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Great Bay Estuarine System (NH) (ID: 34)
Project last modified by
aspeers
on
January 12, 2010.
-
- Download Data
- See Associated Info (5)
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- Basic
- Viability
- Threats
- Viability Assessment
- Action Plan
- Strategy Effectiveness
- Indicators
- Resources
| Name |
|---|
|
TA1 DAMS/BARRIERS: Remove or reduce barriers to diadromous fish passage for 250 miles of rivers and tidal tributaries by 2012
|
|
TA2 PARASITES/PATHOGENS: Reduce levels of MSX/Dermo infection to <20% of standing stock for oysters by 2012
(more info)
|
|
TA3 FRESHWATER DIVERSION: Maintain freshwater flows into the estuary from tributaries and groundwater at current levels
|
|
TA4 HARVEST: Manage annual harvest of oysters and diadromous fish at sustainable levels that do not diminish species viability (i.e. ~5% of standing stock)
(more info)
|
|
TA5 INVASIVE SPECIES: Maintain estuarine extent of Phragmites at 2006 levels and avoid any new problem marine invasive species
(more info)
|
|
TA6 EUTROPHICATION: Reduce nitrogen and phosphorus loading to 1998 levels
(more info)
|
|
TA7 SEDIMENTATION: Maintain watershed impervious surface below 10% while controlling sources of runoff
(more info)
|
|
TA8 SHORELINE DEVELOPMENT: Maintain XX% of shoreline and river bank buffers (100' and 300') as undeveloped/pervious and unarmoured
|
|
TA9 CLIMATE CHANGE: Ensure to the extent possible that marine targets have capacity to adapt to sea level rise through gradual habitat shifts
|
|
TV1 SALT MARSH: Hydrologically restore 50 acres of salt marsh habitat by 2012
(more info)
|
|
TV2 EELGRASS: Restore 25% of suitable eelgrass habitat (100 acres) and increase biomass of 70% of beds to high-density (1996 levels) by 2017
(more info)
|
|
TV3: OYSTERS: Restore 25% of suitable oyster bed habitat (100 acres) through spawner sanctuaries and substrate deployment by 2012
(more info)
|
| Focal Conservation Target | Target Type | Habitat Type |
|---|---|---|
|
Salt marshes
(more info)
|
Ecological System |
|
|
Eelgrass meadows
(more info)
|
Ecological System |
|
|
Filter feeding bivalves
(more info)
|
Species Assemblage: Animals: Aquatic Invertebrates |
|
|
Tidal flat community
(more info)
|
Ecological System |
|
|
Macro invertebrates
(more info)
|
Species Assemblage: Animals: Aquatic Invertebrates | - |
|
Diadromous fish
(more info)
|
Species Assemblage: Animals: Fish |
|
|
Shorebirds & Piscivorous birds
(more info)
|
Species Assemblage: Animals: Birds |
|
|
Benthic fish assemblage
(more info)
|
Species Assemblage: Animals: Fish |
|
| Threat (Common Taxonomy) * | Targets Threatened |
|---|---|
|
Dams (Natural System Modifications :: Dams & Water Management/Use ) |
|
|
Parasites/pathogens (Invasive & Other Problematic Species & Genes :: Problematic Native Species ) |
|
|
Upland development (Residential & Commercial Development :: Housing & Urban Areas ) |
|
|
Harvest (Biological Resource Use :: Fishing & Harvesting Aquatic Resources ) |
|
|
Freshwater diversions (Natural System Modifications :: Dams & Water Management/Use ) |
|
|
Oil spills (Pollution :: Industrial & Military Effluents ) |
|
|
WWT & Septic (Pollution :: Household Sewage & Urban Waste Water ) |
|
|
Shoreline development (Residential & Commercial Development :: Housing & Urban Areas ) |
|
|
Climate Change (Climate Change & Severe Weather :: Habitat Shifting & Alteration ) |
|
|
Toxics (Pollution :: Industrial & Military Effluents ) |
|
|
Invasive species (Invasive & Other Problematic Species & Genes :: Invasive Non-Native/Alien Species ) |
|
|
Dredging & marine construction (Transportation & Service Corridors :: Shipping Lanes ) |
|
|
Boating activities (Human Intrusions & Disturbance :: Recreational Activities ) |
|
|
Lawn chemicals (Pollution :: Household Sewage & Urban Waste Water ) |
|
|
Atmospheric deposition (Pollution :: Air-Borne Pollutants ) |
|
|
Marsh dieback (Invasive & Other Problematic Species & Genes :: Problematic Native Species ) |
|
|
Mosquito control (Natural System Modifications :: Other Ecosystem Modifications ) |
|
|
Agricultural runoff (Pollution :: Agricultural & Forestry Effluents ) |
|
|
Beaver trapping (Biological Resource Use :: Hunting & Collecting Terrestrial Animals ) |
|
|
Canada geese (overwintering pop.) (Invasive & Other Problematic Species & Genes :: Problematic Native Species ) |
|
|
Ditches, berms, tide gates and culverts (Natural System Modifications :: Dams & Water Management/Use ) |
|
|
Historic pollution (Pollution :: Industrial & Military Effluents ) |
|
* For information on the common taxonomy of threats, see http://conservationmeasures.org/CMP/IUCN/.
| Strategy (Common Taxonomy) | Threats Addressed |
|---|---|
|
Advocate for improvement or new installation of fishways at dams on initial targets Lamprey River (MaCallen 10mi, Wiswall 37mi, Wadleigh 121mi) and Exeter River (Town 53mi, Pickpocket 14mi)
( Land/Water Management :: Habitat & Natural Process Restoration ) |
|
|
Advocate for NH’s adoption of Regional Greenhouse Gas Initiative, support NH "25 by 25" alternative energy initiative, and lobby for congressional action on a national climate/energy policy
( Law & Policy :: Policies & Regulations ) |
|
|
Advocate for the enhancement or new installation of fishways that reconnect diadromous fish to habitat on the Lamprey River (Macallen Dam 10 miles, Wiswall Dam 37 miles, Wadleigh Falls Dam 121 miles) and Exeter River (Exeter Dam 54 miles and Pickpocket Dam 14 miles)
( Land/Water Management :: Habitat & Natural Process Restoration ) |
|
|
Advocate for upgrades to Portsmouth and other 17 WWT facilities to tertiary by lobbying EPA/funders to require and support upgrades upon license renewals (15% nutrient reduction estimated)
( Law & Policy :: Policies & Regulations ) |
|
|
Analyze the extent to which harvest is impacting smelt, river herring, and winter flounder and develop strategies if necessary
( Species Management :: Species Management ) |
|
|
Build restoration partnership to develop shared vision, goals, and resources that enable large-scale restoration of historic oyster reefs and eelgrass beds in Great Bay and Little Bay
( External Capacity Building :: Alliance & Partnership Development ) |
|
|
Conduct a study to identify, and then advocate for removal/improvement of culverts that restrict fish passage on the Winnicut, Lamprey, and Exeter Rivers (initial target river systems, possibly expanded to other tributaries)
( Land/Water Management :: Habitat & Natural Process Restoration ) |
|
|
Conduct GIS analysis to determine % of undeveloped 100' and 300' riparian shoreline along Great Bay rivers and tributaries
( Land/Water Management :: Site/Area Management ) |
|
|
Develop local sea level rise models that inform estuarine land managers, public policy makers, and the land protection community
( Land/Water Management :: Site/Area Management ) |
|
|
Employ remote sensing and on-the-ground surveys to track and respond to Phragmites expansion
( Land/Water Management :: Invasive/Problematic Species Control ) |
|
|
Ensure sufficient freshwater flows to knock back oyster diseases.
( Land/Water Management :: Habitat & Natural Process Restoration ) |
|
|
Identify and protect eelgrass sanctuary areas where eelgrass has traditionally remained intact during wasting disease outbreaks
( Land/Water Protection :: Resource & Habitat Protection ) |
|
|
Improve town riparian buffer ordinances and encourage prime wetlands designation for surrounding towns
( Law & Policy :: Policies & Regulations ) |
|
|
Increase protection status of land in the Great Bay watershed to at least 15% and of land in the Conservation Focus Areas (as determined by the Land Conservation Plan for NH’s Coastal Watersheds) and to at least 25%
( Land/Water Protection :: Site/Area Protection ) |
|
|
Investigate feasibility of oyster reefs coupled with existing/new WWTF outfalls for nutrient reductions, freshwater disease control, and spawn sanctuary protection
( Land/Water Management :: Habitat & Natural Process Restoration ) |
|
|
Lobby for reduced oyster harvest limits to allow oysters to recover to sufficient coverage, density, and age class to achieve a self-sustaining status
( Species Management :: Species Management ) |
|
|
Partner with NHEP/CLF to promote local WW treatment improvements rather than regional outfall pipe
( Law & Policy :: Policies & Regulations ) |
|
|
Promote enactment of new regulations and local ordinances that minimize large-scale freshwater withdrawals (>50,000 gal/day)
( Law & Policy :: Policies & Regulations ) |
|
|
Promote improved enforcement of shoreline protection regulations and more restrictive permitting to minimize construction and development in buffers
( Law & Policy :: Compliance & Enforcement ) |
|
|
Support regional planning and policy initiatives for smart-growth and improved storm-water management to filter nutrient inputs due to lawn chemicals, septic, and agricultural runoff
( Law & Policy :: Policies & Regulations ) |
|
|
Support state, regional, and national climate change initiatives to mitigate potential sea surface temperature increases
( Law & Policy :: Policies & Regulations ) |
|
|
Support stormwater-control inititaves and outreach to reduce run-off deposition into the bay
( Education & Awareness :: Awareness & Communications ) |
|
|
Support the continued breeding and restoration of disease-resistant oyster
( Species Management :: Species Recovery ) |
|
|
Support the marine invasives detection initiative (Census for Marine Life) through vigilance and outreach opportunities
( Land/Water Management :: Invasive/Problematic Species Control ) |
|
|
Where appropriate, integrate eelgrass restoration sites with oyster beds to improve eelgrass density and overall health
( Land/Water Management :: Habitat & Natural Process Restoration ) |
|
|
Work with federal and state partners, and the NH River Restoration Task Force (RRTF), in support of dam removal projects on the Winnicut River (39 miles) and other potential sites including Stubbs/Peverly (2 miles) and Kennard (1 mile)
( Land/Water Management :: Habitat & Natural Process Restoration ) |
|
|
Work with GB Silt Commission and regional planning boards to control development and expansion of impervious areas
( Law & Policy :: Policies & Regulations ) |
|
|
Work with GBRPP and land protection community to increase shoreline buffer protection as much as possible
( Land/Water Management :: Habitat & Natural Process Restoration ) |
|
|
Work with NHEP, NHCP, USFWS to target and restore lost marsh (Stubbs Pond, Newington, 40 ac; Squamscott Rd, Stratham, 15 ac)
( Land/Water Management :: Habitat & Natural Process Restoration ) |
|
| Conservation Targets | Landscape Context | Condition | Size | Viability Rank | ||||
|---|---|---|---|---|---|---|---|---|
| Grade | Weight | Grade | Weight | Grade | Weight | |||
| 1 | Salt marshes | Fair | 1.0 | Good | 1.0 | - | 1.0 | Good |
| 2 | Eelgrass meadows | Fair | 1.0 | Fair | 1.0 | Good | 1.0 | Fair |
| 3 | Filter feeding bivalves | Fair | 1.0 | Fair | 1.0 | Poor | 1.0 | Fair |
| 4 | Tidal flat community | Fair | 1.0 | Good | 1.0 | Good | 1.0 | Good |
| 5 | Macro invertebrates | Fair | 1.0 | Fair | 1.0 | Good | 1.0 | Fair |
| 6 | Diadromous fish | Poor | 1.0 | Fair | 1.0 | Poor | 1.0 | Poor |
| 7 | Shorebirds & Piscivorous birds | Fair | 1.0 | Fair | 1.0 | Fair | 1.0 | Fair |
| 8 | Benthic fish assemblage | Fair | 1.0 | Fair | 1.0 | Fair | 1.0 | Fair |
| Project Biodiversity Health Rank | Fair | |||||||
You might have to scroll to see all of the table's data.
|
Project-specific Threats (Common Taxonomy *) |
Benthic fish assemblage | Diadromous fish | Eelgrass meadows | Filter feeding bivalves | Macro invertebrates | Salt marshes | Shorebirds & Piscivorous birds | Tidal flat community | Overall Threat Rank |
|---|---|---|---|---|---|---|---|---|---|
| Dams (Dams & Water Management/Use) |
- | Very High | - | Medium | - | Low | - | Low | High |
| Parasites/pathogens (Problematic Native Species) |
- | - | Medium | Very High | Low | - | - | - | High |
| Upland development (Housing & Urban Areas) |
Low | High | High | High | Low | Low | - | Low | High |
| Harvest (Fishing & Harvesting Aquatic Resources) |
High | High | - | High | Low | - | Low | - | High |
| Freshwater diversions (Dams & Water Management/Use) |
- | Very High | - | Low | - | - | - | - | High |
| Oil spills (Industrial & Military Effluents) |
- | High | Medium | High | Low | Low | Low | Medium | High |
| WWT & Septic (Household Sewage & Urban Waste Water) |
- | High | High | - | Low | Medium | - | Medium | High |
| Shoreline development (Housing & Urban Areas) |
Low | Low | Medium | Medium | Low | High | Medium | Medium | Medium |
| Climate Change (Habitat Shifting & Alteration) |
Low | Medium | Medium | Medium | Low | High | - | Low | Medium |
| Toxics (Industrial & Military Effluents) |
Low | High | - | Medium | Low | - | Low | - | Medium |
| Invasive species (Invasive Non-Native/Alien Species) |
Medium | Medium | Medium | Medium | Low | Low | - | Medium | Medium |
| Dredging & marine construction (Shipping Lanes) |
- | - | Medium | Medium | Low | - | - | Low | Medium |
| Boating activities (Recreational Activities) |
- | - | Medium | Medium | - | - | - | - | Medium |
| Lawn chemicals (Household Sewage & Urban Waste Water) |
- | - | Medium | - | Low | Low | - | Low | Low |
| Atmospheric deposition (Air-Borne Pollutants) |
- | - | Medium | - | - | Low | - | Low | Low |
| Marsh dieback (Problematic Native Species) |
- | - | - | - | - | Medium | - | - | Low |
| Mosquito control (Other Ecosystem Modifications) |
- | - | - | - | - | - | Medium | - | Low |
| Agricultural runoff (Agricultural & Forestry Effluents) |
- | - | - | - | - | Low | - | - | Low |
| Beaver trapping (Hunting & Collecting Terrestrial Animals) |
- | - | - | - | - | - | Low | - | Low |
| Canada geese (overwintering pop.) (Problematic Native Species) |
- | - | Low | - | - | - | - | - | Low |
| Ditches, berms, tide gates and culverts (Dams & Water Management/Use) |
- | - | - | - | - | Low | - | - | Low |
| Historic pollution (Industrial & Military Effluents) |
- | - | - | - | - | - | - | Low | Low |
| Threat Status for Targets and Project | Medium | Very High | High | Very High | Low | High | Medium | Medium | Very High |
| Categories & Measures | Score | |
|---|---|---|
| People | ||
| Staff Leadership | - | |
| Multidisciplinary Team | - | |
| People Average | - | |
Internal Resources |
||
| Institutional Learning | - | |
| Funding | - | |
| Internal Resources Average | - | |
External Resources |
||
| Social/Legal Framework for Conservation | - | |
| Community and Constituency Support | - | |
| External Resources Average | - | |
| Overall Project Resource Rank | ||
| Conservation Target | Key Attribute (Category) |
Indicator | Current Indicator Measurement | Rating Comments: (Poor, Fair Good Very Good) |
Current Rating and Date | Desired Rating and Date |
|---|---|---|---|---|---|---|
| Salt marshes |
Characteristic community
(Condition) |
% of salt marsh acreage dominated by native salt marsh vegetation |
-
|
Poor:
Extensive Phragmites throughout system
Fair: Widespread small patches Good: Most marshes with no Phragmites Very Good: No Phragmites |
Good
Feb 15, 2004 |
Good
|
| Salt marshes |
Characteristic community
(Condition) |
% salt marsh occurrences occupied by characteristic and ecologically significant animal species (mummichog & ribbed mussel) 1 |
-
|
Poor:
Absent
Fair: Present in low numbers Good: Abundant Very Good: Very abundant |
Good
Feb 15, 2004 |
Good
|
| Salt marshes |
Characteristic habitat structure
(Condition) |
Ratio of Spartina alterniflora (low) marsh to Spartina patens (high) marsh |
-
|
Poor:
Clear longterm loss trend
Fair: Most marshes appear stable Good: Stable at regional scale Very Good: Dynamic but stable over 25 years |
Good
Feb 15, 2004 |
Good
|
| Salt marshes |
Characteristic habitat structure
(Condition) |
Diverse habitat types: high & low marsh, fringes, sinuous creeks, bare ground, pools & pannes. |
-
|
Poor:
One community type dominates across system
Fair: Simplified structure across system Good: Mosaic of diverse communites across system Very Good: Mosaic of diverse communites across system |
Good
Jan 11, 2007 |
Very Good
|
| Salt marshes |
Ability to migrate
2
(Landscape Context) |
Percent natural buffer in 100 year sea level edge + 50 meters 3 |
-
|
Poor:
<50
Fair: 50-75 Good: 75-90 Very Good: >90 |
Very Good
Feb 15, 2004 |
Very Good
|
| Salt marshes |
Ability to migrate
4
(Landscape Context) |
Percent of upland edge not armored (natural shoreline) 5 |
-
|
Poor:
<70
Fair: >70 Good: >80 Very Good: >95 |
Very Good
Feb 15, 2004 |
Very Good
|
| Salt marshes |
Nutrient regime
6
(Landscape Context) |
NHEP freshwater (FW) & saltwater (SW) quality trends |
-
|
Poor:
FW and SW nutrients increasing
Fair: Stable or very slight > in nutrients Good: FW & SW nutrients trending down Very Good: FW & SW nutrients trending down |
Fair
Dec 1, 2006 |
Very Good
|
| Salt marshes |
Sediment regime
(Landscape Context) |
Accretion rate (mm per year) relative to sea level rise |
-
|
Poor:
Substantially less than sea level rise + subsidence
Fair: Slightly less than sea level rise + subsidence Good: Equal to sea level rise + subsidence Very Good: Slightly greater than sea level rise + subsidence |
Good
Feb 15, 2004 |
Good
|
| Salt marshes |
Tidal flooding regime
7
(Landscape Context) |
% salt marsh receiving natural tidal flooding regime |
-
|
Poor:
Extensive SW flow alterations.
Fair: Significant alterations affecting portion of marshes Good: Minor SW flow alteration w/natural collapse and fill Very Good: No ditches, dikes, berms, etc. |
Good
8
Feb 15, 2004 |
Good
9
|
| Eelgrass meadows |
Recruitment and growth
10
(Condition) |
Biomass metric tons (NHEP 5yr mean) |
-
|
Poor:
<500
Fair: 500-1000 Good: 1000-1500 Very Good: >1500 |
Fair
Dec 1, 2006 |
Very Good
|
| Eelgrass meadows |
Recruitment and growth
(Condition) |
% acres in >60% density classes (NHEP 5yr mean) |
-
|
Poor:
<30
Fair: 30-50 Good: 50-70 Very Good: >70 |
Fair
Dec 1, 2006 |
Very Good
|
| Eelgrass meadows |
Nutrient regime
11
(Landscape Context) |
Level of epiphytic fouling & macro algae growing within eelgrass beds |
-
|
Poor:
Extensive fouling causing mortality throughout system
Fair: Low-med. fouling causing mortality throughout system Good: Fouling occurs but does not cause extensive mortality Very Good: Fouling occurs but does not cause extensive mortality |
Good
Feb 15, 2004 |
Good
|
| Eelgrass meadows |
Water clarity
12
(Landscape Context) |
Mean annual incidence of low transparency (<1m @ hi. tide) |
-
|
Poor:
> 30%
Fair: 0.3 Good: < 30% Very Good: < 20% |
Fair
13
Jan 15, 2005 |
Good
|
| Eelgrass meadows |
Water clarity
14
(Landscape Context) |
Average depth of deep water edges (@ mean low water) |
-
|
Poor:
< 10'
Fair: > 10' Good: >15' Very Good: >20' |
Fair
|
Good
|
| Eelgrass meadows |
Water temperature regime
15
(Landscape Context) |
Cumulative peak degree days at index sites 16 |
-
|
Poor:
>5 days above 27C
Fair: 1-5 days above 27C Good: Similar to 20 year mean (use proxy) Very Good: Similar to 50 year mean (use proxy) |
Good
Feb 15, 2004 |
Good
|
| Eelgrass meadows |
Minimum dynamic area
17
(Size) |
Acres of eelgrass meadows (5 year mean) 18 |
-
|
Poor:
<1,200 ac
Fair: >1,200 ac Good: >2,000 ac Very Good: >3,000 ac |
Good
Aug 6, 2006 |
Very Good
|
| Filter feeding bivalves |
Characteristic community
19
(Condition) |
Presence of viable populations of all native species (oyster, softshell clam, gem clam, razor clam, ribbed mussel, blue mussel) |
-
|
Poor:
One or more native species extinct from the system
Fair: All native species present, some with poor viability Good: All native species present, variable viability Very Good: All native species present and robust |
Fair
20
Feb 15, 2004 |
Good
|
| Filter feeding bivalves |
Recruitment and growth
21
(Condition) |
Oyster disease index, 3 year mean (MSX) 22 |
-
|
Poor:
>15
Fair: 6-15 Good: 5.0 Very Good: 0.0 |
Fair
Dec 1, 2006 |
Very Good
|
| Filter feeding bivalves |
Recruitment and growth
23
(Condition) |
Number of oyster beds with > 5% Dermo infection 24 |
-
|
Poor:
>3
Fair: 2-3 Good: 1-2 Very Good: 0.0 |
Poor
Dec 1, 2006 |
Good
|
| Filter feeding bivalves |
Recruitment and growth
25
(Condition) |
Predator density. Green crab / Asian shore crab abundance index (CPUE) 26 |
-
|
Poor:
-
Fair: >50 CPUE Good: <50 CPUE Very Good: - |
Fair
Feb 15, 2004 |
Good
|
| Filter feeding bivalves |
Recruitment and growth
27
(Condition) |
Spatfall at index sites (rolling 5-year average) |
-
|
Poor:
0 spat per shell
Fair: 5-10 spat per shell Good: 10-20 spat per shell Very Good: > 20 spat per shell |
Very Good
28
Jan 7, 2007 |
Very Good
29
|
| Filter feeding bivalves |
Prey resources
30
(Landscape Context) |
Plankton community survey data 31 |
-
|
Poor:
-
Fair: - Good: - Very Good: - |
Very Good
Feb 15, 2004 |
Good
|
| Filter feeding bivalves |
Sediment regime
32
(Landscape Context) |
Siltation rate at index stations 33 |
-
|
Poor:
-
Fair: - Good: - Very Good: - |
Fair
34
Feb 15, 2004 |
Very Good
35
|
| Filter feeding bivalves |
Minimum dynamic area
(Size) |
Live oyster reef acreage |
-
|
Poor:
<200 ac
Fair: >200 ac Good: >500 ac Very Good: > 1,000 ac |
Poor
Dec 1, 2006 |
Fair
|
| Filter feeding bivalves |
Population size
(Size) |
Soft shell clam biomass |
-
|
Poor:
-
Fair: - Good: - Very Good: - |
Fair
36
Feb 15, 2004 |
Very Good
|
| Tidal flat community |
Characteristic community
(Condition) |
Benthic integrity index (EPA revised) |
-
|
Poor:
Declining
Fair: Slight deterioration Good: Stable Very Good: Improving |
Good
Feb 15, 2004 |
Good
|
| Tidal flat community |
Nutrient regime
37
(Landscape Context) |
NHEP and Coastwatch saltwater quality trends (2 year mean) |
-
|
Poor:
Declining
Fair: Slight deterioration Good: Stable Very Good: Improving |
Fair
Dec 1, 2006 |
Very Good
|
| Tidal flat community |
Nutrient regime
38
(Landscape Context) |
% acreage with Ulva cover |
-
|
Poor:
Very High
Fair: - Good: - Very Good: Low |
Good
39
Aug 15, 2006 |
Very Good
|
| Tidal flat community |
Water quality-toxics
(Landscape Context) |
GOMC Gulfwatch mussel bioassays (PAHs) |
-
|
Poor:
Toxicity concentrations very high
Fair: Good: Very Good: Toxicity concentrations very low |
Fair
Feb 15, 2004 |
Very Good
|
| Tidal flat community |
Minimum dynamic area
40
(Size) |
Acres of tidal flats |
-
|
Poor:
Fair: Below minimum size threshold Good: Above minimum size threshold Very Good: |
Good
41
Feb 15, 2004 |
Good
|
| Macro invertebrates |
Recruitment and growth
42
(Condition) |
Number of YOY lobster and horseshoe crab (rolling 5-year mean) 43 |
-
|
Poor:
-
Fair: - Good: - Very Good: - |
Fair
Feb 15, 2004 |
Very Good
|
| Macro invertebrates |
Water quality-toxics
(Landscape Context) |
GOMC Gulfwatch mussel bioassays (PAHs) |
-
|
Poor:
Toxic concentrations very high
Fair: Good: Very Good: Toxic concentrations very low |
Fair
Feb 15, 2004 |
Very Good
|
| Macro invertebrates |
Water temperature regime
44
(Landscape Context) |
Lobster disease index 45 |
-
|
Poor:
Disease widespread
Fair: Episodic outbreaks Good: Very low levels Very Good: Disease absent |
Good
Feb 15, 2004 |
Good
|
| Macro invertebrates |
Population size
46
(Size) |
Lobster CPUE trend (3 year mean / historic. mean) 47 |
-
|
Poor:
Declining
Fair: Stable over 3 years Good: Stable over 10 years Very Good: Stable over 10 years |
Good
Dec 1, 2006 |
Very Good
|
| Macro invertebrates |
Population size
(Size) |
Horseshoe crab survey trend (3 year mean / historic. mean) |
-
|
Poor:
Declining
Fair: Stable over 3 years Good: Stable over 10 years Very Good: Stable over 10 years |
Good
Feb 15, 2004 |
Very Good
|
| Diadromous fish |
Characteristic community
48
(Condition) |
# diadromous fish species present and viable |
-
|
Poor:
<5 species present
Fair: >5 present, some but not all viable Good: 7-8 present, most but not all viable Very Good: All 8 species present and viable |
Fair
Aug 15, 2006 |
Good
|
| Diadromous fish |
Recruitment and growth
49
(Condition) |
Rainbow smelt egg deposition survey data (NHFG, 3 year mean) |
-
|
Poor:
-
Fair: - Good: - Very Good: - |
Fair
Feb 15, 2004 |
Very Good
|
| Diadromous fish |
Recruitment and growth
50
(Condition) |
Number of juvenile fish successfully emigrating to estuary (NHFG seine survey trend) 51 |
-
|
Poor:
Decreasing for most runs
Fair: Stable across system-most runs Good: Stable and increasing- most runs Very Good: Increasing all runs |
Fair
Feb 15, 2004 |
Very Good
|
| Diadromous fish |
Connectivity (SW to FW)
52
(Landscape Context) |
% of miles of historic freshwater habitat currently accessible |
-
|
Poor:
<30%
Fair: 30-60% Good: 60-90% Very Good: >90% |
Poor
Feb 15, 2004 |
Good
|
| Diadromous fish |
Freshwater flow regime
53
(Landscape Context) |
Deviation from annual mean low flow (cubic feet/second) compared to natural range of variation in July-Sept 54 |
-
|
Poor:
Flow >25% of optimal
Fair: Flow within 25% of natural range of variation Good: Flow within 15% of natural range of variation Very Good: Flow within 10% of natural range of variation |
Fair
Feb 15, 2004 |
Very Good
|
| Diadromous fish |
Prey resources
55
(Landscape Context) |
Prey density index 56 |
-
|
Poor:
-
Fair: - Good: - Very Good: - |
Fair
Feb 15, 2004 |
Very Good
|
| Diadromous fish |
Water quality - DO
57
(Landscape Context) |
Milligrams per litre of dissolved oxygen, mean value June-Sep 58 |
-
|
Poor:
<5 mg/l
Fair: 5-6 mg/l Good: >6 mg/l Very Good: >9 mg/l |
Fair
59
Jan 11, 2007 |
Very Good
60
|
| Diadromous fish |
Population size
61
(Size) |
NHF&G fish passage count data (3 year mean) 62 |
-
|
Poor:
Decreasing for most runs
Fair: Increasing for some runs Good: Increasing or stable for all runs Very Good: Increasing for all runs |
Poor
Feb 15, 2004 |
Very Good
|
| Shorebirds & Piscivorous birds |
Recruitment and growth
63
(Condition) |
Number of osprey fledged per year (3 year mean) |
-
|
Poor:
<10
Fair: >10 Good: >15 Very Good: >20 |
Fair
Feb 15, 2004 |
Very Good
|
| Shorebirds & Piscivorous birds |
Habitat availibity
(Landscape Context) |
Percent natural buffer in 100 year sea level edge + 50 meters 64 |
-
|
Poor:
-
Fair: - Good: - Very Good: - |
-
|
-
|
| Shorebirds & Piscivorous birds |
Habitat availibity
(Landscape Context) |
Healthy beaver populations |
-
|
Poor:
-
Fair: - Good: - Very Good: - |
-
|
-
|
| Shorebirds & Piscivorous birds |
Prey resources
(Landscape Context) |
NHF&G fish passage count data (3 year mean) 65 |
-
|
Poor:
Decreasing for most runs
Fair: Increasing for some runs Good: Increasing or stable for all runs Very Good: Increasing for all runs |
Poor
Feb 15, 2004 |
Very Good
|
| Shorebirds & Piscivorous birds |
Prey resources
(Landscape Context) |
Benthic integrity index (EPA revised) |
-
|
Poor:
Declining
Fair: Slight deterioration Good: Stable Very Good: Improving |
Good
Aug 15, 2006 |
Good
|
| Shorebirds & Piscivorous birds |
Prey resources
(Landscape Context) |
Population size for key fish species 66 |
-
|
Poor:
-
Fair: - Good: - Very Good: - |
Fair
Feb 15, 2004 |
Very Good
|
| Shorebirds & Piscivorous birds |
Prey resources
(Landscape Context) |
Mussel tissue contamination level (lead, mercury, PCBs) |
-
|
Poor:
Declining
Fair: Stable Good: Improving Very Good: Negligible concentrations |
Fair
Feb 15, 2004 |
Good
|
| Shorebirds & Piscivorous birds |
Population size
(Size) |
Annual bird survey results (3 year means / historic means) |
-
|
Poor:
Declining -key sp.
Fair: Key species stable Good: Key species Increasing Very Good: Key species Abundant |
Fair
Feb 15, 2004 |
Very Good
|
| Benthic fish assemblage |
Recruitment and growth
(Condition) |
NHF&G Survey data: % of catch > 10 cm |
-
|
Poor:
< 5%
Fair: - Good: - Very Good: - |
Fair
Feb 15, 2004 |
Very Good
|
| Benthic fish assemblage |
Habitat availibity
67
(Landscape Context) |
Acres of eelgrass meadows (5 year mean) 68 |
-
|
Poor:
<1,200 ac
Fair: >1,200 ac Good: >2,000 ac Very Good: >3,000 ac |
Good
Dec 1, 2006 |
Very Good
|
| Benthic fish assemblage |
Water temperature regime
69
(Landscape Context) |
Num. of consecutive days winter spawning bottom temp exceeds 10 C 70 |
-
|
Poor:
-
Fair: - Good: - Very Good: - |
Fair
Feb 15, 2004 |
Very Good
|
| Benthic fish assemblage |
Population size
(Size) |
Recreational catch per unit effort (CPUE) |
-
|
Poor:
CPUE approaching 0.0
Fair: CPUE > 0.5 Good: CPUE > 1.5 Very Good: CPUE > 2.0 |
Fair
71
Dec 1, 2006 |
Good
|
| Benthic fish assemblage |
Population size
(Size) |
Spawning stock biomass (NOAA-GOM stock) |
-
|
Poor:
< 5 Mill. Lbs
Fair: 5-10 Mill. Lbs Good: 10-20 Mill. Lbs Very Good: >20 Mill. Lbs |
Fair
Feb 15, 2004 |
Very Good
|
COMMENTS:
1
Positive correlation with S. alterniflora productivity, water filtration services, increased marsh platform stability
2
Ultimate cause is global warming, proximate cause is sea level rise reducing size of marshes that cannot migrate inland because of topographical constraints or because adjacent uplands have been developed.
3
This needs further development. Possibly develop a migration potential index combining slope and buffer condition.
4
Ultimate cause is global warming, proximate cause is sea level rise reducing size of marshes that cannot migrate inland because of topographical constraints or because adjacent uplands have been developed.
5
15 cm every 100 years, or 1.5 mm per year is current rate according to http://www.nrel.colostate.edu/brd_global_change/proj_43_wetland_elev.html
This source also indicates natural salt marsh accretion is about the same - keeping pace.
6
Elevated nitrogen in estuarine water fuels fouling macro algae growth, alters microbial loop cycle and trophic dynamics. Toxic load from historic and current sources may alter community structure, favoring less sensitive species.
7
Watershed condition ultimate determinant of FW quantity and quality flowing into estuary through salt marshes. Percent impervious surfaces is a good measure for watershed condition. Impaired water quality (as a rough rule of thumb) begins at 10%. The 48 town area has an average of 6.3%; highest subwatershed level is 25.5% for Portsmouth harbor. Need to analyze further specifically for salt marsh subwatersheds.
9
Unrealistic to expect improvement, but goal should be to maintain pervious surfaces close to present levels.
10
Oyster abundance greatly reduced from historic levels. Remnant reefs exist but suffer from disease and poor recruitment. Establishment of additional reefs increases probablity of new source populations to restore ecological functions of oysters in the Great Bay estuary.
11
Great Bay eelgrass meadows declined during 1980s, lowest point in 1989. Cause was rapid spread of wasting disease -pathogen Labryrinthula zosterae. (Short and Mathieson, 1992). Decline followed by rapid inrease and recovery between 1989 and 1990 (Burdick et al. 1993). Recovery thought to be result of high rainfall limiting the pathogen, followed by high levels of eelgrass reproduction and seed dispersal. Loss and recovery both = approx. 700 ha[from NHEP 2000] Loss
12
Light attenuation has primacy over other threats according to Dr. Frederick Short of the Jackson Estuarine Lab, University of New Hampshire. This is caused both by excessive phytoplankton growth and suspended sediments. Dr. Shorts current research activities include analyis of the depth of eel grass meadow edges. Light attenuation controls depth at which eelgrass can survive and so eelgrass meadow area will shrink as water clarity becomes reduced.
13
Great Bay Coastwatch, 22 site survey with monthly samples. Confidence fairly good but some problems with survey - power may be low due to natural variablity
14
Light attenuation has primacy over other threats according to Dr. Frederick Short of the Jackson Estuarine Lab, University of New Hampshire. This is caused both by excessive phytoplankton growth and suspended sediments. Dr. Shorts current research activities include analyis of the depth of eel grass meadow edges. Light attenuation controls depth at which eelgrass can survive and so eelgrass meadow area will shrink as water clarity becomes reduced.
18
UNH Jackson Lab has been monitoring eelgrass beds for many years. Eelgrass has averaged about 2,000 acres of coverage over the past 10 years.
20
Shellfish survey data for oysters and softshell clams. High confidence.
NHEP Technical Characterization Report (2000) and State of the Estuary Reports
21
Oyster abundance greatly reduced from historic levels. Remnant reefs exist but suffer from disease and poor recruitment. Establishment of additional reefs increases probablity of new source populations to restore ecological functions of oysters in the Great Bay estuary.
23
Oyster abundance greatly reduced from historic levels. Remnant reefs exist but suffer from disease and poor recruitment. Establishment of additional reefs increases probablity of new source populations to restore ecological functions of oysters in the Great Bay estuary.
25
Oyster abundance greatly reduced from historic levels. Remnant reefs exist but suffer from disease and poor recruitment. Establishment of additional reefs increases probablity of new source populations to restore ecological functions of oysters in the Great Bay estuary.
27
Oyster abundance greatly reduced from historic levels. Remnant reefs exist but suffer from disease and poor recruitment. Establishment of additional reefs increases probablity of new source populations to restore ecological functions of oysters in the Great Bay estuary.
32
Oyster recruitment and persistence requires relatively silt free substrates and restoration of some reefs may require correcting altered sedimentation rates.
36
There is currently very little information on the status of softshell clam beds in Great Bay. Density within existing beds is highly variable based on harvest pressure, substrate characteristics, and other factors. Biomass may be a better inidicator and measaure of ecologial services provided by softshell clams.
37
Elevated nutrient levels stimulate excessive macroalgae growth which can smother tideflat organisms, lower oxygen levels, and alter community and habitat structure.
38
Great Bay mudflats are maintained by a balance of erosional and depositional processess. The majority of sedimentation occurs through resuspension of fine materials from wind and tide driven currents, but riverine sources also nourish tideflats. Natural erosional processes are driven by ice, tides and wind. The feeding activities of benthic invertebrates within tide flats tend to bind sediments and reduce resuspension rates, and macroalgae such as Ulva lactuca shield fine materials from erosion by wind and tides. Consequently, there is a seasonal pattern of net erosion in winter months and net accretion during the summer.
Anthropogenic impacts that reduce sedimentation include dams and hardened shorelines which block sediments from reaching the estuary. Dredging, boating activity, and flashy urban runnoff associated with impervious surfaces all increase sediment loading. Limited data suggests a decreasing trend in Great Bay turbidity.
NHEP, 2000; Short personal communication.
40
Tidal mud flats are dynamic at high temporal scale and depend on redeposition of continuously eroded material for persistence. The combined effects of sediment starvation due to dams and hardened shorelines and sea level rise could reduce size to a level that is no longer viable.
42
Population size for macroinvertebrates is largely determined by environmental factors affecting survival of larvae and early life stages.
43
Cycles with large fluctuations are natural for these species. Populations must be maintained above critical thresholds to prevent reproductive failure and persistent poor year classes. Critical thresholds are unknown and must be estimated from historical observations.
45
Cycles with large fluctuations are natural for these species. Populations must be maintained above critical thresholds to prevent reproductive failure and persistent poor year classes. Critical thresholds are unknown and must be estimated from historical observations.
46
Adult lobster harvested by active commercial and recreational fisheries. Juvenile lobster subject to high predation from various fish.
47
Cycles with large fluctuations are natural for these species. Populations must be maintained above critical thresholds to prevent reproductive failure and persistent poor year classes. Critical thresholds are unknown and must be estimated from historical observations.
48
There are eight characteristic diadromous fish that historically occupied the Great Bay system including: rainbow smelt, alewife, blueback herring, American shad, sea lamprey, American eel, Atlantic salmon, Atlantic sturgeon.
49
Juvenile survival and emmigration from freshwater is a critical bottleneck. Impacts to water quality and quantity reduce diadromous fish population size. Anthropogenic sources of stress include freshwater withdrawals, impoundments, and runoff. River herring are particularly sensitive to low oxygen and elevated nitrogen levels.
Within the estuary, rearing habitat and abundance of prey resources may be controlling factors. Young fish survival is inextricably tied to ability to reach predator size refuges (grow larger than gape of predators). Obviously, positive growth rates are necessary for persistence
50
Juvenile survival and emmigration from freshwater is a critical bottleneck. Impacts to water quality and quantity reduce diadromous fish population size. Anthropogenic sources of stress include freshwater withdrawals, impoundments, and runoff. River herring are particularly sensitive to low oxygen and elevated nitrogen levels.
Within the estuary, rearing habitat and abundance of prey resources may be controlling factors. Young fish survival is inextricably tied to ability to reach predator size refuges (grow larger than gape of predators). Obviously, positive growth rates are necessary for persistence
51
Ideally, we would have threshold values for each fish species of interest. In the absence of that, we are thinking about trends but recognize these as of limited value.
52
Dams are limitiing access spawning habiat and reducing juvenile survival during downstream migration. Fish passage is provided at all dams except for a dam on the Bellamy river, however, current fishways are not optimal for all anadromous species and upstream impoundments reduce suitable spawning and rearing habitat. Impoundments subject to stratification with low oxygen layers that contribute to adult and juvenile mortality.
53
Low flow in freshwater juvenile rearing streams identified as a significant source of mortality. Outmigrating juvenile river herring need adequate water volume and velocity. Mortality rates elevated when transit time is prolonged and very low flow can prevent migration. Low flow also a precursor of hypoic or anoxic conditons. (Mather and Juanes, xxxx)
54
Site specific values based on existing USGS flow records established for x,y, and z rivers. Earliest 10 years of record used as proxy for optimal flow conditions, based on assumption that anthropogenic removals have increased as a function of time. This assumption needs further evaluation.
55
Food availability is a determinant of fitness and survival. Note average weight also influenced by other stressors (water quality).
57
Low dissolved oxygen is implicated as a major cause of anadromous fish mortality in several studies, and blue back herring are known to be particularly sensitive (Mather and Juanes, 1999). Low DO in GB rivers noted in NHEP 2000 tech. report, particulary for the Exeter/Squamscott. Low DO can be caused by anthropogenic nutrient loading, elevated water temperature, and stratification in impoundments.
61
There are regulated recreational fisheries for rainbow smelt, shad, and river herring. These fisheries target pre-reproductive fish and should be managed in consideration of natural stock fluctuations and harvests occurring outside of Great Bay. Need to add more information evaluating current fishery management strategy. Atlantic salmon, Atlantic sturgeon and shortnose sturgeon are not subject to legal fishing. Eel harvest pressure thought to be low. Predation on elvers ....
Natural predation ocurring during juvenile and adult life stages of diadromous fish is a major factor controlling population size and reproductive capacity. More specific information is needed.
64
This needs further development. Possibly develop a migration potential index combining slope and buffer condition.
67
Winter flounder are closely associated with eelgrass beds, and thus the extent of eelgrass may be very indicative of habitat availibility.
- Show all:
Objective: TA1 DAMS/BARRIERS: Remove or reduce barriers to diadromous fish passage for 250 miles of rivers and tidal tributaries by 2012
-
Strategic Action: Work with federal and state partners, and the NH River Restoration Task Force (RRTF), in support of dam removal projects on the Winnicut River (39 miles) and other potential sites including Stubbs/Peverly (2 miles) and Kennard (1 mile)
- Action Step: Engage with dam removal working groups, attend hearings, provide support
- Action Step: Organize and launch the Great Bay Restoration Partnership
- Action Step: Seek out other "opportunistic" projects for dam removal
-
Strategic Action: Conduct a study to identify, and then advocate for removal/improvement of culverts that restrict fish passage on the Winnicut, Lamprey, and Exeter Rivers (initial target river systems, possibly expanded to other tributaries)
- Action Step: Develop culvert analysis of three rivers of initial focus
- Action Step: Work with partners to identify funding sources and priority planning for culvert improvement work
-
Strategic Action: Advocate for improvement or new installation of fishways at dams on initial targets Lamprey River (MaCallen 10mi, Wiswall 37mi, Wadleigh 121mi) and Exeter River (Town 53mi, Pickpocket 14mi)
- Action Step: Lobby for increased funding of NHFG and identify other sources for fishway improvements
Objective: TA2 PARASITES/PATHOGENS: Reduce levels of MSX/Dermo infection to <20% of standing stock for oysters by 2012
(comments)
Comment:
- NHEP: MSX 10-30%; Dermo 16-65% (2004); Partner with JEL<br />
- In conjunction with Freshwater Diversion objective<br />
- Policy needed: No current sanctuaries
-
Strategic Action: Support the continued breeding and restoration of disease-resistant oyster
-
Strategic Action: Ensure sufficient freshwater flows to knock back oyster diseases.
Objective: TA3 FRESHWATER DIVERSION: Maintain freshwater flows into the estuary from tributaries and groundwater at current levels
-
Strategic Action: Partner with NHEP/CLF to promote local WW treatment improvements rather than regional outfall pipe
-
Strategic Action: Promote enactment of new regulations and local ordinances that minimize large-scale freshwater withdrawals (>50,000 gal/day)
Objective: TA4 HARVEST: Manage annual harvest of oysters and diadromous fish at sustainable levels that do not diminish species viability (i.e. ~5% of standing stock)
(comments)
Comment:
- NHEP: 2700 bushels harvested in 1996 (last report); 15,800 bushels standing crop (17%)<br />
- NHEP: 4.3 – 5.6 fish/angler hour smelt harvested since 2000; NHFG: 72,000 river herring counted (down 60% in 2005); 1,700 harvested (Exeter); 29,000 average harvest
-
Strategic Action: Lobby for reduced oyster harvest limits to allow oysters to recover to sufficient coverage, density, and age class to achieve a self-sustaining status
-
Strategic Action: Analyze the extent to which harvest is impacting smelt, river herring, and winter flounder and develop strategies if necessary
Objective: TA5 INVASIVE SPECIES: Maintain estuarine extent of Phragmites at 2006 levels and avoid any new problem marine invasive species
(comments)
Comment:
- NHCP salt marsh monitoring program, WIMS program, and/or aerial photo analysis/remote sensing<br />
- Lobster shell disease; crabs; possibly marsh fungus dieback
-
Strategic Action: Employ remote sensing and on-the-ground surveys to track and respond to Phragmites expansion
-
Strategic Action: Support state, regional, and national climate change initiatives to mitigate potential sea surface temperature increases
-
Strategic Action: Support the marine invasives detection initiative (Census for Marine Life) through vigilance and outreach opportunities
Objective: TA6 EUTROPHICATION: Reduce nitrogen and phosphorus loading to 1998 levels
(comments)
Comment:
- NHEP: 59% increase in N past 25 yrs; Maximum of 63% of summer days with low DO at one site (2004) <br />
- Partner with county planning commissions; NHEP; NHDES; GB Silt Commission<br />
- NHEP: Upgrade to tertiary for all 18 GB WWTF would cost $150-200M and reduce nutrient levels by 15%
-
Strategic Action: Advocate for upgrades to Portsmouth and other 17 WWT facilities to tertiary by lobbying EPA/funders to require and support upgrades upon license renewals (15% nutrient reduction estimated)
- Action Step: Support CLF proposal to EPA for permit enforcement at Portsmouth and engage regional debate
- Action Step: Develop a long-term strategy for upgrades of all secondary WWTFs with outfalls into Great Bay
- Action Step: Support NHDES proposed designation of estuary as a federal Tier 1 waterway to trigger no-new loading regulations
- Action Step: Work with NHDES and NHEP to expand monitoring measures to better track nutrient trends
-
Strategic Action: Support regional planning and policy initiatives for smart-growth and improved storm-water management to filter nutrient inputs due to lawn chemicals, septic, and agricultural runoff
- Action Step: Advocate for implementation of advanced stormwater management as developed at UNH Stormwater Center
- Action Step: Work with regional planning commissions to get towns to adopt conservation overlay districts
-
Strategic Action: Improve town riparian buffer ordinances and encourage prime wetlands designation for surrounding towns
- Action Step: Work with NHEP to implement funding program for town prime wetland designations
- Action Step: Lobby for improvments to and enforcement of state Shoreline Protection Act
Objective: TA7 SEDIMENTATION: Maintain watershed impervious surface below 10% while controlling sources of runoff
(comments)
Comment:
- 11% of land in watershed protected (2006); 22% NHLCP acres protected (2006)<br />
- NHEP: 8% of watershed impervious<br />
- GBCoast Watch: transparency data; GoM CoastWatch: mussel data<br />
- GBERC: mean watershed habitat quality index 2.93
-
Strategic Action: Increase protection status of land in the Great Bay watershed to at least 15% and of land in the Conservation Focus Areas (as determined by the Land Conservation Plan for NH’s Coastal Watersheds) and to at least 25%
-
Strategic Action: Work with GB Silt Commission and regional planning boards to control development and expansion of impervious areas
-
Strategic Action: Support stormwater-control inititaves and outreach to reduce run-off deposition into the bay
Objective: TA8 SHORELINE DEVELOPMENT: Maintain XX% of shoreline and river bank buffers (100' and 300') as undeveloped/pervious and unarmoured
-
Strategic Action: Conduct GIS analysis to determine % of undeveloped 100' and 300' riparian shoreline along Great Bay rivers and tributaries
-
Strategic Action: Work with GBRPP and land protection community to increase shoreline buffer protection as much as possible
-
Strategic Action: Promote improved enforcement of shoreline protection regulations and more restrictive permitting to minimize construction and development in buffers
- Action Step: Attend public hearings and advocate for restrictive permitting
- Action Step: Work with GBRPP and parnters to identify and monitor new shoreline development
Objective: TA9 CLIMATE CHANGE: Ensure to the extent possible that marine targets have capacity to adapt to sea level rise through gradual habitat shifts
-
Strategic Action: Promote improved enforcement of shoreline protection regulations and more restrictive permitting to minimize construction and development in buffers
- Action Step: Attend public hearings and advocate for restrictive permitting
- Action Step: Work with GBRPP and parnters to identify and monitor new shoreline development
-
Strategic Action: Develop local sea level rise models that inform estuarine land managers, public policy makers, and the land protection community
- Action Step: Acquire latest SLR estimates (with regional adjustments if possible)
- Action Step: Acquire LIDAR data sets from NOAA and other federal sources
- Action Step: Work with land protection community to consider land targets that offer migration potential for coastal habitats
- Action Step: Develop GIS model of potential innundation sites to identify areas most at risk
-
Strategic Action: Advocate for NH’s adoption of Regional Greenhouse Gas Initiative, support NH "25 by 25" alternative energy initiative, and lobby for congressional action on a national climate/energy policy
- Action Step: Participate in alternative energy forums and planning meetings
- Action Step: Support lobby of national energy and climate policy
- Action Step: Work at state level to pass RGGI
Objective: TV1 SALT MARSH: Hydrologically restore 50 acres of salt marsh habitat by 2012
(comments)
Comment:
- GBERC: 279 acres restored since 2000; few large-scale opportunities remain
-
Strategic Action: Work with NHEP, NHCP, USFWS to target and restore lost marsh (Stubbs Pond, Newington, 40 ac; Squamscott Rd, Stratham, 15 ac)
- Action Step: Organize and launch the Great Bay Restoration Parternship
- Action Step: Develop an ambitious long-term vision and consensus plan for restoration target implementation
- Action Step: Identify public and private funding sources and develop proposals and legislative support
- Action Step: Acquire funds to build capacity and implement salt marsh restoration projects ($250K)
Objective: TV2 EELGRASS: Restore 25% of suitable eelgrass habitat (100 acres) and increase biomass of 70% of beds to high-density (1996 levels) by 2017
(comments)
Comment:
- NHEP: 12 acres restored since 1993<br />
- GBERC: <1000 acres lost but only 400 suitable acres identified<br />
- NHEP: Since 1990: maximum of 70% acres in high density classes (1996) ; 56% in 2003
-
Strategic Action: Build restoration partnership to develop shared vision, goals, and resources that enable large-scale restoration of historic oyster reefs and eelgrass beds in Great Bay and Little Bay
- Action Step: Organize and launch the Great Bay Restoration Partnership
- Action Step: Develop an ambitious long-term vision and consensus plan for restoration target implementation
- Action Step: Identify public and private funding sources and develop proposals and legislative support
- Action Step: Acquire funds to build capacity and implement eelgrass/oyster restoration projects (8 spawner reefs per $50K, 8 shell reefs per $100K = $1.2M; 100 ac eelgrass at $15K/ac =$1.5M)
-
Strategic Action: Where appropriate, integrate eelgrass restoration sites with oyster beds to improve eelgrass density and overall health
- Action Step: Review site selection models and use experts to identify physical sites
Objective: TV3: OYSTERS: Restore 25% of suitable oyster bed habitat (100 acres) through spawner sanctuaries and substrate deployment by 2012
(comments)
Comment:
- NHEP: 3.2 acres restored since 2000<br />
- GBERC: 800+ acres lost since 1970, analysis needed for suitable acres<br />
- JEL: $50K per acre of oyster reefs
-
Strategic Action: Build restoration partnership to develop shared vision, goals, and resources that enable large-scale restoration of historic oyster reefs and eelgrass beds in Great Bay and Little Bay
- Action Step: Organize and launch the Great Bay Restoration Partnership
- Action Step: Develop an ambitious long-term vision and consensus plan for restoration target implementation
- Action Step: Identify public and private funding sources and develop proposals and legislative support
- Action Step: Acquire funds to build capacity and implement eelgrass/oyster restoration projects (8 spawner reefs per $50K, 8 shell reefs per $100K = $1.2M; 100 ac eelgrass at $15K/ac =$1.5M)
-
Strategic Action: Investigate feasibility of oyster reefs coupled with existing/new WWTF outfalls for nutrient reductions, freshwater disease control, and spawn sanctuary protection
- Action Step: Review site selection models and use experts to identify physical sites
- Show all:
Percent Complete: 0%
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|
Percent Complete: 0%
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|
Comment: - NHEP: MSX 10-30%; Dermo 16-65% (2004); Partner with JEL
- In conjunction with Freshwater Diversion objective
- Policy needed: No current sanctuaries
-
Indicator: Number of oyster beds with > 5% Dermo infection(measurement report)Measurement Report:
Measure Date Source Trend Comments Dec 1, 2006 Not Specified
-
Indicator: Oyster disease index, 3 year mean (MSX)(measurement report)Measurement Report:
Measure Date Source Trend Comments Dec 1, 2006 Not Specified
Percent Complete: 0%
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|
-
Indicator: Deviation from historical mean flow (cubic feet/second) for selected sites
-
Indicator: NHEP and Coastwatch saltwater quality trends (2 year mean)(measurement report)Measurement Report:
Measure Date Source Trend Comments Dec 1, 2006 Not Specified
Percent Complete: 0%
![]() |
|
Comment: - NHEP: 2700 bushels harvested in 1996 (last report); 15,800 bushels standing crop (17%)
- NHEP: 4.3 – 5.6 fish/angler hour smelt harvested since 2000; NHFG: 72,000 river herring counted (down 60% in 2005); 1,700 harvested (Exeter); 29,000 average harvest
-
Indicator: # diadromous fish species present and viable(measurement report)Measurement Report:
Measure Date Source Trend Comments Aug 15, 2006 Not Specified
-
Indicator: NHF&G fish passage count data (3 year mean)(measurement report)Measurement Report:
Measure Date Source Trend Comments Target: Diadromous fish, Category: Size, KEA: Population size Feb 15, 2004 Not Specified Target: Shorebirds & Piscivorous birds, Category: Landscape Context, KEA: Prey resources Feb 15, 2004 Not Specified
-
Indicator: Number of juvenile fish successfully emigrating to estuary (NHFG seine survey trend)(measurement report)Measurement Report:
Measure Date Source Trend Comments Feb 15, 2004 Not Specified
-
Indicator: Oyster reef acreage
-
Indicator: Rainbow smelt egg deposition survey data (3 year mean)
-
Indicator: Recreational catch per unit effort (CPUE)(measurement report)Measurement Report:
Measure Date Source Trend Comments Dec 1, 2006 Not Specified Project Osprey (2004) and NHEP (2000)data indicates increasing trends for osprey and bald eagle.
Percent Complete: 0%
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|
Comment: - NHCP salt marsh monitoring program, WIMS program, and/or aerial photo analysis/remote sensing
- Lobster shell disease; crabs; possibly marsh fungus dieback
-
Indicator: % acreage with Ulva cover(measurement report)Measurement Report:
Measure Date Source Trend Comments Aug 15, 2006 Not Specified We really don't know. There are signs of degradation.
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Indicator: % of salt marsh acreage dominated by native salt marsh vegetation(measurement report)Measurement Report:
Measure Date Source Trend Comments Feb 15, 2004 Not Specified
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Indicator: Lobster disease index(measurement report)Measurement Report:
Measure Date Source Trend Comments Feb 15, 2004 Not Specified
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Indicator: Predator density. Green crab / Asian shore crab abundance index (CPUE)(measurement report)Measurement Report:
Measure Date Source Trend Comments Feb 15, 2004 Not Specified
Percent Complete: 0%
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Comment: - NHEP: 59% increase in N past 25 yrs; Maximum of 63% of summer days with low DO at one site (2004)
- Partner with county planning commissions; NHEP; NHDES; GB Silt Commission
- NHEP: Upgrade to tertiary for all 18 GB WWTF would cost $150-200M and reduce nutrient levels by 15%
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Indicator: Milligrams per litre of dissolved oxygen, mean value June-Sep(measurement report)Measurement Report:
Measure Date Source Trend Comments Jan 11, 2007 Not Specified Sporadic testing...confidence is low
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Indicator: NHEP and Coastwatch saltwater quality trends (2 year mean)(measurement report)Measurement Report:
Measure Date Source Trend Comments Dec 1, 2006 Not Specified
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Indicator: Plankton community survey data(measurement report)Measurement Report:
Measure Date Source Trend Comments Feb 15, 2004 Not Specified
Percent Complete: 0%
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Comment: - 11% of land in watershed protected (2006); 22% NHLCP acres protected (2006)
- NHEP: 8% of watershed impervious
- GBCoast Watch: transparency data; GoM CoastWatch: mussel data
- GBERC: mean watershed habitat quality index 2.93
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Indicator: Accretion rate (mm per year) relative to sea level rise(measurement report)Measurement Report:
Measure Date Source Trend Comments Feb 15, 2004 Not Specified
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Indicator: Average depth of deep water edges
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Indicator: GOMC Gulfwatch mussel bioassays (PAHs)(measurement report)Measurement Report:
Measure Date Source Trend Comments Target: Macro invertebrates, Category: Landscape Context, KEA: Water quality-toxics Feb 15, 2004 Not Specified Target: Tidal flat community, Category: Landscape Context, KEA: Water quality-toxics Feb 15, 2004 Not Specified
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Indicator: Mean annual incidence of low transparency (<1m @ hi. tide)(measurement report)Measurement Report:
Measure Date Source Trend Comments Jan 15, 2005 Not Specified Great Bay Coastwatch, 22 site survey with monthly samples. Confidence fairly good but some problems with survey - power may be low due to natural variablity
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Indicator: NHEP and Coastwatch saltwater quality trends (2 year mean)(measurement report)Measurement Report:
Measure Date Source Trend Comments Dec 1, 2006 Not Specified
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Indicator: Siltation rate at index stations(measurement report)Measurement Report:
Measure Date Source Trend Comments Feb 15, 2004 Not Specified More research needed here
Percent Complete: 0%
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Indicator: Percent natural buffer in 100 year sea level edge + 50 meters(measurement report)Measurement Report:
Measure Date Source Trend Comments Feb 15, 2004 Not Specified
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Indicator: Percent of upland edge not armored
Percent Complete: 0%
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-
Indicator: Accretion rate (mm per year) relative to sea level rise(measurement report)Measurement Report:
Measure Date Source Trend Comments Feb 15, 2004 Not Specified
-
Indicator: Percent natural buffer in 100 year sea level edge + 50 meters(measurement report)Measurement Report:
Measure Date Source Trend Comments Feb 15, 2004 Not Specified
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Indicator: Percent of upland edge not armored
Percent Complete: 0%
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Comment: - GBERC: 279 acres restored since 2000; few large-scale opportunities remain
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Indicator: % salt marsh receiving natural tidal flooding regime(measurement report)Measurement Report:
Measure Date Source Trend Comments Feb 15, 2004 Not Specified GRANIT layer, 2000. Confidence is high.
Percent Complete: 0%
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Comment: - NHEP: 12 acres restored since 1993
- GBERC: <1000 acres lost but only 400 suitable acres identified
- NHEP: Since 1990: maximum of 70% acres in high density classes (1996) ; 56% in 2003
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Indicator: Acres of healthy eelgrass meadows (5 year mean)(methods) (progress report)Methods:
- Aerial photography with GIS analysis
Progress Report:Progress Updated Comments Target: Eelgrass meadows; Threat: Parasites/pathogens Planned Target: Diadromous fish; Threat: WWT & Septic Planned Target: Eelgrass meadows; Threat: WWT & Septic Planned Target: Eelgrass meadows; Threat: Boating activities Planned Target: Eelgrass meadows; Threat: Dredging & marine construction Planned
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Indicator: Biomass metric tons (NHEP 5yr mean)(measurement report)Measurement Report:
Measure Date Source Trend Comments Dec 1, 2006 Not Specified
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Indicator: Seeds per bloom
Percent Complete: 0%
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Comment: - NHEP: 3.2 acres restored since 2000
- GBERC: 800+ acres lost since 1970, analysis needed for suitable acres
- JEL: $50K per acre of oyster reefs
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Indicator: Oyster reef acreage
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Indicator: Spatfall density at index sites
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Indicator: Spawning stock biomass (NOAA-GOM stock)(measurement report)Measurement Report:
Measure Date Source Trend Comments Feb 15, 2004 Not Specified
| Methods | Objectives | Key Indicator References by Target (w/Current Indicator Measurement) | Threat References by Target (w/Current Indicator Measurement) |
|---|---|---|---|
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Indicator: # diadromous fish species present and viable |
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Indicator: % acreage with Ulva cover |
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Indicator: % acres in >60% density classes (NHEP 5yr mean) |
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Indicator: % of miles of historic freshwater habitat currently accessible |
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Indicator: % of salt marsh acreage dominated by native salt marsh vegetation |
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Indicator: % salt marsh occurrences occupied by characteristic and ecologically significant animal species (mummichog & ribbed mussel) |
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Indicator: % salt marsh receiving natural tidal flooding regime |
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Indicator: Accretion rate (mm per year) relative to sea level rise |
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Indicator: Acres of eelgrass meadows (5 year mean) |
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Indicator: Acres of healthy eelgrass meadows (5 year mean) |
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Indicator: Acres of salt marsh |
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Indicator: Acres of tidal flats |
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Indicator: Annual bird survey results (3 year means / historic means) |
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Indicator: Average depth of deep water edges |
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Indicator: Average depth of deep water edges (@ mean low water) |
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Indicator: Benthic integrity index (EPA revised) |
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Indicator: Biomass metric tons (NHEP 5yr mean) |
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Indicator: Cumulative peak degree days at index sites |
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Indicator: Deviation from annual mean low flow (cubic feet/second) compared to natural range of variation in July-Sept |
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Indicator: Deviation from historical mean flow (cubic feet/second) for selected sites |
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Indicator: Diverse habitat types: high & low marsh, fringes, sinuous creeks, bare ground, pools & pannes. |
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Indicator: GOMC Gulfwatch mussel bioassays (PAHs) |
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Indicator: Healthy beaver populations |
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Indicator: Horseshoe crab survey trend (3 year mean / historic. mean) |
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Indicator: Level of epiphytic fouling & macro algae growing within eelgrass beds |
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Indicator: Live oyster reef acreage |
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Indicator: Lobster CPUE trend (3 year mean / historic. mean) |
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Indicator: Lobster disease index |
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Indicator: Mean annual incidence of low transparency (<1m @ hi. tide) |
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Indicator: Milligrams per litre of dissolved oxygen, mean value June-Sep |
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Indicator: Mussel tissue contamination level (lead, mercury, PCBs) |
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Indicator: NHEP and Coastwatch saltwater quality trends (2 year mean) |
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Indicator: NHEP freshwater (FW) & saltwater (SW) quality trends |
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Indicator: NHEP water quality trends |
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Indicator: NHF&G Survey data: % of catch > 10 cm |
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Indicator: NHF&G fish passage count data (3 year mean) |
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Indicator: Num. of consecutive days winter spawning bottom temp exceeds 10 C |
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Indicator: Number of YOY lobster and horseshoe crab (rolling 5-year mean) |
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Indicator: Number of juvenile fish successfully emigrating to estuary (NHFG seine survey trend) |
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Indicator: Number of osprey fledged per year (3 year mean) |
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Indicator: Number of oyster beds with > 5% Dermo infection |
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Indicator: Number of rivers free flowing or with optimal fish passage provided |
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Indicator: Number of successful research projects inititated with TNC assistance |
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Indicator: Oyster disease index, 3 year mean (MSX) |
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Indicator: Oyster reef acreage |
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Indicator: Percent natural buffer in 100 year sea level edge + 50 meters |
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Indicator: Percent of upland edge not armored |
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Indicator: Percent of upland edge not armored (natural shoreline) |
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Indicator: Plankton community survey data |
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Indicator: Population size for key fish species |
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Indicator: Predator density. Green crab / Asian shore crab abundance index (CPUE) |
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Indicator: Presence of viable populations of all native species (oyster, softshell clam, gem clam, razor clam, ribbed mussel, blue mussel) |
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Indicator: Prey density index |
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Indicator: Rainbow smelt egg deposition survey data (3 year mean) |
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Indicator: Rainbow smelt egg deposition survey data (NHFG, 3 year mean) |
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Indicator: Ratio of Spartina alterniflora (low) marsh to Spartina patens (high) marsh |
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Indicator: Ratio of high to low marsh |
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Indicator: Recreational catch per unit effort (CPUE) |
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Indicator: Seeds per bloom |
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Indicator: Siltation rate at index stations |
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Indicator: Soft shell clam biomass |
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Indicator: Spatfall at index sites |
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Indicator: Spatfall at index sites (rolling 5-year average) |
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Indicator: Spatfall density at index sites |
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Indicator: Spawning stock biomass (NOAA-GOM stock) |
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The CAP data pack, available for download using the download link below, has been modified. You will need to use CAP Excel Workbook version 6b
(or later) to import the CAP data pack. The data pack is an Excel 97/2003 formatted file with an extension of .xls. So, if you are using Excel 2007,
please remember to save all CAP files in the Excel 97-2003 Workbook format.
Help regarding this issue can be found in the CAP Workbook instructions and on ConserveOnline at:
http://conserveonline.org/workspaces/cbdgateway/cap/resources
- Download the latest CAP Excel Workbook.
- Download the ConPro Data Pack now!
Notes:
Help regarding this issue can be found in the CAP Workbook instructions and on ConserveOnline at:
http://conserveonline.org/workspaces/cbdgateway/cap/resources
- Download the latest CAP Excel Workbook.
- Download the ConPro Data Pack now!
Notes:
- It is always a good idea to use the latest CAP Excel workbook!
- You may see a "File Error: Data may have been lost" message when opening a Data Pack that was downloaded from ConPro. Please ignore this warning.
This work is licensed under a Creative Commons Attribution-Noncommercial-Share Alike 3.0 United States License

