Habitat Management Flashcards

1
Q

What is reference number 1

A

Sutherland, W. and Hill, D. (1995). Managing habitats for conservation. Cambridge: Cambridge university press

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2
Q

what are the differences in flowing and static waters

A

water movement - if waters are moving so are other things, oxygen movement, organism movement, one way movement in rivers whereas static waters are more surface movement and mixing but not directional, impact on sediment water movement,

open (in out) system vs closed system - if you get pollutents, nutrients and organisms they tend to build up in the system vs flowing water

differences in management - speeding up ecological succession static need a lot of management, flowing open systems arrive and leave again meaning little management as theres no build ups, ecological succession is taking place but its not speeding it up in the same way as static water

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3
Q

what are the origins of waters

A

flowing - tend to be natural but modified by man in some way elgl the thames river

static - tend to be un natural, few natural static waters e.g. lochs in scotland because theyre large and have gone through ecological succession very slowly and uplands but lowlands are man made. natural lowland static waters dried up and turned into woodlands (gone through ecological succession)

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4
Q

what are the differences in flowing and static waters

A

water movement - if waters are moving so are other things, oxygen movement, organism movement, one way movement in rivers whereas static waters are more surface movement and mixing but not directional, impact on sediment water movement,

open (in out) system vs closed system - if you get pollutents, nutrients and organisms they tend to build up in the system vs flowing water

differences in management - speeding up ecological succession static need a lot of management, flowing open systems arrive and leave again meaning little management as theres no build ups, ecological succession is taking place but its not speeding it up in the same way as static water, pollutants act as nutrients for algae resuting in eutrophicaion

think about water flow relative to its size - a small trickle wont move much compared to a river

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5
Q

what are the wildlife values/benefits/needs of water

A

habitat - wading birds, water voles, fish, inverts, plants

water source

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6
Q

what are the methods of control for waterbodies

A

cut, spray, dredge or rake

say which is best for each situation a thats where the marks are

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7
Q

in waterbodies what determines plant growth?

A

abundance of dissolved nitrogen and phosphorus levels , nitrogen is rarely inadequate for plant growth but phosphorus can be limiting

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8
Q

are eutrophic waterbodies natural?

A

most are man made and include reservoirs, lakes and ponds.

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9
Q

what type of management do lowland STANDING waterbodies benefit most from?

A

active recreation: there is often considerable potential to modify habitats to benefit scarcer species and minimise impact of human disturbance but integration of this with other uses needs careful planning.

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10
Q

advantages of phase 1 habitat survey over nvc

A
  • quicker to do
  • requires less specialist botanical knowledge
  • NVC is much slower as its more indepth and requires multiple visits over the year as diff plants grow in diff seasons
  • phase 1 is widely used by ecologists and clients as its quick and cheap
  • useful for coded maps
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11
Q

disadvantages of phase 1

A
  • not very advanced

- wont learn all there is to know about the flora of a site as you only make one visit in one season

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12
Q

what are the 8 factors for static water management

A

Six natural:

Geography (location, topography and geology)
Quantity of water 
Quality of water
Depth of water
Waves
Context

Two man-made:
Pollution
Disturbance

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13
Q

what is reference number 2?

A

Lake, S. (2014). Britain’s Habitats: A Guide to the Wildlife Habitats of Britain and Ireland. 1st ed. Princeton University Press.

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14
Q

what is dystrophic static water

A

Dystrophic: describes a pond or lake containing unusually acidic brown water, lacking in oxygen, and unable to support much plant or animal life because of an excessive humus content

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15
Q

define heathland

A

an area of open uncultivated land, typically on acid sandy soil, with characteristic vegetation of heather, gorse, and coarse grasses.

Dominated by under-shrubs (0.5m)
On nutrient-poor soils
On acidic soils
Mostly heather - Calluna vulgaris 
Plus:
Erica, Vaccinium and Ulex species
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16
Q

causes of heathland losses

A

Lowland heaths:

Abandoned
Succession to woodlands
Forestry

Upland heaths:

Overgrazing
Conversion to grassland
Forestry

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17
Q

what is the conservation value of lowland heaths

A

Lowland heaths:

Vegetation type

Plant species

Reptiles and amphibians - sand lizards

Birds

Insects

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18
Q

conservation value of upland heaths

A

Upland heaths:

Vegetation type

Birds - red and black grouse, hen harriers

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19
Q

describe 4 stages of heather life cycle

A

Heather - Major heathland structural plant

Each plant has four life phases:

Pioneer (3-10yrs); seedling
Building (7-13yrs); dense dome
Mature (12-30yrs); centre opens
Degenerate (>30yrs); collapse

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20
Q

significance on conservation of heather lifecycle in heath?

A

Significance:

Height and vigour influence other species

So phases important in management

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21
Q

main problems of heath management

A

Emphasis now mostly on heather

Four major problems:

  1. Natural succession:

Under grazing; woody plants and/or bracken invade

Mostly lowlands

  1. Nutrient build up:

Natural
Fertilizers
Acid rain

  1. Over grazing:

Grassland, mostly uplands
Magic number, 2 ewes/ha in winter

  1. Fragmentation:

Housing, roads etc.
Mostly lowlands & animals

Problems compounded by interactions:

Fragmentation by other problems
Nutrients cause succession
Over and under grazing

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22
Q

causes of heathland losses

A

Lowland heaths:

Abandoned
Succession to woodlands
Forestry

Upland heaths:

Overgrazing
Conversion to grassland
Forestry

Lowland heaths:

Problems: Under-grazing and fragmentation
Solution: Cutting and restoration

Upland heaths:

Problem: Over-grazing
Solution: Economic and political issues

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23
Q

describe 4 methods of enhancement techniques for heathland problems:

bracken, nutrient depletion, overgrazing,

A

Bracken control:

Deep rhizomes are a problem
Mechanical or chemical control
Mechanical: repeated cutting or rolling
Chemical: Asulam
Both, best in the early summer
Both, expensive and temporary

Nutrient depletion:

Mow and remove (or burn) but this is slow
And fires cause enrichment
Better to remove top of soil
But there is a problem with disposal

Over-grazing:

Remove stock 
But economics
Supplementary winter feed
But adds nutrients
Trampling and/or grazing hot spots
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24
Q

describe three maintenance methods for heathland

A
  1. Grazing:
Traditional
Best, produces a mosaic
But lowlands no stock
And uplands too many
Best 2 ewes/ha in winter
N.B. Sheep eat heather in winter
  1. Muir burning:

Traditional to the uplands
Removes old wood and encourages new shoots
Mixed small patches suitable for grouse
Short for feeding and tall for hiding
Can replace grazing in lowlands but uniform

  1. Cutting:

Not traditional
Can replace grazing in lowlands
Safer, but produces cuttings
Need to remove cuttings

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25
Q

main problems of heath management

A

Emphasis now mostly on heather

Four major problems:

  1. Natural succession:

Under grazing; woody plants and/or bracken invade

Mostly lowlands

  1. Nutrient build up:

Natural
Fertilizers
Acid rain

  1. Over grazing:

Grassland, mostly uplands
Magic number, 2 ewes/ha in winter

  1. Fragmentation:

Housing, roads etc.
Mostly lowlands & animals

Problems compounded by interactions:

Fragmentation by other problems
Nutrients cause succession
Over and under grazing

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26
Q

define a mire

A

Mires (bogs and fens) are herbaceous, terrestrial ecosystems

The soils are organic and water-logged

The water level is at the soil surface

Reed beds (fens) – considered here too

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27
Q

what is the origin of the soil for mires

A

In a mire, the plant communities form the peat, the soil in which they grow.

Peat accumulates at a rate of about one millimetre a year.

Origin of the organic soil:

Peat substrate

Water-logged

Anaerobic environment

Litter does not decay

Litter accumulates

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28
Q

what are the two major types of mires?

A
  1. Bogs:

Ombrotrophic - ‘rain fed’
pH 4
Nutrient poor
Sphagnum mosses, sedges and heaths

  1. Fen:

Minerotrophic – ‘ground water fed’
pH 5 – pH7
Nutrient richer
Tall grasses, sedges and rushes

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29
Q

what are the two main types of bogs?

A

Two main types:

Raised bogs:
Shallow domes on flat land or basins

Blanket bogs:
Sheets on gentle slopes (10o) (and valley bogs)

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30
Q

what are the stages of succession in mires

A

Stages of succession:

Open water, to…
Reed beds (swamp), to…
Fen, to…
\+/- Fen woodland (= Carr), to finally…
Bog

Significance of succession:

Fens; short-lived so require much management

Bogs; long-lived so require little management

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31
Q

what is the wildlife importance of fens and bogs

A

General wildlife interest
Natural and semi-natural habitats

Fens and reed beds:
Rare birds and invertebrates

Bogs:
Area of habitat
Plus some species

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32
Q

name some animals that live in bogs

A

The Raft Spider is one of the largest, and scarcest spiders in Britain.

It inhabits pools on bogs and wet heaths, where it skates across the surface.

If disturbed it breaks the water surface and dives.

golden plover bird, bog bush cricket, common crane (fens)

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33
Q

name some animals that live in bogs

A

The Raft Spider is one of the largest, and scarcest spiders in Britain.

It inhabits pools on bogs and wet heaths, where it skates across the surface.

If disturbed it breaks the water surface and dives.

golden plover bird, bog bush cricket, common crane (fens), bitterns, marsh harrier (fens), marsh orchids

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34
Q

what are the general management techniques for bogs/mires

A

General:

General problems and solutions
Modified by site and / or rare species
Maintain / enhance mostly
Little restoration
Remember variety
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35
Q

what is the difference between bogs mires and fens?

A

reedbed, fen and acid bog habitats are generally part of the succession from open water to woodland

differences between them being due to water chemistry, hydrology, geology and climate

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36
Q

what is the method of management for conservation for mires and fens

A

focuses on the early successional stages with aims to halt or slow succession because lack of management of fens and reedbeds has led to succession and as a result lots of woodlands have sprung up with only small areas of open vegetative communities remaining.

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37
Q

what is the management method for bogs?

A

bogs are generally stable and only require low levels of management or even none at all but they are threatened by peat extraction, drainage and invasion or afforestation by exotic conifers.

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38
Q

define a bog

A

characterised by short vegetation particularly sphagna bt including mosses, sedges and dwarf shrubs. other vegetation inc trees is always due to disturbance e.g. from drainage.

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39
Q

give an example of how drainage can cause problems for raised bogs

A

drainage of the lagg will have an effect on the hydrology of the dome which leads to the sphagnam covered surface drying faster and the eventual colonisation by trees, pools and ridges

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40
Q

how are blanket bogs formed

A

they smother large areas of level or gently sloping ground under a ‘blanket’ of peat. Also known as ‘flow’ or ‘floe’, they are the most extensive type of mire fed entirely by rainfall and snowmelt rather than groundwater.
refers to ombrotrophic mires
true blanket mire peat can form directly on acid nutrient poor podsols and even over bare leeched rock.

the depths of the peat depends on waterlogging and stagnation reaching up to several metres deep.

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41
Q

are blanket bogs natural

A

yes but there are some evidence of man made ones as iron age agriculture may have contributed to the development of blanket peat

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42
Q

what are the problems with blanket bogs?

A

Peat is a precious resource that can take thousands of years to form and peat bogs are important habitats for a whole range of species from bog bush-crickets to hen harriers. However, our peat bogs have been overexploited by the commercial extraction of peat, particularly for horticulture, and have been irreparably damaged by drainage, afforestation and inappropriate management.

Peat is still growing on some active bogs, but the rate of formation is greatly exceeded by the rate of loss. Poorly managed grazing, intensive burning and acid rain all cause erosion, while peat-cutting exposes the underlying bedrock. The subsequent loss of sponge-like blanket bog causes flash flooding and erosion downstream.

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43
Q

how does drainage negatively affect mires and bogs

A

Drainage ditches, l lower the water table
may initiate erosion and oxidation of the peat.

Lowered water tables will alter the species composition of the surface vegetation and have a detrimental affect on specialist invertebrates.

Drainage at the margins of bogs will lower the water table and may modify the surface patterning, such as loss of Sphagnum hollows.

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44
Q

how will afforestation negatively affect mires and bogs

A

Coniferous trees have been planted on extensive areas of blanket bog in the past. The trees will continue to affect the hydrology and species composition of adjacent areas of blanket mire as they mature and require more water. Afforestation has generally been accompanied by furrowing of the ground, and these highly destructive drainage channels become a long-lasting scar.

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45
Q

give more specific details of management techniques for bogs/mires (hydrology)

A

As a peat bog consists of 95-98% water held by Sphagnum peat, the water level is the most crucial aspect to consider when managing this Priority habitat type. Operations some distance away from the ombrotrophic Sphagnum communities can have a devastating effect if they are on sites within the same hydrological unit.
Drainage ditches and forestry plantations will remove water from surface layers of the bog and ultimately lower the bog surface, favouring plants which grow in drier conditions, affecting any specialist invertebrate species.

Wet blanket bog is of great importance to many invertebrates such as spiders and leaf-hopper bugs. Drying peat will shrink and oxidise, creating erosion problems and increasing vulnerability to fire damage, so it is essential to maintain water levels. On sites that are drying, raising the water levels should be considered. -

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46
Q

why is the burning management technique bad for blanket bogs

A

Burning destroys large numbers of invertebrates, potentially entire populations of species living wholly in the above-ground parts of plants. In acid sites it can also encourage purple moor-grass at the expense of other vegetation. Too hot a burn can kill bog-moss and burn into the peat, altering plant communities and damaging invertebrate interest.
Heather management through burning appears to be especially damaging to plant-hopper bugs, sensitive species taking a long time to return. Burning should be therefore replaced with a more sympathetic form of management such as cutting or low-level grazing.

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47
Q

why is nutrient enrichment management bad for blanket bogs

A

Pollution incidents and nutrient enrichment lead to the loss of Sphagnum bog vegetation reducing its ability to support species such as the rare Wybunbury Moss carol-rita spider Carorita limnaea.

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48
Q

give another specific example of blanket bog management

A

prevent growth of scrub and trees

If water table levels are maintained then significant scrub invasion should not present a major problem as the very wet, infertile ground conditions, altitude and exposure of the blanket bogs often makes tree or shrub growth difficult. However, in areas of bog that have already begun to dry as a result of drainage or agricultural operations, scrub invasion can be prevented by cutting or light grazing, but it is important not to overgraze. Grazing can cause problems to blanket bog habitats, causing damage to the vegetation by trampling and affecting the species composition if nutrient enrichment occurs by the deposition of dung

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49
Q

what are the main problems of raised bogs

A

• Peat extraction
Removal of peat in existing and proposed new areas
• Landfill development
Use of cut-over bogs for landfill
• Afforestation
Trees (and associated furrows) dry out neighbouring areas and act as an invasive seed source.
• Drainage
Neighbouring agricultural areas require lowered water levels via marginal ring-ditches and other intrusive drainage measures. Drying out the raised bog through drainage allows invasion by scrub and trees which it turn speed up the drying out process and lead to the loss of special habitat and fauna.
• Water abstraction
Abstraction of water within the catchment area will have an adverse effect on the hydrology of a raised bog.
• Pollution
Run-off from agricultural land (fertilisers and pesticides) will damage the ecology of the bog.
• Livestock & game management
Drainage, trampling, burning, contamination with feed and droppings
• Built development (roads etc)
Apart from direct impact, the natural hydrology is disrupted
• Climate change
- See more at: https://www.buglife.org.uk/advice-and-publications/advice-on-managing-bap-habitats/lowland-raised-bogs#sthash.olkkqB3z.dpuf

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50
Q

what are the same management techniques for both types of bogs?

A

hydrology, prevent scrub encroachment, avoid burning and avoid grazing

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51
Q

name a specific management technique for raised bogs

A

Relatively undisturbed lowland raised bog surfaces are not uniform; they are made up of an almost continuous carpet of Sphagnum with a microtopography of hummocks and hollows providing a range of conditions that support invertebrates. It is important to minimise human activity on undisturbed raised bogs; wet Sphagnum communities are fragile and easily damaged by trampling.
Shallow bog pools should never be deepened or cleared, as their invertebrate interest is likely to be far greater than any larger pool that is created.

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52
Q

what are the main threats/problems for fen

A

Drainage for conversion to intensive agriculture
Past drainage of surrounding areas of land has lowered water tables and led to drying of remnant fen habitats

Water abstraction
Excessive water abstraction from aquifers dries up or reduces spring line flows, lowers water tables and affects water quality
Nutrient enrichment
Nutrients from agricultural run-off and other sources leads to eutrophication of fen waters and a change in plant communities
Afforestation
Afforestation within the catchment areas can lead to drying
Poor management
Lack of appropriate management to prevent drying, deterioration in herb richness, scrub encroachment and succession to woodland

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53
Q

what are the management techniques for fen

A

maintain structural diversity - all succession stages of fen provide important invertebrate habitats and should be retained where these occur naturally. Management should be carried out in rotation to ensure both longer and shorter vegetation is present at all times.

prevent scrub encroachment

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54
Q

what are the management techniques for fen

A

maintain structural diversity - all succession stages of fen provide important invertebrate habitats and should be retained where these occur naturally. Management should be carried out in rotation to ensure both longer and shorter vegetation is present at all times.

prevent scrub encroachment

retain areas of carr (wet woodland) which is important for wildlife and is species rich

maintain water levels to keep invertebrate habitats intact

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55
Q

what is the wildlife importance of reedbeds?

A

important for birds - 5 nationally scarce birds bittern, bearded tit, marsh harrier, cettis warbler and savis warbler breed in reedbeds.

reedbeds are also important pre migratory roost sites for hirundines and winter roosts for pied wagtails.

watervoles use them

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56
Q

management for reedbeds?

A

Scrub removal
Scrub encroachment should be discouraged over most of the area, but in some small areas scrub should be retained. The best method of removal is to pull out bushes, leaving small pools within the reed bed, which can support interesting invertebrates. Simply cutting scrub will have the effect of promoting thicker re-growth from stumps and may lead to an ever-increasing need for cutting.

hydrology: three diff techniques
- water maintained high all year
- water above ground level until after birding season, dropped to below ground level then raised again in autumn
- water held above ground in summer, dropped over autumn and raised in spring

depends on wildlife, 1 is good for animals that need wet conditions (bitterns), 2&3 allow scrub encroachment and drying of litter which is better for other birds

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57
Q

threats to reedbeds

A

• Loss of area
Large areas of reedbed can be lost by water abstraction, land drainage and conversion to intensive agriculture
• Lack of appropriate management
This can include too frequent harvesting/cutting cycle, of existing reedbeds leading to drying, scrub encroachment and succession to woodland
• Sea-level rise
Rising sea levels on the East coast of England are expected to lead to the loss of significant areas of habitat
• Pollution
Pollution of freshwater supplies to the reedbed

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58
Q

why is fen management different to reed management

A

same management can be used but fens have more complicated systems than reedbeds as they have a higher diversity of plant and animal species so messing with the hydrology will have more effect on the conditions plants and animals can survive in

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59
Q

what are the similarities and differences in management between fens reedbeds and bogs?

A

Fens and reed beds:
Constant management
Keep all stages of succession

Bogs:
Minimal management if undisturbed
If not, block drains and remove trees

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60
Q

what is fragmentation caused by and its severity depends on?

A

Caused mostly by agriculture

Severity depends on the size of fragments

Severity depends on the degree isolation

Severity depends on the difference in the habitats between fragments and landscape

61
Q

what are the negative effects of fragmentation?

A

reduced geneflow between populations (genetic isolation) due to large gaps of hostile habitats,barriers to movement (roads,cities etc in the way of animals), pollution, loss of food availability
Four main problems:

Edge effects
Penetration
Barriers
Small population sizes (allopatric speciation)
Restricted foraging
No annual migration
No new colonization
Inability to shift range
62
Q

how to wildlife corridors help to improve biodiversity

A

Refers mostly now to ‘true’ habitat corridors
Can help reduce inbreeding depression
Can help increase genetic variation

Potential value:
Increased foraging areas
Increased interbreeding
Annual migrations
Colonization of new areas and enhances range shifts
63
Q

what is the management for lowland heath

A

Maintain a diverse vegetational structure - important for range of habitats for inverts
Grazing is the preferred management option for maintaining a mosaic of heathland structure - keeps areas of bare ground for inverts, scattered shrubs (various stages of succession), grassland in tussocks,
he grazing habits of cattle tend to produce a more varied vegetation structure than that in sheep-grazed areas and their greater weight will suppress bracken growth and provide areas of disturbed ground. However, ungrazed areas of mature heather should be fenced off to avoid damage.

64
Q

wht is continuous grazing

A

Continuous grazing is when cattle graze a pasture for an extended amount of time with no, or infrequent rest to the plants from grazing.

65
Q

what are the advantages of continuous grazing?

A

dvantages of this method are low fencing cost, low daily management requirements, and when stocking rate is correct, acceptable animal gains. This method is most effective where forage availability is plentiful and the manager does not wish to increase livestock numbers.

66
Q

what are the disavantages of continuous grazing

A

difficulty in controlling the timing and intensity of grazing. Another limitation of this system is during slow forage growth periods animal numbers need to be adjusted, or more acreage available for grazing. Continually grazing a pasture with too many animals will lead to reduced forage availability and quality and animal growth.

A continually grazed pasture will take longer to recover after a drought than a pasture that has been rested because the plants are more stressed. Another disadvantage to continuous grazing is the limited number of forages that can withstand the grazing pressure.

67
Q

what is rotational grazing

A

system where a large pasture is divided into smaller paddocks allowing livestock to be moved from one paddock to the other easily. Using this method cattle are concentrated on a smaller area of the pasture for a few days then moved to another section of pasture.

68
Q

advantages of rotational grazing

A

allows the grazed paddock a rest period that permits forages to initiate regrowth, renew carbohydrate stores, and improve yield and persistency. When utilized properly, rotational grazing can help farmers increase forage productivity. Rotational grazing can help improve productivity, weight gain or milk production per acre, and overall net return to the farm. Rotational grazing allows for better manure distribution that acts as a source of nutrients to the soil. Rotational grazing also has the potential to reduce machinery cost, fuel, supplemental feeding and the amount of forage wasted.

69
Q

disadvantages of rotational grazing

A

the need for more fence to be constructed, time required to move cattle, and the need to have water and access to shade from each smaller paddock. The use of temporary fence is an inexpensive way to divide fields into the smaller paddocks and can be moved based upon the producers’ preference

70
Q

best method of management for low heathland?

A

Grazing is the preferred management option for maintaining a mosaic of heathland structure

71
Q

what is a bad method of management for lowland heath?

A

Burning on lowland heathland is a less favourable method of management than low intensity grazing combined with rotational cutting and scraping of the soil surface to create exposures. The latter form of management will be beneficial to most invertebrate species and a more heterogeneous habitat can be created. However, on larger heathlands burning can be the most effective form of management, especially when combined with grazing. On dry heath one of the advantages of fire, if it is hot enough for a deep burn, is that it burns away the humus layer that builds up under heather, thus exposing the mineral soil that is essential to many heathland invertebrates. Mowing will not achieve this.

72
Q

what are the threats to static and flowing waterbodies?

A

Static, flowing and man-made waters:

  1. Water abstraction
  2. Climate change
  3. Pollution (including eutrophication)
  4. Development
  5. Recreation

Static only:
6. Sediments: natural

73
Q

what is the general management of flowing waterbodies

A

Management in general:

Head waters, lower reaches small rivers; minimum of management

Lower reaches of larger rivers managed for things other than wildlife

By five main techniques

Some more wildlife friendly than others

74
Q

what are the main five management techniques for flowing waters

A

. Water flow

  1. Pollution
  2. Weed control
  3. Bank vegetation
  4. Dredging
75
Q

how to manage waterflow in flowing waterbodies?

A

Problem:
Abstraction from rivers and ground

Solutions:
Alternative sources
Balancing reservoirs
e.g. River Derwent and Carsington Water

76
Q

how to manage pollution in flowing waterbodies?

A

Sources and problems:
Plant nutrients; sewage and agrochemicals; eutrophication
Poisons; sewage and industry; death of river

Solutions:
Clean discharges; time and place of application of agrochemicals

77
Q

what is the conservation value of weeds? what are the problems and methods of control for weeds in flowing water management

A

Conservation value:
Food; cover; breeding sites

Problems:
Restricts water movement and fishing

Methods of control:
Cut, spray, dredge or rake weeds

Control regimes:
All is bad; gradual is good

78
Q

what is the conservation value of bank vegetation? what are the problems and methods of control for bank vegetation in flowing water management

A
Conservation value:
Food; shelter and shade
Problems:
Access; water flow; burrowers
Methods of control:
Mow or graze; prune
Control regimes:
Uniformity is bad; variety is good
79
Q

what is the conservation value of not dredging? what are the problems and methods of control for dredging in flowing water management

A

Introduction:
Removes bed material to improve access or flow; straightening

Problem for wildlife:
Simplification; damages banks

Dredging regimes:
Straight; uniformity is bad
Sinuous; variety is good

80
Q

how do you manage flowing water with and without other management?

A

Where no other management:
Minimum of intervention if clean

Where other management:
Manage sympathetically

81
Q

what is the difference between upland and lowland standing water bodies?

A

Lowland water bodies:
Man-made, polluted and small size
Mesotrophic to eutrophic

Upland water bodies:
Natural, clean and large size
Oligotrophic to mesotrophic

82
Q

what is the management for water quality in static waterbodies?

A

Means of management: overgrown ponds

Control nutrient input:
Recharge time and reed beds
Limit fertilizer application

Remove nutrients from water:
Barley straw

Remove sediments:
Dredge or pump in winter
Remove biomass in summer

83
Q

why is water depth a problem for static waterbodies

A

Effect:

Different species need different depths

Problem:

Natural shallowing

84
Q

what is the management for waterdepth in static waterbodies

A

Solutions:
Dredging
Raking
Sluices

Annual fluctuations:
Occur
Good for amphibians

85
Q

what are the problems waves cause in static waterbodies?

A

Source:
Wave size depends on wind
Wave size depends on fetch

Problems:
Turbidity
Erosion

86
Q

what is the management for waves in static waterbodies

A

Solutions:

Hard banks; but poor for wildlife

Geotextiles; reefs 2m from the shore

Shelterbelts: Height and width

But trees causes shading

87
Q

what is the probem fishing and general disturbance causes in static waterbodies?

A

Source:
Fishing, sailing, bird watching, etc.

Problems:
Movement, noise, wash, chopping, etc.

Presence of people:
Can be beneficial

Solution zoning

88
Q

what is the management technique for disturbance in static waterbodies

A

zoning - splitting a lake or large static waterbody into no fishing sections and fishing sections allows some areas of recovery

89
Q

why is scrub management important for grasslands?

A

almost all grasslands in the uk are dependant on processes that prevent the succession to scrub and woodland as these outcompete them and create shaded areas of light.

90
Q

how are grasslands classified?

A
(A) Functional classification:
Meadows (hay) and pastures
Pastures into rough grazing and enclosed pastures
N.B. Wet grasslands:
Some meadows and enclosed pastures
For birds

(B) floralistic

acidic, mesotrophic and calcareous

by agriculture

semi improved, improved, unimproved

Two classification systems - (A) and (B):

91
Q

what is acidic grassland

A

develop on nutrient poor sooils of low ph and less rich in plant species than mesotrophic and calcaerous

widespread in the uplands forming the bulk of rough grazing land

in the lowlands there are more species rich acid grasslands occurring on sandy and gravelly soils associated with heathland

92
Q

what is a mesotrophic grassland?

A

soils that arent too acidic or alkaline, mainly occur on clay soils

93
Q

what is a grassland

A

Historically, not sown; so semi-natural
But in the last 100 years most improved (including sowing); so increasingly artificial
Now only natural and semi-natural grasslands
Wildlife value:
All; plants and invertebrates
Wet; birds, particularly waders

94
Q

where are you likely to find each type of grassland

A

Acidic and calcareous grasslands
Rough grazings in the uplands

Mesotrophic grasslands
Meadows, enclosed pastures and wet grasslands

95
Q

what are the major problems of mesotrophic grasslands

A
Major problem (wildlife grasslands):
Succession: coarse grass to scrub

Major problem (farmed grasslands):
Improvement: fertilizers, etc.
Many grasslands have few species

Minor problems:
Water levels
Weeds

96
Q

what are the general management techniques for grasslands?

A

grazing - grazing is a gradual form of vegetation removal - rotational vs continual, type of grazing animal

cutting - sudden and large removal of vegetation, can destroy habitats, creats a uniform short grassy area, causes soil compaction from heavy machinery. can avoid killing birds by cutting fields from the inside out

burning - sudden process, destructive, leaves bare patches, risks wildlife and inverts, only acceptable use of burning is to remove impalatable plants to livestock and remove invasive species such as japanese knotweed.

97
Q

why does animal type affect grazing as a management method?

A

diff animals have diff grazing behaviour and selectivity, grazing animals also differ in their distribution of dung and trampling intensity, also there is differences in stocking intensity which can be detrimental to ground dwelling/nesting birds,

sheep: sheep cut vegetation close to the ground and can easily lead to over or undergrazing as they dislike coarse herbage. theyre unsuitable for restorative management but cause little trampling. unsuitable for wet grassland as theyre more susceptible to disease than cattle, during the day sheep drop dung everywhere but at night they congregate on areas of short sward.
cattle: cattle wrap they tongues and cut the grass but cant cut close to the ground like sheep can, they eat taller herbage than sheep, this makes them useful for restorative management as theirfeeding technique can open up small bare areas and destroy sucessive plants. however cattle are selective (wont eat tor grass) and are heavy tramplers which means their grazing is patchy which is good for inverts. higher densities of cattle produces a more even area of grass. cattle leave pats everywhere but wont feed near them which leads to more patchiness
horses: selective grazers, capable of eliminating a particular species from a site so shouldnt be used on areas of high botanical interest, trampling is intermediate between sheep and cattle, they graze patchily leaving areas of short and tall swards which can create lots of diversity in areas of low botanical interest. conditions are poor for inverts

mixed grazing has a danger of creating a species poor uniform area of short swards poor for plants and inverts

98
Q

what are the general management techniques for grasslands?

A

grazing - grazing is a gradual form of vegetation removal - rotational vs continual, type of grazing animal

cutting - sudden and large removal of vegetation, can destroy habitats, creats a uniform short grassy area, causes soil compaction from heavy machinery. can avoid killing birds by cutting fields from the inside out
Less selective, uniform turf, less disturbance, greater impact on tall herbs
Cuttings; if left can swamp small plants

Good and bad points:
Good for enhancement
Bad for invertebrates

burning - sudden process, destructive, leaves bare patches, risks wildlife and inverts, only acceptable use of burning is to remove impalatable plants to livestock and remove invasive species such as japanese knotweed.

99
Q

which technique is the best for maintenence and enhancement for grasslands

A

Major technique for enhancement is cutting

Major technique for maintenance is grazing (except meadows)

100
Q

does woodland management take a long time?

A

woodland management – the whole thing takes TIME, planning ahead and thinking about timespans that go beyond a single (human) lifetime

101
Q

what does management focus on for maximum timber quality

A

Timber producing areas tend to focus on the dominant species for maximum timber quality

102
Q

what are the two main types of woodland management

A

Historically woodland is managed in a number of ways depending on…
Species of tree
Availability of tools
Necessary skills of the workforce
Required ‘products’
Essentially two types – ‘high forest’ and ‘coppice’

103
Q

describe woodland mangement - high forest

A

A traditional approach where trees are allowed (encouraged) to grow straight and tall and form a closed canopy.
Traditionally from seed, often now planted.
Rotation can be as little as 15 years for some poplars and 160 years for oak.
Planted at a high density and thinned (see later)
Planted high forest produces even aged stands.

In the past has often been clear-felled.

Clear felling is now not as common for both conservation and landscape reasons

most used management

104
Q

describe coppice woodland management

A

One of the earliest forms of management
Relies on the ability of most broadleaved trees to regenerate from a stump or ‘stool’.
Most broadleaves will coppice, but the ‘coppice cycle’ varies between species.
Coppice trees have a well established root systems and produce biomass much quicker that trees grown for seed.
In the past the products were used for wood-fuel, charcoal, and building materials
Neglected coppice is sometimes converted into high coppice through the process of singling, or abandoned coppice can convert to high forest in time (although the structure is less stable in this case)

105
Q

what is short rotational coppicing in woodland management

A

Short rotation coppice is a reasonably new phenomenon – in vogue for the past 25 years.
Often consisting of willow planted at very high density
Used as a biomass fuel for power-stations.
Coppice woodlands provide 7.5M Tons of biomass annually
Short rotation energy crops grown on unused agricultural land could be the key for Britain to meet its biofuel targets without disrupting the food industry or the environment

106
Q

what is pollarding

A

Pollarding is specialised form of coppice designed to generate the same types of shoots but offering protection against large herbivores.

rarely used now but is useful for prolonging the life of a tree, produces oaks and beeches rich in fungi and epiphytes making it desirable in lowland wood pasture

107
Q

what is wood pasture

A

A form of agro-forestry combining widely spaced trees and grazing in the same area. More common in continental Europe than UK.

108
Q

what is the best management for ancient woodlands

A

coppicing as many scarcer plants and animals are adapted to the conditions it creates, it creates a variety of habitat strutures

109
Q

what woodlands are best managed by coppicing

A

ancient lowland woodlands, upland sessile oak woodlands

110
Q

what woodlands are managed well by grazing?

A

wood pasture - the aim is to ensure the survival of ancient trees and their associated microhabitats (hollow trunks, dead wood), there should be little need for active management
most pasture woods have regenerated sucessfully when grazing pressure is temporariy reduced producing varied structures and habitats. rotational grazing would be useful here. some rare lichens may become shaded if grazing is relaxed too much

111
Q

describe the 4 systems of high forest in woodland management

A

clear fell - trees are cut in large coupes at least 1 ha and restocked by planting - cant destroy habitats, creates patchwork of even aged stands, takes decades to restore the patch to what it was before (all confiers are clear felled)

shelterwood - cuts a stand in two stages, restocking by natural egeneration, first cut thins the canopy and second after seedlings have established. creates even aes stands,

group fell system - small scale clear fell system with small groups of trees clearfelled 0.3ha, restocked naturally or planting, creates finer mosaic and even aged stands than clear felling

selection systems - felling and regeneration are widespread and frequent, regeneration is natural, only practical for shade bearing species such as beech and lime. rare in UK

112
Q

which high forest system would create habitats for birds

A

selection systems although rarely used in the uk, it would create rich habitats for birds but animals would be scarce as they need open ground undisturbed by machinery

113
Q

what management system should be used for confier woodlands

A

clearfelling - can provide habitats for species associated with different stages of woodland succession because they are harvested rotationally in coupes - also stops red needle blight by creating airflow between trees and helps them to grow straighter for timber

114
Q

describe ancient semi natural woodland

A

Reflects the fact that our woodlands are managed now or in past history.
Wooded since at least 1600 (1750 Scotland)
Composed of native species
Not planted – must be natural regeneration
May be managed – coppiced woodland can be ASNW
Structure and composition reflects location and management history.
Often highly valuable both ecologically and culturally.
Often highly fragmented with knock on effects of a high proportion of woodland edge

rarest woodland type, highest conservation value

115
Q

describe recent semi natural woodland

A

Includes a wide range of woodland types. Characterised by regeneration of locally native species.
May be on abandoned moorlands, disused industrial sites, railway sidings etc.
Younger woodlands tend to be of pioneer species, older post 16 woodlands might include oak, ash and beech.
may provide valuable habitats, species mixture and structure

116
Q

describe recent woodland

A

Includes the Forestry Commission plantations since 1919, private forestry plantations since 1960, 18th century parklands, often of non native species such as Douglas fir or Sitka spruce.
Can be important for wildlife (Red squirrel; Osprey).
Many now valued more for ecological value than timber value (NE England example)
variable from commercial timber woodland to parkland

117
Q

why does thinning woodland management help quality

A
Essentially thinning improves quality by
Reducing competition
Promoting vigorous growth
Removing poor quality trees 
Cracked
Poor crowns
Poor vigour
Poor shape
Disease or pest damage
118
Q

why do trees need to be thinned

A

Trees might be planted at a density of 2000-4000 per ha
Target is 200 mature trees per ha
Trees therefore need to be thinned out on a regular basis
Thinning’s can be sold or burnt (although the market is now almost non-existent)
If not done then final quality is reduced.
Operation takes place every 3-5 years in younger trees; every 10-15 years in older trees. More regular in CCF.
Target is to remove approximately 30% of trees in the first thinning operation, followed by approximately 10% for each subsequent thinning.
Trees must not be allowed to have a reduced crown as this reduces growth and ultimately yield.

119
Q

why is pruning a good management technique for plantations

A

Improves quality
2 types
Formative – up to 3m in height, promoting strong straight stems
High Pruning – ensuring a knot-free stem of 6m+

leads to straighter trees for timber

120
Q

what are the negatives of pruning and thinning

A

Pruning and thinning can lead to increased wind damage and wind-throw
either through endemic (chronic) damage or catastrophic high winds
Therefore need to consider protection for remaining trees (e.g. wind-firm edges or limited open space).
Sun scorch can also be a problem on some species (e.g. Beech)

121
Q

what are some problems of woodland management techniques

A

Drainage – poor drainage is often a sign of a poorly managed woodland
Drought – affects shallow rooted species (birch, beech, larch)
Frost – impossible to avoid but plant frost tolerant species in high risk areas (scots pine, cherry, birch, hornbeam, sycamore)

122
Q

what 6 things are important for butterfly conservation in woodlands

A

Presence of food plant is primary importance

Degree of shelter is important

Age of stand is important
black hairstreaks need old blackthorn to survive but larvae do better on young blackthorn.

Nectar is vital to the adults

A place to bask is vital (a ride will do)

A variety of shrubs etc. on the woodland edge will increase biodiversity

123
Q

what two woodlands does the high brown fritillery breed in

A

Breeds in two areas
coppiced woodland – where there is bracken
Lowland bracken dominated slopes (>50% bracken) interspersed with clearings.
Some bracken is vital because it provides a very warm micro-climate.

124
Q

what two habitats are duke of burgundy butterflies found in

A

Found in two main habitats

Open deciduous/coppice woodlands
Calcareous grasslands with little or no grazing.
Foodplant is primrose (Primula vulgaris) or cowslip

125
Q

what are the current threats of the duke of burgundy butterfly

A

Continuing decline in woodland management
Continuing decline in the demand for woodland products
Further loss of unimproved grassland
Spread of bracken
Recovery in rabbit numbers
Inappropriate grazing (and deer grazing)
Increase in summer droughts as a result of climate change.

Small isolated populations are, of course, subject to genetic issues:

Inbreeding
Genetic stochasticity and drift
Inability to adapt

126
Q

what kind of woodlands are vital for beetle conservation

A

Areas designed for sustained yield will contain many habitats suiting a wide range of beetles.
Commercial forests contain little dead timber – try leaving thinned trees to decay, be untidy!
Often control is more important than conservation

127
Q

why is spatial and structural diversity important for wildlife in woodlands

A

spatial:
Maximise diversity if all tree age classes are present
Scale is also important – large mammals need large areas – many insects don’t!
Fragmentation of woodlands therefore affects species

structural:
Structural diversity creates niches – this creates opportunities for greater biodiversity
40-60% of birds & 65 – 70% mammals in Europe & USA breed in forests …… 20% of birds and 50% of mammals depend on old growth and associated diversity.
Maintenance of old growth features is vital

128
Q

what has led to the decline of birds in woodland in the past 50 years

A

Over the past 50 years coppice woodland has declined and is almost non-existent except for Kent and some key conservation woodlands.
Changes to habitat affect some bird species, lack of new woodland and open woodland (coppice and new plantation) affects species requiring that habitat.
Many new plantations and woodlands consist of conifers rather than broadleaves. This controls bird species in a similar way to insect species.
New conifer plantations are good for some species (e.g. black grouse) but support few species once mature.

129
Q
  1. Critically discuss how the future management of the UK uplands can promote both high levels of biodiversity and a sustainable economy.
A

grazing, forestry, tourism, ecotourism, landscape value, management for water, management for energy, social and wellbeing effects, existence value, wildlife value, recreational value. This may be linked to re-wilding - as discussed in the associated session.
Some critical discussion on how to promote both biodiversity and economic sustainability should follow - this is an emotive issue for some and is likely to generate some personal opinion, this is encouraged as long as it is backed up with facts or data.
There should be a summary of the information presented and, where appropriate, a conclusion.

130
Q

what are the uplands and the habitats associated with them

A

These include very large expanses of blanket bog and upland heathland, calcareous grasslands, fens and swamps,

131
Q

what are some of the main problems in the reduction of upland habitats

A

the uplands have suffered huge losses of semi-natural habitat and associated species. Since the 1950s, species-poor acid grasslands, ‘improved’ hill pastures and conifer plantations have replaced many areas of semi-natural habitat due mainly to afforestation and improvements made for agriculture and game rearing. There have also been widespread reductions in the extent and quality of surviving areas of upland habitats due to over-grazing, inappropriate burning, peat extraction, and quarrying, combined with extensive atmospheric pollution.

132
Q

what habitats are associated with lowlands

A

grasslands - acid and calcaerous, heathland, wetlands

133
Q
  1. A series of Marine Conservation Zones (MCZ) have recently been established in UK waters. Critically discuss both the positive and negative aspects of MCZs. Use referenced case studies in your answer to support your arguments.
A
Positives:
•	Increase diversity
•	Protect species from over harvesting
•	Preserve entire ecosystems
•	Increase fish stocks and other important food stocks
•	Conserve specific key species
•	Recreation
•	Control pests and invasive species
•	Preservation of medical and genetic resources
•	Prevention of land erosion
•	Nutrient cycling
•	Carbon sequestration and climatic regulation

Negatives:
• Social issues
• Loss of income from certain parties – in particular small scales fishermen
• Displacement of local human populations – Chagos MPA as an example
• Difficult to design an effective one
• Expensive to manage effectively
• Can’t predict how the animals will use them
• Linkage between MPAS
• Potential for a species ‘sink’
• Political issues – oil/gas exploration

134
Q
  1. It is often the view of members of the general public that ‘Nature can look after itself’. Critically discuss why natural habitats need to be managed giving referenced examples to support your arguments.
A
  • Habitat management for conservation can maintain, enhance or restore biodiversity. Students should explain the differences: maintain what is already there; enhance what is already there; restore what was once there.
  • Of the three, the restoration of biodiversity is the least common, although an ever increasing number of projects attempt to do this; for example on ‘brown-field’ sites.
  • The majority of habitat management is designed to enhance biodiversity. Many habitats are degraded and management to enhance biodiversity is appropriate.
  • In some habitats – particularly those in the early stages of ecological succession – management is designed to maintain the current biodiversity by holding ecological succession at bay.
  • Not all habitats are equally amenable to restoration; those in the early stages of ecological succession (for example – grasslands; salt-marsh, etc.) more so than climax communities.
  • True climax oak woodland is less amenable to complete restoration because of the time-scales involved and the high level of biodiversity. Secondary woodland is the inevitable outcome.
  • Some habitats require less management than others. On the whole early stage ecological succession habitats require less habitat management than ecological climatic climax communities.
135
Q
  1. ‘Diversity is the key word when it comes to habitat management.’ Critically discuss this statement giving referenced examples to support your arguments
A

Diversity really is a key word when it comes to habitat management as the greater the variety the greater the overall biodiversity.
• The greater the diversity of different habitats on-site the greater the total number of plant species.
• The greater the diversity of plant species on-site the greater the diversity of invertebrate species; and the greater the diversity of bird species that feed on the invertebrates, etc.
• However, a balance needs to be achieved between habitat diversity and habitat area. Small habitat areas will have fewer species than larger ones.
• The greater the diversity of structural layers on the site – ground layer, herb layer, shrub layer, and tree layer – the greater the overall biodiversity.
• The greater the diversity of management techniques the greater the overall biodiversity.

136
Q
  1. With specific reference to Cannock Chase critically discuss how the management of Heather Calluna vulgaris is being used to enhance the biodiversity on the heathland
A
  • Heathland is not a climax community but an intermediate stage of ecological succession.
  • To maintain heathland in this intermediate stage of ecological succession it has to be intensively managed; controlling scrub and tree invasion.
  • Heather Calluna vulgaris is one of the defining species on heathlands. Heather can live for more than 30 years and four distinct growth stages can be defined: Pioneer (3-10 years) – seedling stage; Building (7-13 years) - dense dome stage; Mature (12-30 years) - centre opens stage; Degenerate (>30yrs) – collapse stage.
  • A wide range of heathland invertebrate and vertebrate species require Heather at each of its different growth stages.
  • Heather needs to be managed to maintain a patchwork of these different growth stages. Heather management techniques include:
  • Grazing: Species and grazing density, etc.
  • Burning: Rotating patch system.
  • Clearance by hand: Labour intensive; use of chemicals; removal of debris, etc.
  • Clearance using machinery: Efficient but expensive; damage to fragile heath, etc.
  • At Cannock the Heather is managed using a rotational patchwork system and a piece of cutting machinery dedicated for the purpose.
137
Q
  1. ‘All types of waterbody are managed in exactly the same way.’ Critically discuss this statement giving referenced examples to support your arguments
A
  • Static and flowing water bodies need to be managed in quite different ways.
  • Static water bodies (ponds and lakes) are ‘closed systems’.
  • Flowing water bodies (streams and rivers) are ‘open systems’.
  • Five main management techniques for water bodies; each technique is used to a greater or lesser extent dependent on whether the water body is static or flowing:
    1. Water flow
    1. Pollution
    1. Weed control
    1. Bank vegetation
    1. Dredging
  • Static water bodies are vulnerable to ecological succession and drying out and so require more intensive management.
  • Flowing water bodies are much less vulnerable to ecological succession and drying out and so require less intensive management.
138
Q
  1. Critically discuss coppicing as a means of managing woodlands.
A
  • The UK is a sparsely wooded country: 11.5% of Great Britain is covered with trees. Only 1.2% of GB is ancient semi-natural woodland, a valuable and irreplaceable natural resource. Ancient semi-natural woodland, and plantations on ancient woodland sites, are a priority for conservation.
  • Many woods are threatened by neglect. The reintroduction of management is critical where species of open woodlands are in serious decline or where spread of invasive non-native species threatens long-established vegetation communities.
  • Issues of neglect and restoration are addressed through Woodland Habitat Action Plans (HAPs). Several woodland types are Priority Habitats under the UK Biodiversity Action Plan (BAP): Lowland beech and yew woodland; Lowland wood-pasture and parkland; Native pine woodlands; Upland mixed ashwoods; Upland oakwood; and Wet woodland.
  • Coppicing: Traditional woodland management technique.
  • Coppiced trees are cut off at ground level. Divide wood into coupes of about 0.5 ha. Cut in rotation over 15 years. Cut adjacent coupes next year. Remove wood or pile up.
  • Coppicing is hard to reinstate after a long period of woodland neglect. However, there are clear benefits in the form of increased biodiversity.
  • Coppicing is slowly being reinstated as a woodland management process as the market for the woody material harvested also develops; increasingly used for natural fencing, stakes, ‘pea-sticks’, etc.
139
Q

Critically discuss the usefulness of the National Vegetation Classification (NVC) scheme for habitat management.

A
  • Classification is a prerequisite to structuring knowledge and developing our understanding of the natural world.
  • A strong and consistent base of classification also provides an important tool for habitat management and nature conservation.
  • It is vital to be able to identify and record species, ecological communities and habitat types of interest that are under threat so that they can be related to a legal framework to ensure their protection.
  • Classification also provides a language through which data can be communicated at a national and international level.
  • There are many ways of describing the vegetation, but three main groups: Physiognomy; appearance, as in remote sensing. Structure - tree or shrub. Floristics - species present.
  • National Vegetation Classification (NVC) scheme is one of the most widely accepted and used although there are many others, including Phase 1 Habitat Classification.
  • All have different strengths and weaknesses: Scope (Single ecosystem to comprehensive); Strengths (Basic to complex classification); Weaknesses (Basic to complex classification).
140
Q

Critically discuss how different techniques for the management of Heather Calluna vulgaris can be used to enhance heathland biodiversity.

A
  • Heathland is not a climax community but an intermediate stage of ecological succession.
  • To maintain heathland in this intermediate stage of ecological succession it has to be intensively managed; controlling scrub and tree invasion.
  • Heather Calluna vulgaris is one of the defining species on heathlands. Heather can live for more than 30 years and four distinct growth stages can be defined: Pioneer (3-10 years) – seedling stage; Building (7-13 years) - dense dome stage; Mature (12-30 years) - centre opens stage; Degenerate (>30yrs) – collapse stage.
  • A wide range of heathland invertebrate and vertebrate species require Heather at each of its different growth stages.
  • Heather needs to be managed to maintain a patchwork of these different growth stages. Heather management techniques include:
  • Grazing: Species and grazing density, etc.
  • Burning: Rotating patch system.
  • Clearance by hand: Labour intensive; use of chemicals; removal of debris, etc.
  • Clearance using machinery: Efficient but expensive; damage to fragile heath, etc.
141
Q

Review the methods by which man can seek to reduce the incidence and severity of plant disease, and discuss the extent to which these strategies are likely to be effective against pathogens which threaten our native trees.

A
  • Relevant pathogen/host combinations.
  • Elm/Dutch Elm Disease.
  • Oak (plus wide range of other woody species)/Sudden Oak Death.
  • Ash/Ash Dieback.
  • Good plant hygiene, vigilance and destruction of infected material (without transporting it round the country first).
  • Screening for species and varieties that show some resistance or tolerance to disease. Propagating them, cuttings, micropropogation; potential to use in breeding programmes, but very slow process, while pathogen can evolve virulence rapidly. Mature tree may not behave as seedling so early screening problematic.
  • Fungicides applications, protectant or systemic, work on trunk injection technology. But difficult to get fungicide into xylem where pathogen often resides. Plant often blocks xylem in any case in response to infection. Pathogens can evolve resistance to many fungicides. (One Fungicide being tried is combination of a dithiocabamate and metalaxyl, so may have a longer useful life than one chemical on its own.)
  • Experiments using mulches to prevent disease spread from pathogen surviving in leaf litter and soil. Use of some saprophytic beneficial fungi, - biological control. Copper containing membranes, heat treated wood shavings, chemical soil sterilants.
  • Investigating time of year/weather patterns which are conducive to disease spread in order to focus control attempts.
  • Legislation to ban imports and movement of potentially infected plants, but disease already here. Spores may be able to cross the channel, especially if aided by migrating birds and insects.
  • Difficult/impossible to contain if disease has windborne spores. Controlling Elm bark beetle was potentially easier, but even that failed.
  • Full extent of problem will not be revealed until spring.
142
Q
  1. ‘Diversity is the key word when it comes to habitat management.’ Critically discuss this statement, giving specific examples.
A

Diversity really is a key word when it comes to habitat management as the greater the variety the greater the overall biodiversity.
• The greater the diversity of different habitats on-site the greater the total number of plant species.
• The greater the diversity of plant species on-site the greater the diversity of invertebrate species; and the greater the diversity of bird species that feed on the invertebrates, etc.
• However, a balance needs to be achieved between habitat diversity and habitat area. Small habitat areas will have fewer species than larger ones.
• The greater the diversity of structural layers on the site – ground layer, herb layer, shrub layer, and tree layer – the greater the overall biodiversity.
• The greater the diversity of management techniques the greater the overall biodiversity.

143
Q
  1. Critically evaluate how changes in woodland management strategies might affect bird and butterfly distribution and abundance in woodland habitats
A

There is not obvious single appropriate answer to this question and students might choose to take it in a number of equally acceptable directions.
Answers might define different types of woodland and the key features of them, including ASNW, coppice, high forest wood pasture etc. This is OK but defining woodland types will not be sufficient to answer the question unless it is tied into a strategy at some point.
Answers might introduce the major factors that control populations of woodland birds and butterflies; this includes both the tree species composition and the structure of the woodland – perhaps linked to the premise that diversity begets diversity. Good answers are also likely to provide commentary on changes in the distribution of birds and butterflies over recent history – the data was provided in the lecture and additional material has been made available online. This may elicit an evaluation of the problems currently facing woodland species; this is pretty clear cut for many woodland butterfly species which have declined catastrophically in the past 50 due to the lack of coppice and other management that provides early stage woodland (e.g. high brown, pearl bordered fritillaries) but has been beneficial for other species (e.g. speckled wood). Specialist bird populations have also declined although the reasons are far less obvious.
Students might look at a range of management options that could influence bird and butterfly ecology. These include, inter alia, planting new woodland, removal of less biodiversity-friendly woodlands and bringing undermanaged woodland into production. Some of the better answers might discuss, for example, where new woodlands should be created to maximise biodiversity benefit, or who owns new woodlands (there is growing evidence that this is one of the key issues that ultimately drives biodiversity levels). Additionally, there are a range of other scenario’s that might be brought in here, including which species to plant, harvest regimes (clear fell –v- continuous cover), enhancing connectivity and stimulating demand (as there are very limited funds available for managing woodland without an economic incentive). Some answers may look at woodland grant schemes for supporting these initiatives. This would also be acceptable and has the potential for a good answer as these are unlikely to be explored in great depth in in either the lecture sessions or associated field trip.
As with most level 6 answers, a sensible structure, cogent flow and demonstration of reading around the subject will be required for top marks to be given.

144
Q
  1. Giving specific examples, critically discuss why natural habitats need to be managed
A

Habitat management for conservation can maintain, enhance or restore biodiversity. Students should explain the differences: maintain what is already there; enhance what is already there; restore what was once there.
• Of the three, the restoration of biodiversity is the least common, although an ever increasing number of projects attempt to do this; for example on ‘brown-field’ sites.
• The majority of habitat management is designed to enhance biodiversity. Many habitats are degraded and management to enhance biodiversity is appropriate.
• In some habitats – particularly those in the early stages of ecological succession – management is designed to maintain the current biodiversity by holding ecological succession at bay.
• Not all habitats are equally amenable to restoration; those in the early stages of ecological succession (for example – grasslands; salt-marsh, etc.) more so than climax communities.
• True climax oak woodland is less amenable to complete restoration because of the time-scales involved and the high level of biodiversity. Secondary woodland is the inevitable outcome.
• Some habitats require less management than others. On the whole early stage ecological succession habitats require less habitat management than ecological climatic climax communities.

145
Q
  1. Critically discuss the use of grazing as a tool for the management of calcareous grasslands.
A
  • Grassland is not a climax community but an early stage of ecological succession.
  • To maintain grassland in this early stage of ecological succession it has to be intensively managed to controlling scrub and tree invasion.
  • Grazing is one of several management options. Need to consider what species to use and at what grazing density. There are distinct costs and benefits of this technique.
  • Burning is a second option: Rotating patch system. There are distinct costs and benefits of this technique.
  • Cutting by hand: Labour intensive; issues over the removal of cut grass, etc. There are distinct costs and benefits of this technique.
  • Cutting using machinery: Efficient but expensive; damage to fragile grassland, etc. There are distinct costs and benefits of this technique.
  • Grazing is a traditional technique and is often the preferred option; however, this has to be balanced with many other factors.
  • Grazing creates sward diversity as the grazing animals are selective.
  • Grazing comes with many potential problems; fencing the animals; control of the animals; grazing density; faeces; trampling damage; stock management out of season; food and water supply in winter; etc.
146
Q

Changes in the population of woodland birds in the UK between 1970 and 2012 are shown below in Graph 1. The Index for 1970 has been set at a baseline value of 100 to allow comparison over subsequent years. Critically evaluate how changes in woodland management may have influenced the trends seen in this graph.

A
  • Introduce the issue
  • Briefly describe the trends shown in graph 1 (although an answer that only does this will fail) and differentiate between generalist and specialist birds, demonstrate some background knowledge underpinning the data (such as knowledge of individual species trends).
  • Describe major changes in woodland management
  • Overall increase in population status of generalists
  • Decline overall and especially from the late 1980’s onwards
  • Substantial decline in specialist
  • Recent recovery
  • Critically evaluate how changes in woodland management may have led to the trends including:
  • There is no certain single causative factor but a range of interacting issues
  • Changes in woodland structure are implicated due to
  • Aging of woodlands generally
  • Lack of management increasing canopy and reducing understory species
  • Overgrazing by deer
  • Point to other relevant potential management causes e.g.
  • Grey squirrel population potentially impacts some species (e.g. hawfinch, lesser spotted woodpecker)
  • Be critical about the confidence of the impact of woodland management and point out other issues affecting some species (e.g. migration issues)
147
Q

‘Biodiversity can be enhanced on any site solely through the manipulation of ecological succession.’ Critically discuss this statement, giving examples wherever possible.

A
  • Habitat management for conservation is aimed at the maintenance, enhancement or restoration of biodiversity.
  • Ecological succession is the stages a habitat passes through until it reaches the climatic climax for that particular ecological community.
  • Many habitats being managed for their biodiversity are those in the early stages of ecological succession.
  • All communities - except climatic climax communities – go through ecological succession and so for habitats in early successional stages habitat management is primarily designed to maintain the current biodiversity by holding ecological succession at bay.
  • Some habitats require less management than others. On the whole early stage ecological succession habitats require less habitat management than ecological climatic climax communities.
  • Nutrient accumulation: A natural part of succession but man has increased the nutrient supply. Speeds up succession and creates new communities.
  • The manipulation of ecological succession could be seen as a main goal of habitat management.
  • However, diversity is also a key word when it comes to habitat management as the greater the variety the greater the overall biodiversity.
  • The greater the diversity of different habitats on-site the greater the total number of plant species.
  • The greater the diversity of plant species on-site the greater the diversity of invertebrate species; and the greater the diversity of bird species that feed on the invertebrates, etc.
  • Even in communities that are at their climatic climax and hence not going through such active ecological succession, habitat management can still play an important role in the enhancement of biodiversity.
  • Habitat management can create associated habitats such as ponds, rides, glades, banks, etc., which can greatly enhance the overall biodiversity of the site.
  • Habitat management can create disturbance; many habitats need this; space for regeneration. Creates a patchwork of ecological successional stages. Creates structural diversity. Prevents local ecological climax. However, too much disturbance is harmful.
  • Habitat management aims to create a variety of habitats, at a range of ecological successional stages, using a variety of different management techniques.
148
Q

what are the pros and cons of marine protected areas

A
Pros
•	Increase diversity
•	Protect species from over harvesting
•	Preserve entire ecosystems
•	Increase fish stocks and other important food stocks
•	Conserve specific key species
•	Recreation
•	Control pests and invasive species
•	Preservation of medical and genetic resources
•	Prevention of land erosion
•	Nutrient cycling
•	Carbon sequestration and climatic regulation

Cons
• Social issues
• Loss of income from certain parties – in particular small scales fishermen
• Displacement of local human populations – Chagos MPA as an example
• Difficult to design an effective one
• Expensive to manage effectively
• Can’t predict how the animals will use them
• Linkage between MPAS
• Potential for a species ‘sink’
• Political issues – oil/gas exploration

149
Q

Critically discuss the design of rides and glades and how they can be used for the enhancement of biodiversity.

A
  • The UK is a sparsely wooded country: 11.5% of Great Britain is covered with trees. Only 1.2% of GB is ancient semi-natural woodland, a valuable and irreplaceable natural resource. Ancient semi-natural woodland, and plantations on ancient woodland sites, are a priority for conservation.
  • Many woods are threatened by neglect. The reintroduction of management is critical where species of open woodlands are in serious decline or where spread of invasive non-native species threatens long-established vegetation communities.
  • Issues of neglect and restoration are addressed through Woodland Habitat Action Plans (HAPs). Several woodland types are Priority Habitats under the UK Biodiversity Action Plan (BAP): Lowland beech and yew woodland; Lowland wood-pasture and parkland; Native pine woodlands; Upland mixed ashwoods; Upland oakwood; and Wet woodland.
  • The selective felling of trees to create rides and glades can enhance overall species diversity.
  • A ride is a linear woodland opening, such as a track.
  • A glade is a circular woodland opening.
  • Rides and glades allow more sunlight to reach the ground and can stimulate the growth of a rich ground flora; enhancing overall invertebrate diversity.
  • The orientation of the ride needs to be considered in relation to the rising and setting of the sun. Creates microclimatic differences; light levels; temperature differences; water availability; etc.
  • However, rides and glades will create woodland edge and consequently a potentially wide range of negative ‘edge effects’.
  • Both the positive and negative aspects of rides and glades need to be considered in woodland management.