Fal & Helford SAC features & BRUVS Flashcards

1
Q

conservation in the UK

A
  • coordination of national devolved governments for Scotland, Wales & Northern Ireland along with England in the UK is complicated
  • as such, conservation is structured around series of legislations upheld in each of those regions such as…
    -> Environmental Protection Act 1990
    -> Wildlife and Countryside Act 1981
  • 2 key public bodies advise governments across UK on these acts and conservation:
    -> The Joint Nature Conservation Committee (JNCC)
    -> The Forestry Commission
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2
Q

JNCC

A
  • guided by joint committee made up of heads of conservation bodies throughout UK
  • description of what they do…
    “coordinating nature conservation action at a UK level; working in partnerships to provide common approaches, shared solutions & best practice; & providing cost-effective & robust environmental evidence base across the UK”
  • monitor habitats & environments & also map them
  • of particular interest to this topic is their marine monitoring & mapping program
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3
Q

EMODnet from
JNCC

^marine monitoring & mapping program

A
  • high-quality European seabed mapping project that acts as portal for organisations to share data & interpolate it
  • interactive & downloadable maps give you broadscale data on seabed characteristics, bathymetry & biological features in some areas
  • coverage is patchy
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4
Q

Natural England

(not UK wide)

A
  • executive agency of English government concerned with nature & wildlife conservation, landscape protection
  • are responsible for protection & monitoring of terrestrial & marine habitats & their classification
  • also deliver large scale projects within international funding initiatives eg. ReMEDIES
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5
Q

Habitat Designations

(in Natural England)

A
  • to meet requirements of habitat legislations / acts & government priorities, NE (Natural England) will designate features of special interest (could include wildlife, landform or geology)
  • areas that are identified as having special features may be designated as a Site of Special Scientific Interest (SSSI) in the UK
  • these sites now also form basis of interconnected MPAs across UK
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6
Q

SSSI Assessment
Criteria / Considerations

A
  • typicalness (under-representation is favoured)
  • fragility (in structure or biology)
  • size (larger sites are likely to contain more species)
  • diversity (species richness)
  • naturalness (untouched sites are rare)
  • rarity (scarcity / threatened)
  • natural coherence (part of an interconnected network)

so large, non-typical sites are favoured

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7
Q

The Fal and Helford SAC

A
  • through identification of series of features, estuary was originally designated under EU habitats directive as Natura 2000 site & a Special Area of Conservation (SAC)
  • SAC designation affords one of highest levels of protection available & means its status is consistently monitored
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8
Q

SAC Site Features

A
  • Annex 1 features listed under EU Habitats Directive as sp / habitats that have special features
  • coded with 4-digit number (Natura 2000 code) & these are used on JNCC website & link to EUNIS (European Nature Information System) habitat classification maps
  • eg. 1110 Sandbanks which are slightly covered by sea water all the time
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9
Q

Site Features: Sandbanks
(Maerl & Seagrass)

A

1110 Sandbanks which are slightly covered by sea water all the time

  • important because => well-established & nationally important communities of Maerl & seagrass
  • shallow habitats -> so have low exposure => elongated rounded / irregular mound shapes, which are well suited to benthic communities that might grow on them (especially sediment types like Maerl & seagrass)
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10
Q

Site Features: Large Shallow Inlets & Bays

A

1160 Large Shallow Inlets * Bays - comprised of interdependent mosaic of subtidal & intertidal habitats

  • large indentations of coast, generally more sheltered from wave action than open coast
  • quite shallow (water < 30 m over most of area, & in contrast to 1130 estuaries, generally have much lower freshwater influence
  • in UK, 3 main sub-types can be identified that meet the Annex I definition …
  1. Embayment
    -> type of marine inlet where line of coast typically follows concave sweep between rocky headlands, sometimes with only narrow entrance to embayment
  2. Fjardic sea loch
    -> series of shallow basins connected to sea via shallow (sometimes intertidal) sills.
    -> found in areas of low-lying ground which have been subject to glacial scouring
    -> have highly irregular outline, no main channel & lack high relief & U-shaped cross-section of fjordic sea lochs
  3. Ria
    -> drowned river valley in area of high relief, most have resulted from post-glacial rise in relative sea level
    -> in Scotland this sub-type is called a voe
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11
Q

Site Features: Atlantic Salt Meadows

(basically saltmarsh)

A

1330 Atlantic salt meadows (Glauco-Puccinellietalia maritimae)

  • develop when halophytic vegetation colonises soft intertidal sediments of mud & sand in areas protected from strong wave action
  • this vegetation forms middle & upper reaches of saltmarshes, where tidal inundation still occurs but with ↓ freq & duration
  • wide range of community types represented & saltmarshes can cover large areas, especially where there’s little / no enclosure on landward side
  • vegetation varies with climate & freq & duration of tidal inundation
  • grazing by domestic livestock is particularly significant in determining structure & sp composition of habitat type & in determining its relative value for plants, invertebrates & wintering / breeding waterfowl
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12
Q

SAC features

overview

A
  • framework for identifying & classifying special features of site in UK have been borne out of consultation with scientists & conservation strategies
  • written into law through legislations & acts in UK
  • Fal & Helford estuary is designated as key conservation area because it has several eg.s of nationally rare, outstanding quality habitats eg. seagrass, maerl, mudflats & salt marsh
  • ^these classed as Annex 1 habitats & focus long-term monitoring & conservation efforts
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13
Q

BRUVS

A
  • Baited Remote Underwater Video Systems
  • non-invasive method for collecting ecological data relating to mobile sp
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14
Q

BRUV deployment in the Azores

A

calc ecological metrics –
relative / MaxN (no. of individs)

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15
Q

application of BRUVS

A
  1. review of BRUVs application globally
  2. spatial distribution of pelagic predators
  3. recovery of UK seabed after MPA designation
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16
Q

adv of BRUVS

A
  • low impacts methods (compared to scientific fishing surveys)
  • remote nature helps reveal cryptic sp
    -> usually scared by dive/snorkel surveys
  • low cost & low risk -> cheaper & safer than dive surveys
17
Q

limitations of BRUVS

A
  • relative abundance not true abundance -> likely underestimate
  • biased toward certain sp -> scavengers & predators more common in data
  • uncertainties over area of influence -> bait plume varies on size of tide etc.
18
Q

habitat assessments

A
  • Rocky Reef (most complex, deepest)
    -> Bed Rock & its associated macroalgae, wide depth range & med-high exposure
  • Seagrass Meadow
    -> Subtidal seagrass growing on sediment, shallow with med-low exposure
  • Sand (least complex, deepest)
    -> Bare sand/sediment, all exposures & widerange of depth