 553(b) 
because notice and comment would be impracticable and contrary to the 
public interest. Also, for the same reasons, NMFS finds good cause to 
waive the 30-day delay in effectiveness pursuant to 5 U.S.C. 553(d)(3), 
so that this final rule may become effective July 3, 2017. The 
adjustments to management measures in this document affect commercial 
fisheries in Washington, Oregon and California. No aspect of this 
action is controversial, and changes of this nature were anticipated in 
the biennial harvest specifications and management measures established 
through a notice and comment rulemaking for 2017-18.
    Accordingly, for the reasons stated below, NMFS finds good cause to 
waive prior notice and comment and to waive the delay in effectiveness.

Fishery Management Measures for Lingcod LE and OA Fixed Gear North and 
South of 40[deg]10' N. lat.

    At its June 2017 meeting, the Council recommended an increase to LE 
and OA fixed gear lingcod trip limits north and south of 40[deg]10' N. 
lat. be implemented as quickly as possible to allow harvest of lingcod 
to better attain, but not exceed, the 2017 ACLs. There was not 
sufficient time after that meeting to undergo proposed and final 
rulemaking before this action needs to be in effect. Affording the time 
necessary for prior notice and opportunity for public comment would 
prevent NMFS from managing the LE and OA fixed gear fishery using the 
best available science to increase harvesting opportunities without 
exceeding the ACLs for federally managed species in accordance with the 
PCGFMP and applicable law. These increases to trip limits must be 
implemented as quickly as possible to allow LE and OA fixed

[[Page 31499]]

gear fishermen an opportunity to harvest higher limits for lingcod 
coastwide.
    It is in the public interest for fishermen to have an opportunity 
to harvest more of the lingcod ACLs, north and south of 40[deg]10' N. 
lat., because the lingcod fishery contributes revenue to the coastal 
communities of Washington, Oregon, and California. This action, if 
implemented quickly, is anticipated to allow increased catch of lingcod 
through the end of the year, and allows harvest as intended by the 
Council, consistent with the best scientific information available.
    The Council considered updated discard mortality rates and the 
resulting best available projections of yelloweye rockfish harvest that 
became available at its June 2017 meeting. Projected impacts to 
yelloweye rockfish through the end of the year were 0.7 mt below the 
nearshore fishery's 2.1 mt share of the non-trawl allocation. Based on 
the new information showing lower than anticipated yelloweye rockfish 
discard mortality, and the need to provide additional harvesting 
opportunities for healthy and underutilized groundfish species, the 
Council recommended modifying the shoreward boundary of the non-trawl 
RCA to open additional area, while keeping harvest of yelloweye 
rockfish within its HGs and rebuilding ACL.

Fishery Management Measures for the Non-Trawl RCA between 40[deg]10' N. 
lat. and 34[deg]27' N. lat.

    It is in the public interest for fisherman to have increased access 
to fishing areas where high-value target species, such as canary and 
chilipepper rockfish, are available, because the commercial non-trawl 
fisheries contribute revenue to the coastal communities of Washington, 
Oregon, and California. This action, if implemented quickly, is 
anticipated to allow increased catch of healthy and underutilized 
groundfish, and allows harvest as intended by the Council, consistent 
with the best scientific information available.

Transferring POP to the MS and C/P Sectors

    At its June 2017 meeting, the Council recommended that the 
distribution of POP and darkblotched rockfish ``buffers'' to the MS and 
C/P sectors and be implemented as quickly as possible to facilitate 
fishing for Pacific whiting in northern waters to avoid bycatch of 
Klamath River Chinook salmon. There was not sufficient time after that 
meeting to undergo proposed and final rulemaking before this action 
needs to be in effect. Affording the time necessary for prior notice 
and opportunity for public comment would postpone transfer of POP and 
darkblotched rockfish to the MS and C/P sectors until later in the 
season, or potentially eliminate the possibility or doing so during the 
2017 calendar year entirely, and is therefore impractical. Failing to 
reapportion POP and darkblotched rockfish to the MS and C/P sectors in 
a timely manner could result in additional impacts to Klamath River 
Chinook salmon if catch of POP or darkblotched rockfish approaches the 
MS or C/P sectors' POP and darkblotched rockfish allocations and the 
fleet moves south to prevent a closure prior to their Pacific whiting 
allocations being harvested. Additionally, failing to reapportion the 
POP and darkblotched rockfish ``buffers'' in a timely manner could 
leave quota unharvested through the end of the year, which would 
prevent harvest as intended by the Council. New information and 
analyses that became available to the Council in June indicate that 
both the MS and C/P sectors need additional POP and darkblotched 
rockfish to decrease the likelihood of closing one or more of these 
sectors due to attainment of their rockfish allocations. Therefore, 
distribution of the POP and darkblotched rockfish buffers is consistent 
with regulations at Sec.  660.60(c)(3)(ii).
    It is in the public interest for the MS and C/P sectors to have an 
opportunity to harvest their allocations of Pacific whiting without 
interruption because the Pacific whiting fishery contributes a large 
amount of revenue to the coastal communities of Washington and Oregon. 
Additionally, it is in the public interest to continue to protect 
Klamath River Chinook and reduce potential fishing impacts from the 
Pacific whiting fishery in areas where directed salmon fishing has been 
prohibited. Providing more POP and darkblotched rockfish to the MS and 
C/P sector would allow them to fish further north, lowering the chances 
of encountering Klamath River Chinook. This action facilitates fleet 
dynamics to avoid bycatch of Klamath River Chinook salmon, and allows 
harvest as intended by the Council, consistent with the best scientific 
information available.

List of Subjects in 50 CFR Part 660

    Fisheries, Fishing, and Indian Fisheries.

    Dated: July 3, 2017.
Jennifer M. Wallace,
Acting Director, Office of Sustainable Fisheries, National Marine 
Fisheries Service.
    For the reasons set out in the preamble, 50 CFR part 660 is amended 
as follows:

PART 660--FISHERIES OFF WEST COAST STATES

0
1. The authority citation for part 660 continues to read as follows:

    Authority: 16 U.S.C. 1801 et seq., 16 U.S.C. 773 et seq., and 16 
U.S.C. 7001 et seq.


0
2. Tables 1a and 1b to part 660, subpart C, are revised to read as 
follows:

[[Page 31500]]

[GRAPHIC] [TIFF OMITTED] TR07JY17.008

    \a\ Annual catch limits (ACLs), annual catch targets (ACTs) and 
harvest guidelines (HGs) are specified as total catch values.
    \b\ Fishery HGs means the HG or quota after subtracting Pacific 
Coast treaty Indian tribes allocations and projected catch, 
projected research catch, deductions for fishing mortality in non-
groundfish fisheries, and deductions for EFPs from the ACL or ACT.
    \c\ Bocaccio. A stock assessment was conducted in 2015 for the 
bocaccio stock between the U.S.-Mexico border and Cape Blanco. The 
stock is managed with stock-specific harvest specifications south of 
40[deg]10'

[[Page 31501]]

N. lat. and within the Minor Shelf Rockfish complex north of 
40[deg]10' N. lat. A historical catch distribution of approximately 
7.4 percent was used to apportion the assessed stock to the area 
north of 40[deg]10' N. lat. The bocaccio stock was estimated to be 
at 36.8 percent of its unfished biomass in 2015. The OFL of 2,139 mt 
is projected in the 2015 stock assessment using an FMSY proxy of 
F50%. The ABC of 2,044 mt is a 4.4 percent reduction from the OFL 
([sigma]=0.36/P*=0.45) because it is a category 1 stock. The 790 mt 
ACL is based on the current rebuilding plan with a target year to 
rebuild of 2022 and an SPR harvest rate of 77.7 percent. 15.4 mt is 
deducted from the ACL to accommodate the incidental open access 
fishery (0.8 mt), EFP catch (10 mt) and research catch (4.6 mt), 
resulting in a fishery HG of 774.6 mt. The California recreational 
fishery has an HG of 326.1 mt.
    \d\ Cowcod. A stock assessment for the Conception Area was 
conducted in 2013 and the stock was estimated to be at 33.9 percent 
of its unfished biomass in 2013. The Conception Area OFL of 58 mt is 
projected in the 2013 rebuilding analysis using an FMSY proxy of 
F50%. The OFL contribution of 12 mt for the unassessed portion of 
the stock in the Monterey area is based on depletion-based stock 
reduction analysis. The OFLs for the Monterey and Conception areas 
were summed to derive the south of 40[deg]10' N. lat. OFL of 70 mt. 
The ABC for the area south of 40[deg]10' N. lat. is 63 mt. The 
assessed portion of the stock in the Conception Area is considered 
category 2, with a Conception area contribution to the ABC of 53 mt, 
which is an 8.7 percent reduction from the Conception area OFL 
([sigma]=0.72/P*=0.45). The unassessed portion of the stock in the 
Monterey area is considered a category 3 stock, with a contribution 
to the ABC of 10 mt, which is a 16.6 percent reduction from the 
Monterey area OFL ([sigma]=1.44/P*=0.45). A single ACL of 10 mt is 
being set for both areas combined. The ACL of 10 mt is based on the 
rebuilding plan with a target year to rebuild of 2020 and an SPR 
harvest rate of 82.7 percent, which is equivalent to an exploitation 
rate (catch over age 11+ biomass) of 0.007. 2 mt is deducted from 
the ACL to accommodate the incidental open access fishery (less than 
0.1 mt), EFP fishing (less than 0.1 mt) and research activity (2 
mt), resulting in a fishery HG of 8 mt. Any additional mortality in 
research activities will be deducted from the ACL. A single ACT of 4 
mt is being set for both areas combined.
    \e\ Darkblotched rockfish. A 2015 stock assessment estimated the 
stock to be at 39 percent of its unfished biomass in 2015. The OFL 
of 671 mt is projected in the 2015 stock assessment using an FMSY 
proxy of F50%. The ABC of 641 mt is a 4.4 percent reduction from the 
OFL ([sigma]=0.36/P*=0.45) because it is a category 1 stock. The ACL 
is set equal to the ABC, as the stock is projected to be above its 
target biomass of B40% in 2017. 77.3 mt is deducted from the ACL to 
accommodate the Tribal fishery (0.2 mt), the incidental open access 
fishery (24.5 mt), EFP catch (0.1 mt), research catch (2.5 mt) and 
an additional deduction for unforeseen catch events (50 mt), 
resulting in a fishery HG of 563.8 mt. Of the 50 mt initially 
deducted from the ACL to account for unforeseen catch events, 50 mt 
is distributed to the mothership and catcher/processor sectors 
inseason, 25 mt to each sector, consistent with 660.60(c)(3)(ii).
    \f\ Pacific ocean perch. A stock assessment was conducted in 
2011 and the stock was estimated to be at 19.1 percent of its 
unfished biomass in 2011. The OFL of 964 mt for the area north of 
40[deg]10' N. lat. is based on an updated catch-only projection of 
the 2011 rebuilding analysis using an F50% FMSY proxy. The ABC of 
922 mt is a 4.4 percent reduction from the OFL ([sigma]=0.36/
P*=0.45) because it is a category 1 stock. The ACL is based on the 
current rebuilding plan with a target year to rebuild of 2051 and a 
constant catch amount of 281 mt in 2017 and 2018, followed in 2019 
and beyond by ACLs based on an SPR harvest rate of 86.4 percent. 
49.4 mt is deducted from the ACL to accommodate the Tribal fishery 
(9.2 mt), the incidental open access fishery (10 mt), research catch 
(5.2 mt) and an additional deduction for unforeseen catch events (25 
mt), resulting in a fishery HG of 231.6 mt. Of the 10 mt initially 
deducted from the ACL to account for mortality in the incidental 
open access fishery, a total of 7 mt is distributed to the 
mothership and catcher/processor sectors inseason, 3.5 mt to each 
sector consistent with 660.60(c)(3)(ii), resulting in a 3 mt 
deduction from the ACL for mortality in the incidental open access 
fishery. Of the 25 mt initially deducted from the ACL to account for 
unforeseen catch events, 25 mt is distributed to the mothership and 
catcher/processor sectors inseason, 12.5 mt to each sector, 
consistent with 660.60(c)(3)(ii).
    \g\ Yelloweye rockfish. A stock assessment update was conducted 
in 2011. The stock was estimated to be at 21.4 percent of its 
unfished biomass in 2011. The 57 mt coastwide OFL is based on a 
catch-only update of the 2011 stock assessment, assuming actual 
catches since 2011 and using an FMSY proxy of F50%. The ABC of 47 mt 
is a 16.7 percent reduction from the OFL ([sigma]=0.72/P*=0.40) 
because it is a category 2 stock. The 20 mt ACL is based on the 
current rebuilding plan with a target year to rebuild of 2074 and an 
SPR harvest rate of 76.0 percent. 5.4 mt is deducted from the ACL to 
accommodate the Tribal fishery (2.3 mt), the incidental open access 
fishery (0.4 mt), EFP catch (less than 0.1 mt) and research catch 
(2.7 mt), resulting in a fishery HG of 14.6 mt. Recreational HGs 
are: 3.3 mt (Washington); 3 mt (Oregon); and 3.9 mt (California).
    \h\ Arrowtooth flounder. The arrowtooth flounder stock was last 
assessed in 2007 and was estimated to be at 79 percent of its 
unfished biomass in 2007. The OFL of 16,571 mt is derived from a 
catch-only update of the 2007 stock assessment assuming actual 
catches since 2007 and using an F30% FMSY proxy. The ABC of 13,804 
mt is a 16.7 percent reduction from the OFL ([sigma]=0.72/P*=0.40) 
because it is a category 2 stock. The ACL is set equal to the ABC 
because the stock is above its target biomass of B25%. 2,098.1 mt is 
deducted from the ACL to accommodate the Tribal fishery (2,041 mt), 
the incidental open access fishery (40.8 mt), and research catch 
(16.4 mt), resulting in a fishery HG of 11,705.9 mt.
    \i\ Big skate. The OFL of 541 mt is based on an estimate of 
trawl survey biomass and natural mortality. The ABC of 494 mt is an 
8.7 percent reduction from the OFL ([sigma]=0.72/P*=0.45) as it is a 
category 2 stock. The ACL is set equal to the ABC. 57.4 mt is 
deducted from the ACL to accommodate the Tribal fishery (15 mt), the 
incidental open access fishery (38.4 mt), and research catch (4 mt), 
resulting in a fishery HG of 436.6 mt.
    \j\ Black rockfish (California). A 2015 stock assessment 
estimated the stock to be at 33 percent of its unfished biomass in 
2015. The OFL of 349 mt is projected in the 2015 stock assessment 
using an FMSY proxy of F50%. The ABC of 334 mt is a 4.4 percent 
reduction from the OFL ([sigma]=0.36/P*=0.45) because it is a 
category 1 stock. The ACL is set equal to the ABC because the stock 
is projected to be above its target biomass of B40% in 2017. 1 mt is 
deducted from the ACL to accommodate EFP catch (1 mt), resulting in 
a fishery HG of 333 mt.
    \k\ Black rockfish (Oregon). A 2015 stock assessment estimated 
the stock to be at 60 percent of its unfished biomass in 2015. The 
OFL of 577 mt is projected in the 2015 stock assessment using an 
FMSY proxy of F50%. The ABC of 527 mt is an 8.7 percent reduction 
from the OFL ([sigma]=0.72/P*=0.45) because it is a category 2 
stock. The ACL is set equal to the ABC because the stock is above 
its target biomass of B40%. 0.6 mt is deducted from the ACL to 
accommodate the incidental open access fishery (0.6 mt), resulting 
in a fishery HG of 526.4 mt.
    \l\ Black rockfish (Washington). A 2015 stock assessment 
estimated the stock to be at 43 percent of its unfished biomass in 
2015. The OFL of 319 mt is projected in the 2015 stock assessment 
using an FMSY proxy of F50%. The ABC of 305 mt is a 4.4 percent 
reduction from the OFL ([sigma]=0.36/P*=0.45) because it is a 
category 1 stock. The ACL is set equal to the ABC because the stock 
is above its target biomass of B40%. 18 mt is deducted from the ACL 
to accommodate the Tribal fishery, resulting in a fishery HG of 287 
mt.
    \m\ Blackgill rockfish. Blackgill rockfish contributes to the 
harvest specifications for the Minor Slope Rockfish South complex. 
See footnote/pp.
    \n\ Cabezon (California). A cabezon stock assessment was 
conducted in 2009. The cabezon spawning biomass in waters off 
California was estimated to be at 48.3 percent of its unfished 
biomass in 2009. The OFL of 157 mt is calculated using an FMSY proxy 
of F45%. The ABC of 150 mt is based on a 4.4 percent reduction from 
the OFL ([sigma]=0.36/P*=0.45) because it is a category 1 stock. The 
ACL is set equal to the ABC because the stock is above its target 
biomass of B40%. 0.3 mt is deducted from the ACL to accommodate the 
incidental open access fishery, resulting in a fishery HG of 149.7 
mt.
    \o\ Cabezon (Oregon). A cabezon stock assessment was conducted 
in 2009. The cabezon spawning biomass in waters off Oregon was 
estimated to be at 52 percent of its unfished biomass in 2009. The 
OFL of 49 mt is calculated using an FMSY proxy of F45%. The ABC of 
47 mt is based on a 4.4 percent reduction from the OFL 
([sigma]=0.36/P*=0.45) because it is a category 1 species. The ACL 
is set equal to the ABC because the

[[Page 31502]]

stock is above its target biomass of B40%. There are no deductions 
from the ACL so the fishery HG is also equal to the ACL of 47 mt.
    \p\ California scorpionfish. A California scorpionfish 
assessment was conducted in 2005 and was estimated to be at 79.8 
percent of its unfished biomass in 2005. The OFL of 289 mt is based 
on projections from a catch-only update of the 2005 assessment 
assuming actual catches since 2005 and using an FMSY harvest rate 
proxy of F50%. The ABC of 264 mt is an 8.7 percent reduction from 
the OFL ([sigma]=0.72/P*=0.45) because it is a category 2 stock. The 
ACL is set at a constant catch amount of 150 mt. 2.2 mt is deducted 
from the ACL to accommodate the incidental open access fishery (2 
mt) and research catch (0.2 mt), resulting in a fishery HG of 147.8 
mt. An ACT of 111 mt is established.
    \q\ Canary rockfish. A stock assessment was conducted in 2015 
and the stock was estimated to be at 55.5 percent of its unfished 
biomass coastwide in 2015. The coastwide OFL of 1,793 mt is 
projected in the 2015 assessment using an FMSY harvest rate proxy of 
F50%. The ABC of 1,714 mt is a 4.4 percent reduction from the OFL 
([sigma]=0.36/P*=0.45) because it is a category 1 stock. The ACL is 
set equal to the ABC because the stock is above its target biomass 
of B40%. 247 mt is deducted from the ACL to accommodate the Tribal 
fishery (50 mt), the incidental open access fishery (1.2 mt), EFP 
catch (1 mt), research catch (7.2 mt), and an additional deduction 
for unforeseen catch events (188 mt), resulting in a fishery HG of 
1,466.6 mt. Recreational HGs are: 50 mt (Washington); 75 mt 
(Oregon); and 135 mt (California).
    \r\ Chilipepper. A coastwide update assessment of the 
chilipepper stock was conducted in 2015 and estimated to be at 64 
percent of its unfished biomass in 2015. Chilipepper are managed 
with stock-specific harvest specifications south of 40[deg]10' N. 
lat. and within the Minor Shelf Rockfish complex north of 40[deg]10' 
N. lat. Projected OFLs are stratified north and south of 40[deg]10' 
N. lat. based on the average historical assessed area catch, which 
is 93 percent for the area south of 40[deg]10' N. lat. and 7 percent 
for the area north of 40[deg]10' N. lat. The OFL of 2,727 mt for the 
area south of 40[deg]10' N. lat. is projected in the 2015 assessment 
using an FMSY proxy of F50%. The ABC of 2,607 mt is a 4.4 percent 
reduction from the OFL ([sigma]=0.36/P*=0.45) because it is a 
category 1 stock. The ACL is set equal to the ABC because the stock 
is above its target biomass of B40%. 45.9 mt is deducted from the 
ACL to accommodate the incidental open access fishery (5 mt), EFP 
fishing (30 mt), and research catch (10.9 mt), resulting in a 
fishery HG of 2,561.1 mt.
    \s\ Dover sole. A 2011 Dover sole assessment estimated the stock 
to be at 83.7 percent of its unfished biomass in 2011. The OFL of 
89,702 mt is based on an updated catch-only projection from the 2011 
stock assessment assuming actual catches since 2011 and using an 
FMSY proxy of F30%. The ABC of 85,755 mt is a 4.4 percent reduction 
from the OFL ([sigma]=0.36/P*=0.45) because it is a category 1 
stock. The ACL could be set equal to the ABC because the stock is 
above its target biomass of B25%. However, the ACL of 50,000 mt is 
set at a level below the ABC and higher than the maximum historical 
landed catch. 1,593.7 mt is deducted from the ACL to accommodate the 
Tribal fishery (1,497 mt), the incidental open access fishery (54.8 
mt), and research catch (41.9 mt), resulting in a fishery HG of 
48,406.3 mt.
    \t\ English sole. A 2013 stock assessment was conducted, which 
estimated the stock to be at 88 percent of its unfished biomass in 
2013. The OFL of 10,914 mt is projected in the 2013 assessment using 
an FMSY proxy of F30%. The ABC of 9,964 mt is an 8.7 percent 
reduction from the OFL ([sigma]=0.72/P*=0.45) because it is a 
category 2 stock. The ACL is set equal to the ABC because the stock 
is above its target biomass of B25%. 212.8 mt is deducted from the 
ACL to accommodate the Tribal fishery (200 mt), the incidental open 
access fishery (7.0 mt) and research catch (5.8 mt), resulting in a 
fishery HG of 9,751.2 mt.
    \u\ Lingcod north. The 2009 lingcod assessment modeled two 
populations north and south of the California-Oregon border (42[deg] 
N. lat.). Both populations were healthy with stock depletion 
estimated at 62 and 74 percent for the north and south, respectively 
in 2009. The OFL is based on an updated catch-only projection from 
the 2009 assessment assuming actual catches since 2009 and using an 
FMSY proxy of F45%. The OFL is apportioned north of 40[deg]10' N. 
lat. by adding 48% of the OFL from California, resulting in an OFL 
of 3,549 mt for the area north of 40[deg]10' N. lat. The ABC of 
3,333 mt is based on a 4.4 percent reduction ([sigma]=0.36/P*=0.45) 
from the OFL contribution for the area north of 42[deg] N. lat. 
because it is a category 1 stock, and an 8.7 percent reduction 
([sigma]=0.72/P*=0.45) from the OFL contribution for the area 
between 42[deg] N. lat. and 40[deg]10' N. lat. because it is a 
category 2 stock. The ACL is set equal to the ABC because the stock 
is above its target biomass of B40%. 278.2 mt is deducted from the 
ACL for the Tribal fishery (250 mt), the incidental open access 
fishery (16 mt), EFP catch (0.5 mt) and research catch (11.7 mt), 
resulting in a fishery HG of 3,054.8 mt.
    \v\ Lingcod south. The 2009 lingcod assessment modeled two 
populations north and south of the California-Oregon border (42[deg] 
N. lat.). Both populations were healthy with stock depletion 
estimated at 62 and 74 percent for the north and south, respectively 
in 2009.The OFL is based on an updated catch-only projection of the 
2009 stock assessment assuming actual catches since 2009 using an 
FMSY proxy of F45%. The OFL is apportioned by subtracting 48% of the 
California OFL, resulting in an OFL of 1,502 mt for the area south 
of 40[deg]10' N. lat. The ABC of 1,251 mt is based on a 16.7 percent 
reduction from the OFL ([sigma]=0.72/P*=0.40) because it is a 
category 2 stock. The ACL is set equal to the ABC because the stock 
is above its target biomass of B40%. 9 mt is deducted from the ACL 
to accommodate the incidental open access fishery (6.9 mt), EFP 
fishing (1 mt), and research catch (1.1 mt), resulting in a fishery 
HG of 1,242 mt.
    \w\ Longnose skate. A stock assessment was conducted in 2007 and 
the stock was estimated to be at 66 percent of its unfished biomass. 
The OFL of 2,556 mt is derived from the 2007 stock assessment using 
an FMSY proxy of F50%. The ABC of 2,444 mt is a 4.4 percent 
reduction from the OFL ([sigma]=0.36/P*=0.45) because it is a 
category 1 stock. The ACL of 2,000 mt is a fixed harvest level that 
provides greater access to the stock and is less than the ABC. 147 
mt is deducted from the ACL to accommodate the Tribal fishery (130 
mt), incidental open access fishery (3.8 mt), and research catch 
(13.2 mt), resulting in a fishery HG of 1,853 mt.
    \x\ Longspine thornyhead. A 2013 longspine thornyhead coastwide 
stock assessment estimated the stock to be at 75 percent of its 
unfished biomass in 2013. A coastwide OFL of 4,571 mt is projected 
in the 2013 stock assessment using an F50% FMSY proxy. The coastwide 
ABC of 3,808 mt is a 16.7 percent reduction from the OFL 
([sigma]=0.72/P*=0.40) because it is a category 2 stock. For the 
portion of the stock that is north of 34[deg]27' N. lat., the ACL is 
2,894 mt, and is 76 percent of the coastwide ABC based on the 
average swept-area biomass estimates (2003-2012) from the NMFS NWFSC 
trawl survey. 46.8 mt is deducted from the ACL to accommodate the 
Tribal fishery (30 mt), the incidental open access fishery (3.3 mt), 
and research catch (13.5 mt), resulting in a fishery HG of 2,847.2 
mt. For that portion of the stock south of 34[deg]27' N. lat. the 
ACL is 914 mt and is 24 percent of the coastwide ABC based on the 
average swept-area biomass estimates (2003-2012) from the NMFS NWFSC 
trawl survey. 3.2 mt is deducted from the ACL to accommodate the 
incidental open access fishery (1.8 mt), and research catch (1.4 
mt), resulting in a fishery HG of 910.8 mt.
    \y\ Pacific cod. The 3,200 mt OFL is based on the maximum level 
of historic landings. The ABC of 2,221 mt is a 30.6 percent 
reduction from the OFL ([sigma]=1.44/P*=0.40) because it is a 
category 3 stock. The 1,600 mt ACL is the OFL reduced by 50 percent 
as a precautionary adjustment. 509 mt is deducted from the ACL to 
accommodate the Tribal fishery (500 mt), research catch (7 mt), and 
the incidental open access fishery (2 mt), resulting in a fishery HG 
of 1,091 mt.
    \z\ Pacific whiting. The coastwide (U.S. and Canada) stock 
assessment was published in 2017 and estimated the spawning stock to 
be at 89 percent of its unfished biomass. The 2017 coastwide OFL of 
969,840 mt is based on the 2017 assessment with an F40% FMSY proxy. 
The 2017 coastwide, unadjusted Total Allowable Catch (TAC) of 
531,501 mt is based on the 2017 stock assessment and the 
recommendation by the Joint Management Committee (JMC), based on a 
precautionary approach. The U.S. TAC is 73.88 percent of the 
coastwide TAC, or 392,673 mt unadjusted TAC for 2017. 15 percent of 
each party's unadjusted 2016 TAC (48,760 mt for the U.S) is added to 
each party's 2017 unadjusted TAC, resulting in a U.S. adjusted 2017 
TAC of 431,433 mt. The 2017 fishery HG for Pacific whiting is 
362,682 mt. This amount was determined by deducting from the total 
U.S. TAC of 431,433 mt, the 77,251 mt tribal allocation, along with 
1,500 mt for scientific research catch and fishing mortality in non-
groundfish fisheries.
    \aa\ Petrale sole. A 2015 stock assessment update was conducted, 
which estimated the stock to be at 31 percent of its unfished

[[Page 31503]]

biomass in 2015. The OFL of 3,280 mt is projected in the 2015 
assessment using an FMSY proxy of F30%. The ABC of 3,136 mt is a 4.4 
percent reduction from the OFL ([sigma]=0.36/P*=0.45) because it is 
a category 1 stock. The ACL is set equal to the ABC because the 
stock is above its target biomass of B25%. 240.9 mt is deducted from 
the ACL to accommodate the Tribal fishery (220 mt), the incidental 
open access fishery (3.2 mt) and research catch (17.7 mt), resulting 
in a fishery HG of 2,895.1 mt.
    \bb\ Sablefish north. A coastwide sablefish stock assessment 
update was conducted in 2015. The coastwide sablefish biomass was 
estimated to be at 33 percent of its unfished biomass in 2015. The 
coastwide OFL of 8,050 mt is projected in the 2015 stock assessment 
using an FMSY proxy of F45%. The ABC of 7,350 mt is an 8.7 percent 
reduction from the OFL ([sigma]=0.36/P*=0.40). The 40-10 adjustment 
is applied to the ABC to derive a coastwide ACL value because the 
stock is in the precautionary zone. This coastwide ACL value is not 
specified in regulations. The coastwide ACL value is apportioned 
north and south of 36[deg] N. lat., using the 2003-2014 average 
estimated swept area biomass from the NMFS NWFSC trawl survey, with 
73.8 percent apportioned north of 36[deg] N. lat. and 26.2 percent 
apportioned south of 36[deg] N. lat. The northern ACL is 5,252 mt 
and is reduced by 525 mt for the Tribal allocation (10 percent of 
the ACL north of 36[deg] N. lat.). The 525 mt Tribal allocation is 
reduced by 1.5 percent to account for discard mortality. Detailed 
sablefish allocations are shown in Table 1c.
    \cc\ Sablefish south. The ACL for the area south of 36[deg] N. 
lat. is 1,864 mt (26.2 percent of the calculated coastwide ACL 
value). 5 mt is deducted from the ACL to accommodate the incidental 
open access fishery (2 mt) and research catch (3 mt), resulting in a 
fishery HG of 1,859 mt.
    \dd\ Shortbelly rockfish. A non-quantitative shortbelly rockfish 
assessment was conducted in 2007. The spawning stock biomass of 
shortbelly rockfish was estimated to be 67 percent of its unfished 
biomass in 2005. The OFL of 6,950 mt is based on the estimated MSY 
in the 2007 stock assessment. The ABC of 5,789 mt is a 16.7 percent 
reduction of the OFL ([sigma]=0.72/P*=0.40) because it is a category 
2 stock. The 500 mt ACL is set to accommodate incidental catch when 
fishing for co-occurring healthy stocks and in recognition of the 
stock's importance as a forage species in the California Current 
ecosystem. 10.9 mt is deducted from the ACL to accommodate the 
incidental open access fishery (8.9 mt) and research catch (2 mt), 
resulting in a fishery HG of 489.1 mt.
    \ee\ Shortspine thornyhead. A 2013 coastwide shortspine 
thornyhead stock assessment estimated the stock to be at 74.2 
percent of its unfished biomass in 2013. A coastwide OFL of 3,144 mt 
is projected in the 2013 stock assessment using an F50% FMSY proxy. 
The coastwide ABC of 2,619 mt is a 16.7 percent reduction from the 
OFL ([sigma]=0.72/P*=0.40) because it is a category 2 stock. For the 
portion of the stock that is north of 34[deg]27' N. lat., the ACL is 
1,713 mt. The northern ACL is 65.4 percent of the coastwide ABC 
based on the average swept-area biomass estimates (2003-2012) from 
the NMFS NWFSC trawl survey. 59 mt is deducted from the ACL to 
accommodate the Tribal fishery (50 mt), the incidental open access 
fishery (1.8 mt), and research catch (7.2 mt), resulting in a 
fishery HG of 1,654 mt for the area north of 34[deg]27' N. lat. For 
that portion of the stock south of 34[deg]27' N. lat. the ACL is 906 
mt. The southern ACL is 34.6 percent of the coastwide ABC based on 
the average swept-area biomass estimates (2003-2012) from the NMFS 
NWFSC trawl survey. 42.3 mt is deducted from the ACL to accommodate 
the incidental open access fishery (41.3 mt) and research catch (1 
mt), resulting in a fishery HG of 863.7 mt for the area south of 
34[deg]27' N. lat.
    \ff\ Spiny dogfish. A coastwide spiny dogfish stock assessment 
was conducted in 2011. The coastwide spiny dogfish biomass was 
estimated to be at 63 percent of its unfished biomass in 2011. The 
coastwide OFL of 2,514 mt is derived from the 2011 assessment using 
an FMSY proxy of F50%. The coastwide ABC of 2,094 mt is a 16.7 
percent reduction from the OFL ([sigma]=0.72/P*=0.40) because it is 
a category 2 stock. The ACL is set equal to the ABC because the 
stock is above its target biomass of B40%. 338 mt is deducted from 
the ACL to accommodate the Tribal fishery (275 mt), the incidental 
open access fishery (49.5 mt), EFP catch (1 mt), and research catch 
(12.5 mt), resulting in a fishery HG of 1,756 mt.
    \gg\ Splitnose rockfish. A coastwide splitnose rockfish 
assessment was conducted in 2009 that estimated the stock to be at 
66 percent of its unfished biomass in 2009. Splitnose rockfish in 
the north is managed in the Minor Slope Rockfish complex and with 
stock-specific harvest specifications south of 40[deg]10' N. lat. 
The coastwide OFL is projected in the 2009 assessment using an FMSY 
proxy of F50%. The coastwide OFL is apportioned north and south of 
40[deg]10' N. lat. based on the average 1916-2008 assessed area 
catch, resulting in 64.2 percent of the coastwide OFL apportioned 
south of 40[deg]10' N. lat., and 35.8 percent apportioned for the 
contribution of splitnose rockfish to the northern Minor Slope 
Rockfish complex. The southern OFL of 1,841 mt results from the 
apportionment described above. The southern ABC of 1,760 mt is a 4.4 
percent reduction from the southern OFL ([sigma]=0.36/P*=0.45) 
because it is a category 1 stock. The ACL is set equal to the ABC 
because the stock is estimated to be above its target biomass of 
B40%. 10.7 mt is deducted from the ACL to accommodate the incidental 
open access fishery (0.2 mt), research catch (9 mt) and EFP catch 
(1.5 mt), resulting in a fishery HG of 1,749.3 mt.
    \hh\ Starry flounder. The stock was assessed in 2005 and was 
estimated to be above 40 percent of its unfished biomass in 2005 (44 
percent in Washington and Oregon, and 62 percent in California). The 
coastwide OFL of 1,847 mt is set equal to the 2016 OFL, which was 
derived from the 2005 assessment using an FMSY proxy of F30%. The 
ABC of 1,282 mt is a 30.6 percent reduction from the OFL 
([sigma]=1.44/P*=0.40) because it is a category 3 stock. The ACL is 
set equal to the ABC because the stock was estimated to be above its 
target biomass of B25% in 2017. 10.3 mt is deducted from the ACL to 
accommodate the Tribal fishery (2 mt), and the incidental open 
access fishery (8.3 mt), resulting in a fishery HG of 1,271.7 mt.
    \ii\ Widow rockfish. The widow rockfish stock was assessed in 
2015 and was estimated to be at 75 percent of its unfished biomass 
in 2015. The OFL of 14,130 mt is projected in the 2015 stock 
assessment using the F50% FMSY proxy. The ABC of 13,508 mt is a 4.4 
percent reduction from the OFL ([sigma]=0.36/P*=0.45) because it is 
a category 1 stock. The ACL is set equal to the ABC because the 
stock is above its target biomass of B40%. 217.7 mt is deducted from 
the ACL to accommodate the Tribal fishery (200 mt), the incidental 
open access fishery (0.5 mt), EFP catch (9 mt) and research catch 
(8.2 mt), resulting in a fishery HG of 13,290.3 mt.
    \jj\ Yellowtail rockfish. A 2013 yellowtail rockfish stock 
assessment was conducted for the portion of the population north of 
40[deg]10' N. lat. The estimated stock depletion was 67 percent of 
its unfished biomass in 2013. The OFL of 6,786 mt is projected in 
the 2013 stock assessment using an FMSY proxy of F50%. The ABC of 
6,196 mt is an 8.7 percent reduction from the OFL ([sigma]=0.72/
P*=0.45) because it is a category 2 stock. The ACL is set equal to 
the ABC because the stock is above its target biomass of B40%. 1,030 
mt is deducted from the ACL to accommodate the Tribal fishery (1,000 
mt), the incidental open access fishery (3.4 mt), EFP catch (10 mt) 
and research catch (16.6 mt), resulting in a fishery HG of 5,166.1 
mt.
    \kk\ Minor Nearshore Rockfish north. The OFL for Minor Nearshore 
Rockfish north of 40[deg]10' N. lat. of 118 mt is the sum of the OFL 
contributions for the component species managed in the complex. The 
ABCs for the minor rockfish complexes are based on a sigma value of 
0.72 for category 2 stocks (blue/deacon rockfish in California, 
brown rockfish, China rockfish, and copper rockfish) and a sigma 
value of 1.44 for category 3 stocks (all others) with a P* of 0.45. 
The resulting ABC of 105 mt is the summed contribution of the ABCs 
for the component species. The ACL of 105 mt is the sum of 
contributing ABCs of healthy assessed stocks and unassessed stocks, 
plus the ACL contributions for blue/deacon rockfish in California 
where the 40-10 adjustment was applied to the ABC contribution for 
this stock because it is in the precautionary zone. 1.8 mt is 
deducted from the ACL to accommodate the Tribal fishery (1.5 mt) and 
the incidental open access fishery (0.3 mt), resulting in a fishery 
HG of 103.2 mt. Between 40[deg]10' N. lat. and 42[deg] N. lat. the 
Minor Nearshore Rockfish complex north has a HG of 40.2 mt. Blue/
deacon rockfish south of 42[deg] N. lat. has a stock-specific HG, 
described in footnote nn/.
    \ll\ Minor Shelf Rockfish north. The OFL for Minor Shelf 
Rockfish north of 40[deg]10' N. lat. of 2,303 mt is the sum of the 
OFL contributions for the component species within the complex. The 
ABCs for the minor rockfish complexes are based on a sigma value of 
0.36 for a category 1 stock (chilipepper), a sigma value of 0.72 for 
category 2 stocks (greenspotted rockfish between 40[deg]10' and 
42[deg] N. lat. and greenstriped rockfish), and a sigma value of 
1.44 for category 3 stocks (all others) with a

[[Page 31504]]

P* of 0.45. The resulting ABC of 2,049 mt is the summed contribution 
of the ABCs for the component species. The ACL of 2,049 mt is the 
sum of contributing ABCs of healthy assessed stocks and unassessed 
stocks, plus the ACL contribution of greenspotted rockfish in 
California where the 40-10 adjustment was applied to the ABC 
contribution for this stock because it is in the precautionary zone. 
83.8 mt is deducted from the ACL to accommodate the Tribal fishery 
(30 mt), the incidental open access fishery (26 mt), EFP catch (3 
mt), and research catch (24.8 mt), resulting in a fishery HG of 
1,965.2 mt.
    \mm\ Minor Slope Rockfish north. The OFL for Minor Slope 
Rockfish north of 40[deg]10' N. lat. of 1,897 mt is the sum of the 
OFL contributions for the component species within the complex. The 
ABCs for the Minor Slope Rockfish complexes are based on a sigma 
value of 0.39 for aurora rockfish, a sigma value of 0.36 for the 
other category 1 stock (splitnose rockfish), a sigma value of 0.72 
for category 2 stocks (rougheye rockfish, blackspotted rockfish, and 
sharpchin rockfish), and a sigma value of 1.44 for category 3 stocks 
(all others) with a P* of 0.45. A unique sigma of 0.39 was 
calculated for aurora rockfish because the variance in estimated 
spawning biomass was greater than the 0.36 used as a proxy for other 
category 1 stocks. The resulting ABC of 1,755 mt is the summed 
contribution of the ABCs for the component species. The ACL is set 
equal to the ABC because all the assessed component stocks (i.e., 
rougheye rockfish, blackspotted rockfish, sharpchin rockfish, and 
splitnose rockfish) are above the target biomass of B40%. 65.1 mt is 
deducted from the ACL to accommodate the Tribal fishery (36 mt), the 
incidental open access fishery (18.6 mt), EFP catch (1 mt), and 
research catch (9.5 mt), resulting in a fishery HG of 1,689.9 mt.
    \nn\ Minor Nearshore Rockfish south. The OFL for the Minor 
Nearshore Rockfish complex south of 40[deg]10' N. lat. of 1,329 mt 
is the sum of the OFL contributions for the component species within 
the complex. The ABC for the southern Minor Nearshore Rockfish 
complex is based on a sigma value of 0.72 for category 2 stocks 
(i.e., blue/deacon rockfish north of 34[deg]27' N. lat., brown 
rockfish, China rockfish, and copper rockfish) and a sigma value of 
1.44 for category 3 stocks (all others) with a P* of 0.45. The 
resulting ABC of 1,166 mt is the summed contribution of the ABCs for 
the component species. The ACL of 1,163 mt is the sum of the 
contributing ABCs of healthy assessed stocks and unassessed stocks, 
plus the ACL contribution for blue/deacon rockfish north of 
34[deg]27' N. lat. and China rockfish where the 40-10 adjustment was 
applied to the ABC contributions for these two stocks because they 
are in the precautionary zone. 4.1 mt is deducted from the ACL to 
accommodate the incidental open access fishery (1.4 mt) and research 
catch (2.7 mt), resulting in a fishery HG of 1,158.9 mt. Blue/deacon 
rockfish south of 42[deg] N. lat. has a stock-specific HG set equal 
to the 40-10-adjusted ACL for the portion of the stock north of 
34[deg]27' N lat. (243.7 mt) plus the ABC contribution for the 
unassessed portion of the stock south of 34[deg]27' N. lat. (60.8 
mt). The California (i.e. south of 42[deg] N. lat.) blue/deacon 
rockfish HG is 304.5 mt.
    \oo\ Minor Shelf Rockfish south. The OFL for the Minor Shelf 
Rockfish complex south of 40[deg]10' N. lat. of 1,917 mt is the sum 
of the OFL contributions for the component species within the 
complex. The ABC for the southern Minor Shelf Rockfish complex is 
based on a sigma value of 0.72 for category 2 stocks (greenspotted 
and greenstriped rockfish) and a sigma value of 1.44 for category 3 
stocks (all others) with a P* of 0.45. The resulting ABC of 1,624 mt 
is the summed contribution of the ABCs for the component species. 
The ACL of 1,623 mt is the sum of contributing ABCs of healthy 
assessed stocks and unassessed stocks, plus the ACL contribution of 
greenspotted rockfish in California where the 40-10 adjustment was 
applied to the ABC contribution for this stock because it is in the 
precautionary zone. 47.2 mt is deducted from the ACL to accommodate 
the incidental open access fishery (8.6 mt), EFP catch (30 mt), and 
research catch (8.6 mt), resulting in a fishery HG of 1,575.8 mt.
    \pp\ Minor Slope Rockfish south. The OFL of 827 mt is the sum of 
the OFL contributions for the component species within the complex. 
The ABC for the southern Minor Slope Rockfish complex is based on a 
sigma value of 0.39 for aurora rockfish, a sigma value of 0.72 for 
category 2 stocks (blackgill rockfish, rougheye rockfish, 
blackspotted rockfish, and sharpchin rockfish) and a sigma value of 
1.44 for category 3 stocks (all others) with a P* of 0.45. A unique 
sigma of 0.39 was calculated for aurora rockfish because the 
variance in estimated biomass was greater than the 0.36 used as a 
proxy for other category 1 stocks. The resulting ABC of 718 mt is 
the summed contribution of the ABCs for the component species. The 
ACL of 707 mt is the sum of the contributing ABCs of healthy 
assessed stocks and unassessed stocks, plus the ACL contribution of 
blackgill rockfish where the 40-10 adjustment was applied to the ABC 
contribution for this stock because it is in the precautionary zone. 
20.2 mt is deducted from the ACL to accommodate the incidental open 
access fishery (17.2 mt), EFP catch (1 mt), and research catch (2 
mt), resulting in a fishery HG of 686.8 mt. Blackgill rockfish has a 
stock-specific HG for the entire groundfish fishery south of 
40[deg]10' N lat. set equal to the species' contribution to the 40-
10-adjusted ACL. Harvest of blackgill rockfish in all groundfish 
fisheries counts against this HG of 120.2 mt. Nontrawl fisheries are 
subject to a blackgill rockfish HG of 44.5 mt.
    \qq\ Other Flatfish. The Other Flatfish complex is comprised of 
flatfish species managed in the PCGFMP that are not managed with 
stock-specific OFLs/ABCs/ACLs. Most of the species in the Other 
Flatfish complex are unassessed and include: butter sole, curlfin 
sole, flathead sole, Pacific sanddab, rock sole, sand sole, and rex 
sole. The Other Flatfish OFL of 11,165 mt is based on the sum of the 
OFL contributions of the component stocks. The ABC of 8,510 mt is 
based on a sigma value of 0.72 for a category 2 stock (rex sole) and 
a sigma value of 1.44 for category 3 stocks (all others) with a P* 
of 0.40. The ACL is set equal to the ABC. The ACL is set equal to 
the ABC because all of the assessed stocks (i.e., Pacific sanddabs 
and rex sole) were above their target biomass of B25%. 204 mt is 
deducted from the ACL to accommodate the Tribal fishery (60 mt), the 
incidental open access fishery (125 mt), and research catch (19 mt), 
resulting in a fishery HG of 8,306 mt.
    \rr\ Other Fish. The Other Fish complex is comprised of kelp 
greenling coastwide, cabezon off Washington, and leopard shark 
coastwide. The 2015 assessment for the kelp greenling stock off of 
Oregon projected an estimated depletion of 80 percent in 2015. All 
other stocks are unassessed. The OFL of 537 mt is the sum of the OFL 
contributions for kelp greenling coastwide, cabezon off Washington, 
and leopard shark coastwide. The ABC for the Other Fish complex is 
based on a sigma value of 0.44 for kelp greenling off Oregon and a 
sigma value of 1.44 for category 3 stocks (all others) with a P* of 
0.45. A unique sigma of 0.44 was calculated for kelp greenling off 
Oregon because the variance in estimated spawning biomass was 
greater than the 0.36 sigma used as a proxy for other category 1 
stocks. The resulting ABC of 474 mt is the summed contribution of 
the ABCs for the component species. The ACL is set equal to the ABC 
because all of the assessed stocks (kelp greenling off Oregon) were 
above their target biomass of B40%. There are no deductions from the 
ACL so the fishery HG is equal to the ACL of 474 mt.

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0
3. Tables 2 (North) and 2 (South) to part 660, subpart E, are revised 
to read as follows:

0
4. Tables 3 (North) and 3 (South) to part 660, subpart F, are revised 
to read as follows:
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[FR Doc. 2017-14313 Filed 7-3-17; 4:15 pm]
BILLING CODE 3510-22-C