Table des matières
1. AMPHIBIAN CONSERVATION
1.2 Threat: Agriculture
- 1.2.1 Engage farmers and other volunteers
- Likely to be beneficial
- Engage landowners and other volunteers to manage land for amphibians
- Pay farmers to cover the costs of conservation measures
- 1.2.2 Terrestrial habitat management
- Manage silviculture practices in plantations
- Unknown effectiveness (limited evidence)
- Manage cutting regime
- Manage grazing regime
- No evidence found (no assessment)
- 1.2.3 Aquatic habitat management
- Likely to be beneficial
- Manage ditches
- Likely to be ineffective or harmful
- Exclude domestic animals or wild hogs from ponds by fencing
1.4 Threat: Transportation and service corridors
- Likely to be beneficial
- Close roads during seasonal amphibian migration
- Modify gully pots and kerbs
- Trade-off between benefit and harms
- Install barrier fencing along roads
- Install culverts or tunnels as road crossings
- Unknown effectiveness (limited evidence)
- Use signage to warn motorists
- Unlikely to be beneficial
- Use humans to assist migrating amphibians across roads
1.5 Threat: Biological resource use
- 1.5.1 Hunting and collecting terrestrial animals
- Likely to be beneficial
- Reduce impact of amphibian trade
- Unknown effectiveness (limited evidence)
- Use legislative regulation to protect wild populations
- No evidence found (no assessment)
- 1.5.2 Logging and wood harvesting
- Likely to be beneficial
- Retain riparian buffer strips during timber harvest
- Use shelterwood harvesting instead of clearcutting
- Trade-off between benefit and harms
- Leave coarse woody debris in forests
- Unknown effectiveness (limited evidence)
- Use patch retention harvesting instead of clearcutting
- Unlikely to be beneficial
- Leave standing deadwood/snags in forests
- Use leave-tree harvesting instead of clearcutting
- Likely to be ineffective or harmful
- Harvest groups of trees instead of clearcutting
- Thin trees within forests
1.7 Threat: Natural system modifications
- Beneficial
- Regulate water levels
- Unknown effectiveness (limited evidence)
- Mechanically remove mid-storey or ground vegetation
- Likely to be ineffective or harmful
- Use herbicides to control mid-storey or ground vegetation
- Use prescribed fire or modifications to burning regime (forests)
- Use prescribed fire or modifications to burning regime (grassland)
1.8 Threat: Invasive and other problematic species
- 1.8.1 Reduce predation by other species
- Beneficial
- Remove or control fish by drying out ponds
- Likely to be beneficial
- Remove or control fish population by catching
- Remove or control invasive bullfrogs
- Remove or control invasive viperine snake
- Remove or control mammals
- Trade-off between benefit and harms
- Remove or control fish using Rotenone
- Unknown effectiveness (limited evidence)
- Exclude fish with barriers
- No evidence found (no assessment)
- 1.8.2 Reduce competition with other species
- Unknown effectiveness (limited evidence)
- Reduce competition from native amphibians
- Remove or control invasive Cuban tree frogs
- No evidence found (no assessment)
- 1.8.3 Reduce adverse habitat alteration by other species
- Likely to be beneficial
- Control invasive plants
- No evidence found (no assessment)
- 1.8.4 Reduce parasitism and disease–chytridiomycosis
- Likely to be beneficial
- Use temperature treatment to reduce infection
- Trade-off between benefit and harms
- Use antifungal treatment to reduce infection
- Unknown effectiveness (limited evidence)
- Add salt to ponds
- Immunize amphibians against infection
- Remove the chytrid fungus from ponds
- Sterilize equipment when moving between amphibian sites
- Treating amphibians in the wild or pre-release
- Use gloves to handle amphibians
- Unlikely to be beneficial
- Use antibacterial treatment to reduce infection
- Use antifungal skin bacteria or peptides to reduce infection
- No evidence found (no assessment)
- 1.8.5 Reduce parasitism and disease–ranaviruses
- No evidence found (no assessment)
1.9 Threat: Pollution
- 1.9.1 Agricultural pollution
- Unknown effectiveness (limited evidence)
- Create walls or barriers to exclude pollutants
- Plant riparian buffer strips
- Reduce pesticide, herbicide or fertilizer use
- No evidence found (no assessment)
- 1.9.2 Industrial pollution
- Trade-off between benefit and harms
- Add limestone to water bodies to reduce acidification
- No evidence found (no assessment)
1.12 Habitat restoration and creation
- 1.12.1 Terrestrial habitat
- Beneficial
- Replant vegetation
- Likely to be beneficial
- Clear vegetation
- Create artificial hibernacula or aestivation sites
- Create refuges
- Restore habitat connectivity
- Unknown effectiveness (limited evidence)
- Change mowing regime
- No evidence found (no assessment)
- 1.12.2 Aquatic habitat
- Beneficial
- Create ponds (amphibians in general)
- Create ponds (frogs)
- Create ponds (natterjack toads)
- Create ponds (salamanders including newts)
- Create wetlands
- Deepen, de-silt or re-profile ponds
- Restore wetlands
- Likely to be beneficial
- Create ponds (great crested newts)
- Create ponds (green toads)
- Create ponds (toads)
- Remove specific aquatic plants
- Restore ponds
- Unknown effectiveness (limited evidence)
- Remove tree canopy to reduce pond shading
- No evidence found (no assessment)
1.13 Species management
- 1.13.1 Translocate amphibians
- Likely to be beneficial
- Translocate amphibians (amphibians in general)
- Translocate amphibians (great crested newts)
- Translocate amphibians (natterjack toads)
- Translocate amphibians (salamanders including newts)
- Translocate amphibians (toads)
- Translocate amphibians (wood frogs)
- Trade-off between benefit and harms
- Translocate amphibians (frogs)
- 1.13.2 Captive breeding, rearing and releases
- Likely to be beneficial
- Release captive-bred individuals (amphibians in general)
- Release captive-bred individuals (frogs)
- Trade-off between benefit and harms
- Breed amphibians in captivity (frogs)
- Breed amphibians in captivity (harlequin toads)
- Breed amphibians in captivity (Mallorcan midwife toad)
- Breed amphibians in captivity (salamanders including newts)
- Breed amphibians in captivity (toads)
- Head-start amphibians for release
- Release captive-bred individuals (Mallorcan midwife toad)
- Release captive-bred individuals (toads)
- Use artificial fertilization in captive breeding
- Use hormone treatment to induce sperm and egg release
- Unknown effectiveness (limited evidence)
- Release captive-bred individuals (salamanders including newts)
- Unlikely to be beneficial
- Freeze sperm or eggs for future use
- Likely to be ineffective or harmful
- Release captive-bred individuals (green and golden bell frogs)
2. BAT CONSERVATION
2.2 Threat: Agriculture
- 2.2.1 Land use change
- Likely to be beneficial
- Protect or create wetlands as foraging habitat for bats
- Unknown effectiveness (limited evidence)
- Retain or plant trees on agricultural land to replace foraging habitat
- No evidence found (no assessment)
- 2.2.2 Intensive farming
- Likely to be beneficial
- Convert to organic farming
- Encourage agroforestry
- Unknown effectiveness (limited evidence)
- Introduce agri-environment schemes
2.5 Threat: Transportation and service corridors
- Likely to be beneficial
- Install underpasses as road crossing structures for bats
- Unknown effectiveness (limited evidence)
- Divert bats to safe crossing points with plantings or fencing
- Install bat gantries or bat bridges as road crossing structures for bats
- Install overpasses as road crossing structures for bats
- No evidence found (no assessment)
2.6 Threat: Biological resource use
- 2.6.1 Hunting
- No evidence found (no assessment)
- 2.6.2 Guano harvesting
- No evidence found (no assessment)
- 2.6.3 Logging and wood harvesting
- Likely to be beneficial
- Incorporate forested corridors or buffers into logged areas
- Use selective harvesting/reduced impact logging instead of clearcutting
- Use shelterwood cutting instead of clearcutting
- Unknown effectiveness (limited evidence)
- Retain residual tree patches in logged areas
- Thin trees within forests
- No evidence found (no assessment)
2.10 Threat: Pollution
- 2.10.1 Domestic and urban waste water
- Unknown effectiveness (limited evidence)
- Change effluent treatments of domestic and urban waste water
- 2.10.2 Agricultural and forestry effluents
- No evidence found (no assessment)
- 2.10.3 Light and noise pollution
- Likely to be beneficial
- Leave bat roosts, roost entrances and commuting routes unlit
- Minimize excess light pollution
- No evidence found (no assessment)
- 2.10.4 Timber treatments
- Beneficial
- Use mammal safe timber treatments in roof spaces
- Likely to be ineffective or harmful
- Restrict timing of treatment
3. BIRD CONSERVATION
3.4 Threat: Agriculture
- 3.4.1 All farming systems
- Beneficial
- Plant wild bird seed or cover mixture
- Provide (or retain) set-aside areas in farmland
- Likely to be beneficial
- Create uncultivated margins around intensive arable or pasture fields
- Increase the proportion of natural/semi-natural habitat in the farmed landscape
- Manage ditches to benefit wildlife
- Pay farmers to cover the costs of conservation measures
- Plant grass buffer strips/margins around arable or pasture fields
- Plant nectar flower mixture/wildflower strips
- Leave refuges in fields during harvest
- Reduce conflict by deterring birds from taking crops (using bird scarers)
- Relocate nests at harvest time to reduce nestling mortality
- Use mowing techniques to reduce mortality
- Unknown effectiveness (limited evidence)
- Control scrub on farmland
- Offer per clutch payment for farmland birds
- Manage hedges to benefit wildlife
- Plant new hedges
- Reduce conflict by deterring birds from taking crops (using repellents)
- Take field corners out of management
- Likely to be ineffective or harmful
- Mark bird nests during harvest or mowing
- No evidence found (no assessment)
- 3.4.2 Arable farming
- Likely to be beneficial
- Create ‘skylark plots’ (undrilled patches in cereal fields)
- Leave overwinter stubbles
- Leave uncropped cultivated margins or fallow land (includes lapwing and stone curlew plots)
- Sow crops in spring rather than autumn
- Undersow spring cereals, with clover for example
- Trade-off between benefit and harms
- Reduce tillage
- Unknown effectiveness (limited evidence)
- Implement mosaic management
- Increase crop diversity to benefit birds
- Plant more than one crop per field (intercropping)
- Unlikely to be beneficial
- Create beetle banks
- Likely to be ineffective or harmful
- Plant cereals in wide-spaced rows
- Revert arable land to permanent grassland
- No evidence found (no assessment)
- 3.4.3 Livestock farming
- Likely to be beneficial
- Delay mowing date on grasslands
- Leave uncut rye grass in silage fields
- Maintain species-rich, semi-natural grassland
- Maintain traditional water meadows
- Mark fencing to avoid bird mortality
- Plant cereals for whole crop silage
- Reduce grazing intensity
- Reduce management intensity of permanent grasslands
- Trade-off between benefit and harms
- Exclude livestock from semi-natural habitat
- Unknown effectiveness (limited evidence)
- Create open patches or strips in permanent grassland
- Maintain upland heath/moor
- Protect nests from livestock to reduce trampling
- Provide short grass for waders
- Raise mowing height on grasslands
- Unlikely to be beneficial
- Use traditional breeds of livestock
- No evidence found (no assessment)
- 3.4.4 Perennial, non-timber crops
- Unknown effectiveness (limited evidence)
- Maintain traditional orchards
- No evidence found (no assessment)
- 3.4.5 Aquaculture
- Likely to be beneficial
- Deter birds from landing on shellfish culture gear
- Disturb birds at roosts
- Provide refuges for fish within ponds
- Use electric fencing to exclude fish-eating birds
- Use ‘mussel socks’ to prevent birds from attacking shellfish
- Use netting to exclude fish-eating birds
- Unknown effectiveness (limited evidence)
- Increase water turbidity to reduce fish predation by birds
- Translocate birds away from fish farms
- Use in-water devices to reduce fish loss from ponds
- Unlikely to be beneficial
- Disturb birds using foot patrols
- Spray water to deter birds from ponds
- Likely to be ineffective or harmful
- Scare birds from fish farms
3.6 Threat: Transportation and service corridors
- 3.6.1 Verges and airports
- Likely to be beneficial
- Scare or otherwise deter birds from airports
- Unknown effectiveness (limited evidence)
- Mow roadside verges
- No evidence found (no assessment)
- 3.6.2 Power lines and electricity pylons
- Beneficial
- Mark power lines
- Likely to be beneficial
- Bury or isolate power lines
- Insulate electricity pylons
- Remove earth wires from power lines
- Use perch-deterrents to stop raptors perching on pylons
- Unknown effectiveness (limited evidence)
- Thicken earth wires
- Unlikely to be beneficial
- Add perches to electricity pylons
- Reduce electrocutions by using plastic, not metal, leg rings to mark birds
- Use raptor models to deter birds from power lines
3.7 Threat: Biological resource use
- 3.7.1 Reducing exploitation and conflict
- Scare fish-eating birds from areas to reduce conflict
- Beneficial
- Use legislative regulation to protect wild populations
- Likely to be beneficial
- Use wildlife refuges to reduce hunting disturbance
- Unknown effectiveness (limited evidence)
- Employ local people as ‘biomonitors’
- Increase ‘on-the-ground’ protection to reduce unsustainable levels of exploitation
- Introduce voluntary ‘maximum shoot distances’
- Mark eggs to reduce their appeal to collectors
- Move fish-eating birds to reduce conflict with fishermen
- Promote sustainable alternative livelihoods
- Provide ‘sacrificial grasslands’ to reduce conflict with farmers
- Relocate nestlings to reduce poaching
- Use education programmes and local engagement to help reduce persecution or exploitation of species
- No evidence found (no assessment)
- 3.7.2 Reducing fisheries bycatch
- Beneficial
- Use streamer lines to reduce seabird bycatch on longlines
- Likely to be beneficial
- Mark trawler warp cables to reduce seabird collisions
- Reduce seabird bycatch by releasing offal overboard when setting longlines
- Weight baits or lines to reduce longline bycatch of seabirds
- Trade-off between benefit and harms
- Set lines underwater to reduce seabird bycatch
- Set longlines at night to reduce seabird bycatch
- Unknown effectiveness (limited evidence)
- Dye baits to reduce seabird bycatch
- Thaw bait before setting lines to reduce seabird bycatch
- Turn deck lights off during night-time setting of longlines to reduce bycatch
- Use a sonic scarer when setting longlines to reduce seabird bycatch
- Use acoustic alerts on gillnets to reduce seabird bycatch
- Use bait throwers to reduce seabird bycatch
- Use bird exclusion devices such as ‘Brickle curtains’ to reduce seabird mortality when hauling longlines
- Use high visibility mesh on gillnets to reduce seabird bycatch
- Use shark liver oil to deter birds when setting lines
- Likely to be ineffective or harmful
- Use a line shooter to reduce seabird bycatch
- No evidence found (no assessment)
3.8 Threat: Human intrusions and disturbance
- Likely to be beneficial
- Provide paths to limit disturbance
- Start educational programmes for personal watercraft owners
- Use signs and access restrictions to reduce disturbance at nest sites
- Use voluntary agreements with local people to reduce disturbance
- Unknown effectiveness (limited evidence)
- Habituate birds to human visitors
- Use nest covers to reduce the impact of research on predation of ground-nesting seabirds
- No evidence found (no assessment)
3.9 Threat: Natural system modifications
- Likely to be beneficial
- Create scrapes and pools in wetlands and wet grasslands
- Provide deadwood/snags in forests (use ring-barking, cutting or silvicides)
- Use patch retention harvesting instead of clearcutting
- Trade-off between benefit and harms
- Clear or open patches in forests
- Employ grazing in artificial grasslands/pastures
- Employ grazing in natural grasslands
- Employ grazing in non-grassland habitats
- Manage water level in wetlands
- Manually control or remove midstorey and ground-level vegetation (including mowing, chaining, cutting etc.) (forests)
- Manually control or remove midstorey and ground-level vegetation (including mowing, chaining, cutting etc.) (mowing or cutting natural grasslands)
- Manually control or remove midstorey and ground-level vegetation (including mowing, chaining, cutting etc.) (mowing or cutting semi-natural grasslands/pastures)
- Manually control or remove midstorey and ground-level vegetation (including mowing, chaining, cutting etc.) (shrublands)
- Raise water levels in ditches or grassland
- Thin trees within forests
- Use prescribed burning (grasslands)
- Use prescribed burning (pine forests)
- Use prescribed burning (savannahs)
- Use prescribed burning (shrublands)
- Use selective harvesting/logging instead of clearcutting
- Unknown effectiveness (limited evidence)
- Clearcut and re-seed forests
- Coppice trees
- Fertilise grasslands
- Manage woodland edges for birds
- Manually control or remove midstorey and ground-level vegetation (including mowing, chaining, cutting etc.) (reedbeds)
- Manually control or remove midstorey and ground-level vegetation (including mowing, chaining, cutting etc.) (savannahs)
- Plant trees to act as windbreaks
- Plough habitats
- Provide deadwood/snags in forests (adding woody debris to forests)
- Remove coarse woody debris from forests
- Replace non-native species of tree/shrub
- Re-seed grasslands
- Use environmentally sensitive flood management
- Use fire suppression/control
- Use greentree reservoir management
- Use prescribed burning (Australian sclerophyll forest)
- Use shelterwood cutting instead of clearcutting
- Use variable retention management during forestry operations
- Likely to be ineffective or harmful
- Apply herbicide to mid-and understorey vegetation
- Treat wetlands with herbicides
- Use prescribed burning (coastal habitats)
- Use prescribed burning (deciduous forests)
- No evidence found (no assessment)
3.10 Habitat restoration and creation
- Beneficial
- Restore or create forests
- Restore or create wetlands and marine habitats (inland wetlands)
- Likely to be beneficial
- Restore or create grassland
- Restore or create traditional water meadows
- Restore or create wetlands and marine habitats (coastal and intertidal wetlands)
- Unknown effectiveness (limited evidence)
- Restore or create shrubland
- Restore or create wetlands and marine habitats (kelp forests)
- Restore or create wetlands and marine habitats (lagoons)
- No evidence found (no assessment)
3.11 Threat: Invasive alien and other problematic species
- 3.11.1 Reduce predation by other species
- Beneficial
- Control mammalian predators on islands
- Remove or control predators to enhance bird populations and communities
- Likely to be beneficial
- Control avian predators on islands
- Unknown effectiveness (limited evidence)
- Control invasive ants on islands
- Reduce predation by translocating predators
- Evidence not assessed
- Control predators not on islands
- 3.11.2 Reduce incidental mortality during predator eradication or control
- Unknown effectiveness (limited evidence)
- Distribute poison bait using dispensers
- Use coloured baits to reduce accidental mortality during predator control
- Use repellents on baits
- Evidence not assessed
- Do birds take bait designed for pest control?
- 3.11.3 Reduce nest predation by excluding predators from nests or nesting areas
- Likely to be beneficial
- Physically protect nests from predators using non-electric fencing
- Physically protect nests with individual exclosures/barriers or provide shelters for chicks
- Protect bird nests using electric fencing
- Use artificial nests that discourage predation
- Unknown effectiveness (limited evidence)
- Guard nests to prevent predation
- Plant nesting cover to reduce nest predation
- Protect nests from ants
- Use multiple barriers to protect nests
- Use naphthalene to deter mammalian predators
- Use snakeskin to deter mammalian nest predators
- No evidence found (no assessment)
- Evidence not assessed
- Can nest protection increase nest abandonment?
- Can nest protection increase predation of adults and chicks?
- 3.11.4 Reduce mortality by reducing hunting ability or changing predator behaviour
- Unknown effectiveness (limited evidence)
- Reduce predation by translocating nest boxes
- Use collar-mounted devices to reduce predation
- Use supplementary feeding to reduce predation
- Unlikely to be beneficial
- Use aversive conditioning to reduce nest predation
- 3.11.5 Reduce competition with other species for food and nest sites
- Likely to be beneficial
- Reduce inter-specific competition for food by removing or controlling competitor species
- Unknown effectiveness (limited evidence)
- Protect nest sites from competitors
- Reduce competition between species by providing nest boxes
- Reduce inter-specific competition for nest sites by modifying habitats to exclude competitor species
- Reduce inter-specific competition for nest sites by removing competitor species (ground nesting seabirds)
- Reduce inter-specific competition for nest sites by removing competitor species (songbirds)
- Reduce inter-specific competition for nest sites by removing competitor species (woodpeckers)
- 3.11.6 Reduce adverse habitat alteration by other species
- Likely to be beneficial
- Control or remove habitat-altering mammals
- Reduce adverse habitat alterations by excluding problematic species (terrestrial species)
- Unknown effectiveness (limited evidence)
- Reduce adverse habitat alterations by excluding problematic species (aquatic species)
- Remove problematic vegetation
- Use buffer zones to reduce the impact of invasive plant control
- 3.11.7 Reduce parasitism and disease
- Likely to be beneficial
- Remove/control adult brood parasites
- Trade-off between benefit and harms
- Remove/treat endoparasites and diseases
- Unknown effectiveness (limited evidence)
- Alter artificial nest sites to discourage brood parasitism
- Exclude or control ‘reservoir species’ to reduce parasite burdens
- Remove brood parasite eggs from target species’ nests
- Remove/treat ectoparasites to increase survival or reproductive success (provide beneficial nesting material)
- Remove/treat ectoparasites to increase survival or reproductive success (remove ectoparasites from feathers)
- Use false brood parasite eggs to discourage brood parasitism
- Unlikely to be beneficial
- Remove/treat ectoparasites to increase survival or reproductive success (remove ectoparasites from nests)
- 3.11.8 Reduce detrimental impacts of other problematic species
- Unknown effectiveness (limited evidence)
- Use copper strips to exclude snails from nests
3.12 Threat: Pollution
- 3.12.1 Industrial pollution
- Likely to be beneficial
- Use visual and acoustic ‘scarers’ to deter birds from landing on pools polluted by mining or sewage
- Unknown effectiveness (limited evidence)
- Relocate birds following oil spills
- Use repellents to deter birds from landing on pools polluted by mining
- Unlikely to be beneficial
- Clean birds after oil spills
- 3.12.2 Agricultural pollution
- Likely to be beneficial
- Leave headlands in fields unsprayed (conservation headlands)
- Provide food for vultures to reduce mortality from diclofenac
- Reduce pesticide, herbicide and fertiliser use generally
- Unknown effectiveness (limited evidence)
- Reduce chemical inputs in permanent grassland management
- Restrict certain pesticides or other agricultural chemicals
- No evidence found (no assessment)
- 3.12.3 Air-borne pollutants
- Unknown effectiveness (limited evidence)
- Use lime to reduce acidification in lakes
- 3.12.4 Excess energy
- Unknown effectiveness (limited evidence)
- Shield lights to reduce mortality from artificial lights
- Turning off lights to reduce mortality from artificial lights
- Use flashing lights to reduce mortality from artificial lights
- Use lights low in spectral red to reduce mortality from artificial lights
- No evidence found (no assessment)
3.14 General responses to small/declining populations
- 3.14.1 Inducing breeding, rehabilitation and egg removal
- Unknown effectiveness (limited evidence)
- Rehabilitate injured birds
- Remove eggs from wild nests to increase reproductive output
- Use artificial visual and auditory stimuli to induce breeding in wild populations
- 3.14.2 Provide artificial nesting sites
- Beneficial
- Provide artificial nests (falcons)
- Provide artificial nests (owls)
- Provide artificial nests (songbirds)
- Provide artificial nests (wildfowl)
- Likely to be beneficial
- Clean artificial nests to increase occupancy or reproductive success
- Provide artificial nests (burrow-nesting seabirds)
- Provide artificial nests (divers/loons)
- Provide artificial nests (ground-and tree-nesting seabirds)
- Provide artificial nests (oilbirds)
- Provide artificial nests (raptors)
- Provide artificial nests (wildfowl — artificial/floating islands)
- Unknown effectiveness (limited evidence)
- Artificially incubate eggs or warm nests
- Guard nests
- Provide artificial nests (gamebirds)
- Provide artificial nests (grebes)
- Provide artificial nests (ibises and flamingos)
- Provide artificial nests (parrots)
- Provide artificial nests (pigeons)
- Provide artificial nests (rails)
- Provide artificial nests (rollers)
- Provide artificial nests (swifts)
- Provide artificial nests (trogons)
- Provide artificial nests (waders)
- Provide artificial nests (woodpeckers)
- Provide nesting habitat for birds that is safe from extreme weather
- Provide nesting material for wild birds
- Remove vegetation to create nesting areas
- Repair/support nests to support breeding
- Use differently-coloured artificial nests
- 3.14.3 Foster chicks in the wild
- Likely to be beneficial
- Foster eggs or chicks with wild conspecifics (raptors)
- Foster eggs or chicks with wild non-conspecifics (cross-fostering) (songbirds)
- Unknown effectiveness (limited evidence)
- Foster eggs or chicks with wild conspecifics (bustards)
- Foster eggs or chicks with wild conspecifics (cranes)
- Foster eggs or chicks with wild conspecifics (gannets and boobies)
- Foster eggs or chicks with wild conspecifics (owls)
- Foster eggs or chicks with wild conspecifics (parrots)
- Foster eggs or chicks with wild conspecifics (vultures)
- Foster eggs or chicks with wild conspecifics (waders)
- Foster eggs or chicks with wild conspecifics (woodpeckers)
- Foster eggs or chicks with wild non-conspecifics (cross-fostering) (cranes)
- Foster eggs or chicks with wild non-conspecifics (cross-fostering) (ibises)
- Foster eggs or chicks with wild non-conspecifics (cross-fostering) (petrels and shearwaters)
- Foster eggs or chicks with wild non-conspecifics (cross-fostering) (waders)
- 3.14.4 Provide supplementary food
- Beneficial
- Provide supplementary food to increase adult survival (songbirds)
- Likely to be beneficial
- Place feeders close to windows to reduce collisions
- Provide calcium supplements to increase survival or reproductive success
- Provide supplementary food to increase adult survival (cranes)
- Provide supplementary food to increase reproductive success (gulls, terns and skuas)
- Provide supplementary food to increase reproductive success (owls)
- Provide supplementary food to increase reproductive success (raptors)
- Provide supplementary food to increase reproductive success (songbirds)
- Unknown effectiveness (limited evidence)
- Provide perches to improve foraging success
- Provide supplementary food through the establishment of food populations
- Provide supplementary food to allow the rescue of a second chick
- Provide supplementary food to increase adult survival (gamebirds)
- Provide supplementary food to increase adult survival (gulls, terns and skuas)
- Provide supplementary food to increase adult survival (hummingbirds)
- Provide supplementary food to increase adult survival (nectar-feeding songbirds)
- Provide supplementary food to increase adult survival (pigeons)
- Provide supplementary food to increase adult survival (raptors)
- Provide supplementary food to increase adult survival (vultures)
- Provide supplementary food to increase adult survival (waders)
- Provide supplementary food to increase adult survival (wildfowl)
- Provide supplementary food to increase adult survival (woodpeckers)
- Provide supplementary food to increase reproductive success (auks)
- Provide supplementary food to increase reproductive success (gamebirds)
- Provide supplementary food to increase reproductive success (gannets and boobies)
- Provide supplementary food to increase reproductive success (ibises)
- Provide supplementary food to increase reproductive success (kingfishers)
- Provide supplementary food to increase reproductive success (parrots)
- Provide supplementary food to increase reproductive success (petrels)
- Provide supplementary food to increase reproductive success (pigeons)
- Provide supplementary food to increase reproductive success (rails and coots)
- Provide supplementary food to increase reproductive success (vultures)
- Provide supplementary food to increase reproductive success (waders)
- Provide supplementary food to increase reproductive success (wildfowl)
- Provide supplementary water to increase survival or reproductive success
- 3.14.5 Translocations
- Beneficial
- Translocate birds to re-establish populations or increase genetic variation (birds in general)
- Translocate birds to re-establish populations or increase genetic variation (raptors)
- Likely to be beneficial
- Translocate birds to re-establish populations or increase genetic variation (parrots)
- Translocate birds to re-establish populations or increase genetic variation (pelicans)
- Translocate birds to re-establish populations or increase genetic variation (petrels and shearwaters)
- Translocate birds to re-establish populations or increase genetic variation (rails)
- Translocate birds to re-establish populations or increase genetic variation (songbirds)
- Translocate birds to re-establish populations or increase genetic variation (wildfowl)
- Translocate birds to re-establish populations or increase genetic variation (woodpeckers)
- Use decoys to attract birds to new sites
- Use techniques to increase the survival of species after capture
- Use vocalisations to attract birds to new sites
- Trade-off between benefit and harms
- Translocate birds to re-establish populations or increase genetic variation (gamebirds)
- Unknown effectiveness (limited evidence)
- Alter habitats to encourage birds to leave
- Ensure translocated birds are familiar with each other before release
- Translocate birds to re-establish populations or increase genetic variation (auks)
- Translocate birds to re-establish populations or increase genetic variation (herons, storks and ibises)
- Translocate birds to re-establish populations or increase genetic variation (megapodes)
- Translocate birds to re-establish populations or increase genetic variation (owls)
- Translocate nests to avoid disturbance
- No evidence found (no assessment)
3.15 Captive breeding, rearing and releases (ex situ conservation)
- 3.15.1 Captive breeding
- Likely to be beneficial
- Artificially incubate and hand-rear birds in captivity (raptors)
- Artificially incubate and hand-rear birds in captivity (seabirds)
- Artificially incubate and hand-rear birds in captivity (songbirds)
- Artificially incubate and hand-rear birds in captivity (waders)
- Use captive breeding to increase or maintain populations (raptors)
- Unknown effectiveness (limited evidence)
- Artificially incubate and hand-rear birds in captivity (bustards)
- Artificially incubate and hand-rear birds in captivity (cranes)
- Artificially incubate and hand-rear birds in captivity (gamebirds)
- Artificially incubate and hand-rear birds in captivity (parrots)
- Artificially incubate and hand-rear birds in captivity (penguins)
- Artificially incubate and hand-rear birds in captivity (rails)
- Artificially incubate and hand-rear birds in captivity (storks and ibises)
- Artificially incubate and hand-rear birds in captivity (vultures)
- Artificially incubate and hand-rear birds in captivity (wildfowl)
- Freeze semen for artificial insemination
- Use artificial insemination in captive breeding
- Use captive breeding to increase or maintain populations (bustards)
- Use captive breeding to increase or maintain populations (cranes)
- Use captive breeding to increase or maintain populations (pigeons)
- Use captive breeding to increase or maintain populations (rails)
- Use captive breeding to increase or maintain populations (seabirds)
- Use captive breeding to increase or maintain populations (songbirds)
- Use captive breeding to increase or maintain populations (storks and ibises)
- Use captive breeding to increase or maintain populations (tinamous)
- Use puppets to increase the success of hand-rearing
- Wash contaminated semen and use it for artificial insemination
- Evidence not assessed
- Can captive breeding have deleterious effects?
- 3.15.2 Release captive-bred individuals
- Likely to be beneficial
- Provide supplementary food after release
- Release captive-bred individuals into the wild to restore or augment wild populations (cranes)
- Release captive-bred individuals into the wild to restore or augment wild populations (raptors)
- Release captive-bred individuals into the wild to restore or augment wild populations (songbirds)
- Release captive-bred individuals into the wild to restore or augment wild populations (vultures)
- Unknown effectiveness (limited evidence)
- Clip birds’ wings on release
- Release birds as adults or sub-adults not juveniles
- Release birds in groups
- Release captive-bred individuals into the wild to restore or augment wild populations (bustards)
- Release captive-bred individuals into the wild to restore or augment wild populations (gamebirds)
- Release captive-bred individuals into the wild to restore or augment wild populations (owls)
- Release captive-bred individuals into the wild to restore or augment wild populations (parrots)
- Release captive-bred individuals into the wild to restore or augment wild populations (pigeons)
- Release captive-bred individuals into the wild to restore or augment wild populations (rails)
- Release captive-bred individuals into the wild to restore or augment wild populations (storks and ibises)
- Release captive-bred individuals into the wild to restore or augment wild populations (waders)
- Release captive-bred individuals into the wild to restore or augment wild populations (wildfowl)
- Release chicks and adults in ‘coveys’
- Use ‘anti-predator training’ to improve survival after release
- Use appropriate populations to source released populations
- Use ‘flying training’ before release
- Use holding pens at release sites
- Use microlites to help birds migrate
4. FARMLAND CONSERVATION
4.1 All farming systems
- Beneficial
- Create uncultivated margins around intensive arable or pasture fields
- Plant grass buffer strips/margins around arable or pasture fields
- Plant nectar flower mixture/wildflower strips
- Plant wild bird seed or cover mixture
- Provide or retain set-aside areas in farmland
- Likely to be beneficial
- Manage ditches to benefit wildlife
- Manage hedgerows to benefit wildlife (includes no spray, gap-filling and laying)
- Pay farmers to cover the cost of conservation measures (as in agri-environment schemes)
- Provide supplementary food for birds or mammals
- Unknown effectiveness (limited evidence)
- Connect areas of natural or semi-natural habitat
- Increase the proportion of semi-natural habitat in the farmed landscape
- Make direct payments per clutch for farmland birds
- Manage the agricultural landscape to enhance floral resources
- Mark bird nests during harvest or mowing
- Plant new hedges
- Provide nest boxes for bees (solitary bees or bumblebees)
- Provide nest boxes for birds
- Provide other resources for birds (water, sand for bathing)
- Provide refuges during harvest or mowing
- No evidence found (no assessment)
4.2 Arable farming
- Beneficial
- Create skylark plots
- Leave cultivated, uncropped margins or plots (includes ‘lapwing plots’)
- Likely to be beneficial
- Create beetle banks
- Leave overwinter stubbles
- Reduce tillage
- Undersow spring cereals, with clover for example
- Unknown effectiveness (limited evidence)
- Convert or revert arable land to permanent grassland
- Create rotational grass or clover leys
- Increase crop diversity
- Plant cereals in wide-spaced rows
- Plant crops in spring rather than autumn
- Plant nettle strips
- Sow rare or declining arable weeds
- No evidence found (no assessment)
- Evidence not assessed
- Implement ‘mosaic management’, a Dutch agri-environment option
- Plant more than one crop per field (intercropping)
- Take field corners out of management
4.4 Livestock farming
- Beneficial
- Restore or create species-rich, semi-natural grassland
- Use mowing techniques to reduce mortality
- Likely to be beneficial
- Delay mowing or first grazing date on grasslands
- Leave uncut strips of rye grass on silage fields
- Maintain species-rich, semi-natural grassland
- Maintain traditional water meadows (includes management for breeding and/or wintering waders/waterfowl)
- Maintain upland heath/moorland
- Reduce management intensity on permanent grasslands (several interventions at once)
- Restore or create traditional water meadows
- Unknown effectiveness (limited evidence)
- Add yellow rattle seed Rhinanthus minor to hay meadows
- Employ areas of semi-natural habitat for rough grazing (includes salt marsh, lowland heath, bog, fen)
- Exclude livestock from semi-natural habitat (including woodland)
- Maintain wood pasture and parkland
- Plant cereals for whole crop silage
- Raise mowing height on grasslands
- Restore or create upland heath/moorland
- Restore or create wood pasture
- Use traditional breeds of livestock
- Likely to be ineffective or harmful
- Reduce grazing intensity on grassland (including seasonal removal of livestock)
- No evidence found (no assessment)
- Evidence not assessed
- Create open patches or strips in permanent grassland
- Provide short grass for birds
- Use mixed stocking
4.6 Threat: Agri-chemicals
- Beneficial
- Leave headlands in fields unsprayed (conservation headlands)
- Reduce fertilizer, pesticide or herbicide use generally
- Use organic rather than mineral fertilizers
- Likely to be beneficial
- Reduce chemical inputs in grassland management
- Unknown effectiveness (limited evidence)
- Provide buffer strips alongside water courses (rivers and streams)
- Restrict certain pesticides
- No evidence found (no assessment)
- Evidence not assessed
- Make selective use of spring herbicides
4.8 Threat: Hunting and trapping (for pest control, food or sport)
- Unknown effectiveness (limited evidence)
- Enforce legislation to protect birds against persecution
- Provide ‘sacrificial’ grasslands to reduce the impact of wild geese on crops
- No evidence found (no assessment)
- Evidence not assessed
- Use scaring devices (e. g. gas guns) and other deterrents to reduce persecution of native species
4.9 Threat: Natural system modification
- Likely to be beneficial
- Raise water levels in ditches or grassland
- Unknown effectiveness (limited evidence)
- Create scrapes and pools
- Manage heather by swiping to simulate burning
- Manage heather, gorse or grass by burning
- Remove flood defence banks to allow inundation
- No evidence found (no assessment)
4.10 Threat: Invasive and other problematic species
- Likely to be beneficial
- Control predatory mammals and birds (foxes, crows, stoats and weasels)
- Unknown effectiveness (limited evidence)
- Control scrub
- Control weeds without damaging other plants in conservation areas
- Protect individual nests of ground-nesting birds
- No evidence found (no assessment)
- Evidence not assessed
- Control bracken
- Control invasive non-native plants on farmland (such as Himalayan balsam, Japanese knotweed)
- Control mink
- Provide medicated grit for grouse
5. FOREST CONSERVATION
5.2 Threat: Agriculture
- 5.2.1 Livestock farming
- Likely to be beneficial
- Use wire fences within grazing areas to exclude livestock from specific forest sections
- Trade-off between benefit and harms
- Prevent livestock grazing in forests
- Unknown effectiveness (limited evidence)
- Reduce the intensity of livestock grazing in forests
- Shorten livestock grazing period or control grazing season in forests
- No evidence found (no assessment)
5.4 Threat: Biological resource use
- 5.4.1 Thinning and wood harvesting
- Beneficial
- Log/remove trees within forests: effects on understory plants
- Likely to be beneficial
- Thin trees within forests: effects on understory plants
- Thin trees within forests: effects on young trees
- Use shelterwood harvest instead of clearcutting
- Trade-off between benefit and harms
- Thin trees within forests: effects on mature trees
- Unknown effectiveness (limited evidence)
- Log/remove trees within forests: effects on young trees
- Use partial retention harvesting instead of clearcutting
- Use summer instead of winter harvesting
- Unlikely to be beneficial
- Remove woody debris after timber harvest
- Likely to be ineffective or harmful
- Log/remove trees within forests: effect on mature trees
- Log/remove trees within forests: effect on effects on nonvascular plants
- Thin trees within forests: effects on non-vascular plants
- No evidence found (no assessment)
- 5.4.2 Harvest forest products
- Unknown effectiveness (limited evidence)
- Adopt certification
- No evidence found (no assessment)
- 5.4.3 Firewood
- No evidence found (no assessment)
5.5 Habitat protection
- 5.5.1 Changing fire frequency
- Trade-off between benefit and harms
- Use prescribed fire: effect on understory plants
- Use prescribed fire: effect on young trees
- Likely to be ineffective or harmful
- Use prescribed fire: effect on mature trees
- No evidence found (no assessment)
- 5.5.2 Water management
- No evidence found (no assessment)
- 5.5.3 Changing disturbance regime
- Trade-off between benefit and harms
- Use clearcutting to increase understory diversity
- Use group-selection harvesting
- Use shelterwood harvesting
- Unknown effectiveness (limited evidence)
- Thin trees by girdling (cutting rings around tree trunks)
- Use herbicides to thin trees
- Unlikely to be beneficial
- Use thinning followed by prescribed fire
- No evidence found (no assessment)
5.6 Threat: Invasive and other problematic species
- 5.6.1 Invasive plants
- Unknown effectiveness (limited evidence)
- Manually/mechanically remove invasive plants
- Use herbicides to remove invasive plant species
- No evidence found (no assessment)
- 5.6.2 Native plants
- No evidence found (no assessment)
- 5.6.3 Herbivores
- Likely to be beneficial
- Use wire fences to exclude large native herbivores
- Unknown effectiveness (limited evidence)
- Use electric fencing to exclude large native herbivores
- No evidence found (no assessment)
- 5.6.4 Rodents
- Unknown effectiveness (limited evidence)
- Control rodents
- 5.6.5 Birds
- Unknown effectiveness (limited evidence)
- Control birds
5.10 Habitat restoration and creation
- 5.10.1 Restoration after wildfire
- Trade-off between benefit and harms
- Thin trees after wildfire
- Unknown effectiveness (limited evidence)
- Remove burned trees
- Likely to be ineffective or harmful
- Sow tree seeds after wildfire
- No evidence found (no assessment)
- 5.10.2 Restoration after agriculture
- Unknown effectiveness (limited evidence)
- Restore wood pasture (e. g. introduce grazing)
- 5.10.3 Manipulate habitat to increase planted tree survival during restoration
- Unknown effectiveness (limited evidence)
- Apply herbicides after restoration planting
- Cover the ground using techniques other than plastic mats after restoration planting
- Cover the ground with plastic mats after restoration planting
- Use selective thinning after restoration planting
- 5.10.4 Restore forest community
- Unknown effectiveness (limited evidence)
- Build bird-perches to enhance natural seed dispersal
- Plant a mixture of tree species to enhance diversity
- Sow tree seeds
- Water plants to preserve dry tropical forest species
- No evidence found (no assessment)
- 5.10.5 Prevent/encourage leaf litter accumulation
- Unknown effectiveness (limited evidence)
- Remove or disturb leaf litter to enhance germination
- No evidence found (no assessment)
- 5.10.6 Increase soil fertility
- Likely to be beneficial
- Use vegetation removal together with mechanical disturbance to the soil
- Trade-off between benefit and harms
- Add organic matter
- Use fertilizer
- Use soil scarification or ploughing to enhance germination
- Unknown effectiveness (limited evidence)
- Add lime to the soil to increase fertility
- Use soil disturbance to enhance germination (excluding scarification or ploughing)
- Likely to be ineffective or harmful
- Enhance soil compaction
5.11 Actions to improve survival and growth rate of planted trees
- Beneficial
- Prepare the ground before tree planting
- Use mechanical thinning before or after planting
- Likely to be beneficial
- Fence to prevent grazing after tree planting
- Use herbicide after tree planting
- Trade-off between benefit and harms
- Use prescribed fire after tree planting
- Unknown effectiveness (limited evidence)
- Apply insecticide to protect seedlings from invertebrates
- Add lime to the soil after tree planting
- Add organic matter after tree planting
- Cover the ground with straw after tree planting
- Improve soil quality after tree planting (excluding applying fertilizer)
- Manage woody debris before tree planting
- Use shading for planted trees
- Use tree guards or shelters to protect planted trees
- Use weed mats to protect planted trees
- Water seedlings
- Unlikely to be beneficial
- Mechanically remove understory vegetation after tree planting
- Use different planting or seeding methods
- Use fertilizer after tree planting
- No evidence found (no assessment)
6. SOME ASPECTS OF CONTROL OF FRESHWATER INVASIVE SPECIES
6.1 Threat: Invasive plants
- 6.1.1 Floating pennywort Hydrocotyle ranunculoides
- Beneficial
- Chemical control using herbicides
- Likely to be beneficial
- Flame treatment
- Physical removal
- Unknown effectiveness (limited evidence)
- Combination treatment using herbicides and physical removal
- Unlikely to be beneficial
- Biological control using co-evolved, host-specific herbivores
- Use of hydrogen peroxide
- No evidence found (no assessment)
- 6.1.2 Water primrose Ludwigia spp
- Likely to be beneficial
- Biological control using co-evolved, host specific herbivores
- Chemical control using herbicides
- Combination treatment using herbicides and physical removal
- Unlikely to be beneficial
- Physical removal
- No evidence found (no assessment)
- 6.1.3 Skunk cabbage Lysichiton americanus
- Likely to be beneficial
- Chemical control using herbicides
- Physical removal
- No evidence found (no assessment)
- 6.1.4 New Zealand pigmyweed Crassula helmsii
- Beneficial
- Chemical control using herbicides
- Decontamination to prevent further spread
- Likely to be beneficial
- Use lightproof barriers to control plants
- Use salt water to kill plants
- Unknown effectiveness (limited evidence)
- Use a combination of control methods
- Unlikely to be beneficial
- Use dyes to reduce light levels
- Use grazing to control plants
- Use hot foam to control plants
- Use hydrogen peroxide to control plants
- No evidence found (no assessment)
6.3 Threat: Invasive crustaceans
- 6.3.1 Ponto-Caspian gammarids
- Likely to be beneficial
- Change salinity of the water
- Change water temperature
- Dewatering (drying out) habitat
- Exposure to parasites
- Unlikely to be beneficial
- Add chemicals to water
- Change water pH
- Control movement of gammarids
- No evidence found (no assessment)
- 6.3.2 Procambarus spp. crayfish
- Likely to be beneficial
- Add chemicals to the water
- Sterilization of males
- Trapping and removal
- Trapping combined with encouragement of predators
- Unknown effectiveness (limited evidence)
- Create barriers
- Unlikely to be beneficial
- Encouraging predators
- No evidence found (no assessment)
7. SOME ASPECTS OF ENHANCING NATURAL PEST CONTROL
7.2 All farming systems
- Likely to be beneficial
- Grow non-crop plants that produce chemicals that attract natural enemies
- Use chemicals to attract natural enemies
- Trade-off between benefit and harms
- Leave part of the crop or pasture unharvested or uncut
- Unknown effectiveness (limited evidence)
- Plant new hedges
- Use alley cropping
- Evidence not assessed
- Use mass-emergence devices to increase natural enemy populations
7.3 Arable farming
- Beneficial
- Combine trap and repellent crops in a push-pull system
- Trade-off between benefit and harms
- Use crop rotation in potato farming systems
- Unlikely to be beneficial
- Create beetle banks
- Likely to be ineffective or harmful
- Incorporate plant remains into the soil that produce weed-controlling chemicals
8. ENHANCING SOIL FERTILITY
8.3 Arable farming
- Beneficial
- Amend the soil using a mix of organic and inorganic amendments
- Grow cover crops when the field is empty
- Use crop rotation
- Likely to be beneficial
- Amend the soil with formulated chemical compounds
- Grow cover crops beneath the main crop (living mulches) or between crop rows
- Trade-off between benefit and harms
- Add mulch to crops
- Amend the soil with fresh plant material or crop remains
- Amend the soil with manures and agricultural composts
- Amend the soil with municipal wastes or their composts
- Incorporate leys into crop rotation
- Retain crop residues
- Unknown effectiveness (limited evidence)
- Amend the soil with bacteria or fungi
- Amend the soil with composts not otherwise specified
- Amend the soil with crops grown as green manures
- Amend the soil with non-chemical minerals and mineral wastes
- Amend the soil with organic processing wastes or their composts
- Encourage foraging waterfowl
- Use alley cropping