Final Action Michelle Bachman, NEFMC Staff, Habitat PDT Chair
NEFMC Meeting June 16-18, 2015
Final Action Michelle Bachman, NEFMC Staff, Habitat PDT Chair - - PowerPoint PPT Presentation
Final Action Michelle Bachman, NEFMC Staff, Habitat PDT Chair NEFMC Meeting June 16-18, 2015 Purpose: Take final action on Omnibus EFH Amendment 2 Select final alternatives for: Georges Bank habitat note that the Committee updated
NEFMC Meeting June 16-18, 2015
Select final alternatives for:
Georges Bank habitat – note that the Committee
updated their recommendation on June 1
Gulf of Maine spawning and Georges Bank spawning
Other sections of the document were approved in April Submit the action to the National Marine Fisheries Service
for approval
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Materials:
1.
DEIS – Georges Bank sections of Volume 3
2.
Habitat Committee summary (June 1)
3.
Memo from Exec. Director on Ctte. pref. alternative (June 10)
4.
Correspondence
June 1, 2015 Georges Bank Analysis 3
Mobile bottom- tending gear closures Measures same as existing CAII groundfish area
Overlaps groundfish SAP Area Scallop access in future?
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7
Combines elements of 7 and 9; recommended
June 1, 2015 8
Gears allowed Gears excluded Pot gear for lobsters or hagfish Pelagic longline gear or pelagic hook-and-line gear, or harpoon gear Pelagic midwater trawl gear, with bycatch limits Tuna purse seine gear outside
as the Habitat Area of Particular Concern Groundfish trawls west of 67° 20’ W (in E. U.S./CAN SAP) Scallop dredges fishing as part
Non-pot fixed gears, including demersal longlines and gillnets Hook and line gear for groundfish Hydraulic clam dredges Groundfish trawls east of 67° 20’ W (outside of SAP) Scallop dredges fishing on a day at sea
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Gears allowed Gears excluded Fixed gears including traps, longlines, gillnets (perhaps different restrictions were intended east vs. west of 67° 20’?) Pelagic longline gear, pelagic hook-and- line, harpoons Recreational gears Mid-water trawls Purse seines Scallop dredges fishing as part of an access fishery Groundfish trawls west of 67° 20’ W (in
Hydraulic clam dredges Groundfish trawls east
Scallop dredges fishing
*as interpreted by staff
GB region within US EEZ – 50,273 km2 Hatched and crosshatched areas currently closed to MBTG – 8,780 km2 Mortality and habitat closures combined – 18,102 km2
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Alternative 1 Alternative 7 Alternative 8 Alternative 9 Committee Alternative Total Area = 3,162 km2 habitat closures
Total area = 10,801 km2 habitat and mortality combined
Total Area = 1,303 km2
278 km2
Shoal 2, 1,025 km2 Total Area = 4,788 km2
4,788 km2 Total Area = 1,949 km2
900 km2
607 km2
443 km2 Total area = 2,075
km2
700 km2
350 km2
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Substrate Area, km2 Low energy High energy M S G C B M S G C B No action EFH Closed Area I EFH N (607, #1)
Closed Area I EFH S (263, #1)
7% 1%
Closed Area II EFH (1,175, #1) 1% 1% <1%
650 No action groundfish Closed Area I GF (2,628, #1)
2% <1% 4,063 Closed Area II GF (2,904, #1) <1% 5% 1%
8% 2% <1% 6,826 Habitat management areas EFH South (195, #7)
8% 1% 277 Georges Shoal 2 (277, #7)
Northern Georges (3,229, #8) 2% 16% 1%
4,808 Western area (429, #9)
1% 895 Eastern area (517, #9)
9% 1% 611 Mortality area (1,099, #9)
1% 435 Georges Bank/GSC region (17,663, n/a) 2% 21% 1% <1%
8% 3% <1% 48,992
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June 1, 2015 Georges Bank Analysis 17
Alternative 1 Alternative 7
Alternative 9 CAI N Habitat CAI S Habitat CAII Habitat EFH South Georges Shoal 2 Northern Georges Western MBTG Eastern MBTG Mortality Closure 0.63 1.45 0.11 0.52 2.51 0.65 0.54 0.59 0.05 Stable Unstable Stable Stable Unstable Stable Stable Stable Stable
for juvenile cod and haddock, but the area overlaps more designations overall because it is so large
designated EFH
Species and lifestage EFH South Georges Shoal 2 Northern Georges Western Area Eastern Area Mortality Closure Atlantic cod juvenile Full Moderate Moderate High High High Haddock juvenile High None Moderate Slight High High Total score 68 47 72 60 69 79 Count of species represented (out of 23) 17 13 23 18 16 20 Count of designations represented (out of 43) 25 19 41 27 25 33
June 1, 2015 18
Caveats
Conclusions are preliminary right now The amount of fishing effort authorized in the Mortality
Closure or Reduced Impact HMA (Committee preferred) will have substantial bearing on the degree of adverse impacts minimization achieved.
Effort displacement into other vulnerable habitat types
will need to be considered – complex issue.
Current status as a habitat closure that has led to
benthic habitat recovery matters in terms of estimating impacts.
June 1, 2015 19
Estimated ranking of alternatives from most to least
Alternative 8 (Northern Georges HMA) – DEIS highly
positive (+++)
Alt 1/No Action – DEIS positive (++) Alternative 9 – not in DEIS Committee preferred alternative (similar to Alternative 9
in the east, and less adverse effects minimization in the west)
Alternative 7 – DEIS slightly positive (+)
DEIS: 3 ++, 4++, 5 --, 6A +++, 6B -
June 1, 2015 20
Species and season Alt 1 Alt 7 Alt 8 Alt 9 Ctte Yellowtail (Summer & Fall) 1 1 1 Red hake (Fall) 12 26 9 4 Haddock (Fall) 8 7 2 2 Winter flounder (Summer) 5 1 14 7 7 American plaice (Fall) 1 Windowpane (Fall) 2 Total 26 1 50 19 14
June 1, 2015 21
June 1, 2015 22
<15 cm
June 1, 2015 28
Species Alternative 1/No Action Alternative 7 Alternative 8 Alternative 9 Committee pref. Cod Positive Negative Highly Positive Slightly Negative Slightly Negative Haddock Highly Positive Highly Negative Positive Negative Negative Winter flounder Positive Negative Highly Positive Positive Slightly Positive Windowpa ne flounder Uncertain Uncertain Uncertain Uncertain Uncertain Yellowtail flounder Uncertain Uncertain Uncertain Uncertain Uncertain Considering only juvenile cod, haddock, winter flounder, yellowtail flounder, and windowpane flounder, the Committee’s preferred alternative would have mixed (impacts when compared to No Action. This assessment is preliminary and the conclusions may change upon review of additional data.
Alternative 9 MBTG Closure, 2005 - 2012 Alternative 9 MBTG Closure, 2008 - 2012 Alternative 9 MBTG Closure, 2010 - 2012
Bottom Trawl Clam Dredge Longline Midwater Trawl Other Gear Pot SAP Trawl Scallop Dredge
Graphs by Area and years
Western and Eastern Areas Mortality Area
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Western area Vessel Size Mean Rev Median Rev SD Rev Max Rev Min Rev Indv # trip
L 1,606,851 1,595,582 50,322 1,661,852 1,563,119 68 880
OTHER 156,550 149,903 27,352 186,613 133,135 15 96 Clam drg. ALL 595,306
59 SAP trawl ALL 112,597 123,802 53,483 159,590 54,400 24 129
L 870,492 1,018,994 647,439 1,430,778 161,703 36 51
OTHER 32,243 45,770 28,044 50,959
4 Mortality area Vessel Size Mean Rev Median Rev SD Rev Max Rev Min Rev Indv # trip
L 337,524 292,548 106,788 459,443 260,581 58 534
OTHER 20,803 21,597 10,576 30,959 9,853 12 56 SAP Trawl ALL 72,391 70,695 45,725 118,940 27,537 20 95
L 1,884,799 978,545 2,193,115 4,385,799 290,053 36 50
OTHER 116,059 97,604 119,583 243,796 6,776 3 4
June 1, 2015 30
June 1, 2015 31
currently open to fishing, and opens areas that would not be fishable to the clam industry given PSP closure
VTR) and substantial biomass of scallops within this area. Highly positive vs. Alt. 1 if extensive access allocated, lesser magnitude if fishing allocated at reduced rate
long term impacts when compared to the no action Alternative 1.
9 when compared to no action across all fisheries will depend greatly on the impact on the scallop fishery
production from closed areas, discussion of potential impacts of density dependence on growth, reproduction success, and mortality from predators
model generated estimates from RSA seasonal survey in CA1 and CA2
scallop biomass from dredge survey
How changes in closed areas fit with overall area rotation program. Three separate runs completed for 2015-2027
more recent trends in GOM (2013 and 2014)
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DEIS Conclusion: Generally Neutral
constraints in place that limit fishing overall and areas will remain closed to scallop fishery until future action considers opening them.
Scallop PDT Conclusions:
Impacts of closed areas on increased spawning success and yield
are currently uncertain and variable.
If there is no spawning advantage from high density closed areas
then net loss in yield, but if increased fertilization success in open areas from closures then beneficial impacts.
Closed areas may help prevent overfishing but there does not seem
to be strong evidence that they directly increase scallop recruitment success on GB.
With a greater understanding of these linkages Council could
consider specific closures to increase scallop recruitment in future action, but not a primary goal of OHA2.
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Left: Hennen and Hart (2012) Below: RSA Final Report (CFF 2013)
GB/GSC
more realistic
Background – Scallop specifications are complex
areas F in other areas can be set higher to compensate, but other constraints
1.
2.
F in open areas cannot exceed 0.38 (Fmsy) to prevent localized overfishing
3.
Scallop densities are not uniform - not always possible to replace all yield that may be inside a closed area, especially if very productive
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biomass in those areas (Table 9 in recent memo ~4,500 mt or 10 mil lbs.
due to other constraints in setting allocations
system comes into play
long term landings are higher when closures do not overlap productive areas (No closure run is ~107 million pounds ($ 722 mil) higher than No Action for all years (2015-2037), or ~$32 mill per year (6% of total revenues)
losses of yield within closures can be compensated for to some degree, but not always pound for pound
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Area Long-term yield (mean) Long-term yield (median) Biomass 2013* Short-term yield CAII North (all area north of scallop access area within CAII closure (subset
1,254 536 8,630 2,589
CAI-N Habitat Closure (subset of Alt 1)
601 42 4,841 1,452
CAI-S Habitat Closure (subset of Alt 1)
29 11 1,658 497
All Current Habitat Closures on GB (CAII north, CAIN and CAIS) (Does not include NL)
1,884 589 15,129 4,538
Northern Edge HMA (Alts 3 and 4)
1,214 502 7,433 2,230
EFH Extended 1 HMA (Alt 6A)
1,858 800 11,519 3,456
EFH Extended 2 HMA (Alt 6B)
825 324 4,493 1,348
Georges Shoal 2 MBTG HMA (Alt 7)
2 3 1
EFH South MBTG HMA (Alt 7)
23 10 440 139
Northern Georges MBTG HMA (Alt 8)
2,829 1,211 13,654 4,317
Western Area (MBTG closure, Alt 9)
52 8 22 6
Eastern Area (MBTG closure, Alt 9)
158 75 1,674 419
Mortality closure (Alt 9)
1,126 479 11,978 2995
Eastern Habitat Management Area – larger than Alternative 9
258 135 3,376 844
Reduced Impact Habitat Management Area – smaller than Alternative 9
1,079 419 10,617 2,654
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25 210 260 825 1,214 1,858 1,884 2,829 Alt 7 Alt 9 Cmte Pref Alt 6b Alt 3 and 4 Alt 6a Alt 1 Alt 8
Mean LY yield (mt)
Western MBTG HMA closures included in either Alt 7 or Alt 9 do
not have impacts on scallop fishery – very low scallop yield areas
Eastern MBTG HMA closures do not contain much scallop yield
either - low impact LT, Cmte Pref has higher ST impact than Alt9
(Cmte Pref Alt contains 258 mt (mean LT yield), which is more than the eastern areas in Alt 7 (23 mt) and Alt 9 (158 mt). LT about 100 mt more than Alt9 eastern area and about 400mt difference in ST).
Reduced Impact HMA closures in Alt 9 and Cmte Pref are similar
in terms of LT yield potential, but Cmte Pref has lower ST yield
Unclear how scallop fishery would actually access the RIHMA
(How often? Lower fishing mortality rate? Seasonal restrictions?) But expectation is that some of that yield potential would become landings, maybe not as much as presented in tables due to other constraints.
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Alt Area Proportion of total potential Long-term yield (mean) Proportion of total potential Long-term yield (median) Proportion of total short-term biomass (2013) Proportion of total short-term potential yield
(No Action) All Current Habitat Closures
CAIS) (Does not include NL)
7.5% 2.4% 13.4% 18.2%
Georges Shoal 2 MBTG HMA (Alt 7)
0.0% 0.0% 0.0% 0.0%
EFH South MBTG HMA (Alt 7)
0.1% 0.0% 0.4% 0.6%
Northern Georges MBTG HMA (Alt 8)
11.3% 4.8% 12.1% 17.3%
NEW EFH Western Area (MBTG closure, Alt 9)
0.2% 0.0% 0.0% 0.0%
NEW EFH Eastern Area (MBTG closure, Alt 9)
0.6% 0.3% 1.5% 1.7%
NEW Reduced Impact HMA (Alt 9)***
4.5% 1.9% 10.6% 12.0%
Alternative 9 **** (net access portion)
0.8% 0.3% 1.5% 1.7%
Final Cmte Rec. for Pref Alt. On GB EFH South MBTG HMA (Alt 7)
0.1% 0.0% 0.4% 0.6%
Eastern Habitat Management Area – larger than Alternative 9
1.0% 0.5% 3.0% 3.4%
Reduced Impact Habitat Management Area *** (smaller than Alternative 9)
4.3% 1.7% 9.4% 10.6%
Final Cmte Recommendation **** (net access portion)
1.1% 0.5% 3.4% 4.0%
June 1, 2015 43
Georges Bank and GSC Eastern Georges Bank
1982-2014 lobsters >=100mm:
June 1, 2015 45
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Framework 53’s cod protection measures became the
Are there other time/area closures necessary for
spawning protection in addition to what was implemented via Framework 53?
Alternative 3 - Massachusetts Bay Area, which has different
restrictions vs. the overlapping cod protection closures.
Closures of thirty minute blocks in April, which were removed
via Framework 53.
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Alternative 1 (No Action)
Western GOM and Cashes Ledge (year-round) Sector Rolling Closures: April, May, June Common Pool Rolling Closures: March–June, October, and November Gulf of Maine Cod Spawning Protection Area - ‘Whaleback’: April 1 – June
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Alternative 2
Sector Rolling Closures: April, May, June MA Bay Cod Spawning Closure – November 1 – January 31 Gulf of Maine Cod Spawning Protection Area -‘Whaleback’ (April 1 – June
30)
Option 1 would restrict commercial gears Option 2 would restrict commercial and recreational gears
Alternative 3
MA Bay Cod Spawning Closure – November 1 – January 31 Intended to be used in conjunction with the Alternative 1 (No Action)
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Framework 53 cod protection zones Framework 53 spawning area (i.e. Whaleback
Alternative 3: Massachusetts Bay area
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Concerns regarding FW 53 cod measures as adequate to meeting objectives of OHA2:
April closures proposed for opening historically important for spawning activity and Gulf
Reduce spawning protection for four other groundfish stocks: winter flounder, yellowtail flounder, plaice, and haddock in the Gulf of Maine
Effort shift could compromise the benefits from the FW 53 closures during December and January Analysis indicates that FW 53 will protect an additional 35 percent of the winter spawning biomass and 8 percent less of the spring spawning biomass.
Framework 53 provides spawning protection during the winter, which the status quo measures do not provide.
“Available information does not indicate whether the winter or spring spawning biomass is more important relative to overall contribution to cod recruitment.” (FW 53 Analysis)
“However, some analysis indicates that the winter spawning component may be much smaller than the spring component, although the reasons for this are unknown.” (FW 53 Analysis)
The available GOM cod spawning research suggests that once a specific spawning aggregation is lost, there is little indication that the aggregation could recolonize.” (FW 53 Analysis). Assessment Update in September 2015 for all 20 groundfish stocks
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Seasonal Closure (May) Closed Area I, Closed Area II, and Nantucket Lightship Closed Area
(year-round)
Alternative 2
Closed Area I, Closed Area II ( Feb. 1 – Apr. 15)
Closed Area I North and Closed Area II ( Feb. 1 – Apr. 15)
Option A (commercial gear), Option B (commercial and
recreational), Option C (exemption for scallop dredges)
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Closed Area I North and Closed Area II, Feb 1 – Apr 15
Closed to selected commercial and recreational gears (Option B),
exemption for sea scallop dredges (Option C)
Closed Area I and Closed Area II, Feb 1 – Apr 15
Closed to selected commercial and recreational gears (Option B)and
Council did not weigh in on sea scallop dredge exemption
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