Conservation Evidence: Evidence Data

Collected Evidence: Collected Evidence: Delay mowing or first grazing date on pasture or grassland Eight studies from the Netherlands, Sweden and the UK (three replicated and controlled of which one also randomized and one European systematic review) found that delaying mowing or grazing dates resulted in benefits to some or all plants, invertebrates or birds studied. These benefits included: higher plant species richness, higher densities of two rare arable weeds, more insect species and individuals visiting flowers, greater abundance of some spiders and ground beetles, increased breeding wading bird densities, and increased Eurasian skylark productivity. Three reviews found the UK corncrake population increased after measures including delaying mowing dates were introduced. Six studies from Finland, the Netherlands, Sweden, Switzerland and the UK (including three replicated controlled trials of which one was also randomized and a European systematic review) found that delaying mowing or grazing dates on grassland had no clear effect on plant species richness, ground beetle communities, abundance of some insects and spiders, or population trends of wading bird species. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F131https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F131Mon, 14 Nov 2011 22:17:17 +0000Collected Evidence: Collected Evidence: Plant grass buffer strips/margins around arable or pasture fields for birds One replicated controlled study from the USA found that there were more species in fields bordered by margins than unbordered fields. Two replicated studies from the UK, one with paired sites, found no effect of field margins on species richness. A replicated, controlled study from the UK found that more birds and more species used sown strips in fields than the fields themselves, but even more used field margins. Nine studies from the UK and USA, seven replicated, two controlled, found more positive population trends, higher populations or strong habitat associations for some or all species for sites with grass margins to fields. One study investigated multiple interventions. Three replicated studies from the UK found that grass field margins did not have a positive effect on populations of some or all bird species investigated. Both studies that examined habitat use (one replicated, both from the UK) found that species used margins more than other habitats. A randomised, replicated and controlled study from the UK found that birds used cut margins more than uncut margins during winter but less than other management regimes during summer. The authors argue that management type is more important than the seed mix used to sow the margins. A replicated study from the UK found that grey partridge Perdix perdix had smaller broods in grass margins than other habitat types. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F191https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F191Wed, 27 Jun 2012 16:39:04 +0100Collected Evidence: Collected Evidence: Use chemicals to attract natural enemiesParasitism and predation (by natural enemies): One review and two of five studies from Asia, Europe and North America found that attractive chemicals increased parasitism. Two studies, including one randomised, replicated, controlled trial, found greater parasitism for some but not all chemicals, crops, sites or years and one study found no effect. One study showed that parasites found pests more rapidly. One study found lower egg predation by natural predators. Natural enemies: Five of 13 studies from Africa, Asia, Australasia, Europe and North America found more natural enemies while eight (including seven randomised, replicated, controlled trials) found positive effects varied between enemy groups, sites or study dates. Four of 13 studies (including a meta-analysis) found more natural enemies with some but not all test chemicals. Two of four studies (including a review) found higher chemical doses attracted more enemies, but one study found lower doses were more effective and one found no effect. Pests: Three of nine studies (seven randomised, replicated, controlled) from Asia, Australasia, Europe and North America found fewer pests, although the effect occurred only in the egg stage in one study. Two studies found more pests and four found no effect. Crop damage: One study found reduced damage with some chemicals but not others, and one study found no effect. Yield: One study found higher wheat yields. Crops studied were apple, banana, bean, broccoli, Chinese cabbage, cotton, cowpea, cranberry, grape, grapefruit, hop, maize, oilseed, orange, tomato, turnip and wheat.Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F754https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F754Thu, 08 Aug 2013 13:40:59 +0100Collected Evidence: Collected Evidence: Restore ponds Fifteen studies investigated the effectiveness of pond restoration for amphibians. One replicated, before-and-after study in Denmark found that pond restoration had mixed effects on European tree frog population numbers depending on site. One replicated, controlled, before-and-after study in the UK found that pond restoration did not increase great crested newt populations. Six replicated, before-and-after studies (including one controlled and one site comparison study) in Denmark, Estonia, Italy and the UK found that pond restoration and creation increased numbers of amphibian species, maintained or increased populations, or increased pond occupancy and ponds with breeding success. One found that numbers of species did not increase. Two before-and-after studies (including one replicated study) in Estonia found that pond restoration, along with terrestrial habitat management, maintained or increased populations of natterjack toads. One systematic review in the UK found that there was no conclusive evidence that mitigation, which often included pond restoration, resulted in self-sustaining great crested newt populations. One small, replicated study in the USA found that pond restoration had mixed effects on spotted salamander hatching success depending on restoration method. One replicated, before-and-after study in the UK found that restoration increased the number of ponds used by breeding natterjack toads. One replicated study in Sweden found that following restoration green toads only reproduced in one of 10 ponds. Three before-and-after studies (including one replicated, controlled study) in Denmark and Italy found that restored and created ponds were colonized by 1–7 species, with 6–65% of ponds colonized and 35% used for breeding. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F878https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F878Thu, 12 Sep 2013 15:17:02 +0100Collected Evidence: Collected Evidence: Create wetland Fifteen studies investigated the effectiveness of creating wetlands for amphibians. Five site comparison studies (including four replicated studies) in the USA compared created to natural wetlands and found that created wetlands had similar numbers of amphibian species, amphibian abundance or communities depending on depth as natural wetlands. Two of the studies found that created wetlands had fewer amphibian species or lower abundance and different communities compared to natural wetlands. One site comparison study in the USA found that created wetlands had similar numbers of species to adjacent forest. One global review and two site comparison studies (including one replicated study) in the USA combined created and restored wetlands and compared them to natural wetlands and found that numbers of amphibian species and abundance was higher or similar, or higher in 54% of studies and similar in 35% of studies reviewed compared to natural wetlands. Three site comparison studies (including one replicated study) in the USA found that certain amphibian species were only found in created or natural wetlands. One before-and-after study in Australia found that captive-bred green and golden bell frog tadpoles released into a created wetland did not establish a self-sustaining population. Five studies (including two replicated studies) in Kenya and the USA that investigated colonization of created wetlands found that four to 15 amphibian species used or colonized the wetlands. One global review and three studies (including two replicated studies) in the USA found that numbers of amphibian species and amphibian abundance in created wetlands were affected by wetland design, vegetation, water levels, surrounding habitat, fish presence and distance to source wetlands. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F880https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F880Fri, 13 Sep 2013 11:16:59 +0100Collected Evidence: Collected Evidence: Amend the soil with manures and agricultural compostsBiodiversity loss: Three controlled, replicated studies from the UK and USA found higher microbial biomass when manure or compost was applied, and higher microbial respiration when poultry manure was applied. Erosion: One controlled, randomized, replicated study from India found lower soil loss and water runoff with manure application in combination with other treatments. Nutrient management: Four studies from Canada, Spain, the UK and the USA measured the effect of a variety of manure types on soil nutrient levels. Of these, three randomized, replicated studies (two also controlled) found reduced nutrient loss and higher nitrogen levels when farmyard or poultry manure was applied. One also found lower nutrient loss when farmyard manure (rather than poultry manure or slurry) was applied in winter rather than autumn. One controlled replicated study found higher nitrate leaching. Soil organic carbon: Four studies (including three controlled, replicated studies (one also randomized) and a review) from India, Japan and the UK found higher carbon levels when manures were applied. Soil organic matter: One controlled, randomized, replicated study from Turkey found higher organic matter, larger soil aggregations and a positive effect on soil physical properties when manure and compost were applied. Two studies from Denmark and Germany found no effect of manure on organic matter levels. Yield: Four controlled, replicated studies (including three also randomized) from India, Spain and Turkey found higher crop yields when manures or compost were applied. One study found higher yields when manure were applied in combination with cover crops. Soil types covered: Clay loam, fine sandy-silty loam, loam, loamy, sandy loam, sandy clay loam, silty loam, and sandy silt loam. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F911https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F911Thu, 03 Oct 2013 11:10:07 +0100Collected Evidence: Collected Evidence: Use prescribed burning Fifteen studies evaluated the effects of prescribed burning on bat populations. Thirteen studies were in the USA and two were in Australia. COMMUNITY RESPONSE (2 STUDIES) Community composition (2 studies): One of two replicated studies (one before-and-after with paired sites, one site comparison) in Australia found that the composition of bat species differed between burned and unburned woodland sites. The other study found that the composition of bat species was similar between unlogged forest blocks burned every two or four years and unburned blocks. Richness/diversity (1 study): One replicated, randomized, site comparison study in Australia found more bat species in unlogged forest blocks burned every four years than in blocks burned every two years or unburned blocks. POPULATION RESPONSE (9 STUDIES) Abundance (9 studies): Two replicated, site comparison studies (including one controlled study) in the USA found that the activity (relative abundance) of open habitat bat species and evening bats increased with the number of prescribed fires, but there was no effect on other bat species, including cluttered habitat bat species. Four replicated, before-and-after or site comparison studies (including two controlled studies) in the USA and Australia found that prescribed burning, prescribed burning along with thinning or prescribed burning every four years resulted in higher overall bat activity or activity of Florida bonneted bats. One site comparison study in the USA found that two of seven sites that had been burned alongside other restoration practices had higher bat activity than unrestored sites. One replicated, randomized, site comparison study in the USA found that three of four burning and thinning treatments resulted in higher overall bat activity. One replicated, controlled, site comparison study in the USA found similar activity of three bat species in burned and unburned tree stands. BEHAVIOUR (6 STUDIES) Use (5 studies): One replicated, controlled before-and-after study in the USA found that more female northern myotis bats roosted in burned than unburned forest. Two replicated, controlled, site comparison studies in the USA found that fewer female northern myotis bats and male Indiana bats roosted in burned than unburned forest. One replicated study in the USA found that evening bats roosted in burned but not unburned forest. One replicated, paired sites study in the USA found that burned sites had a higher occupancy of five bat species/species groups than unburned sites, and burn severity had a negative effect on the occupancy of two bat species/species groups. Behaviour change (4 studies): Two replicated, controlled, site comparison studies in the USA found no difference in roost switching frequency or the distance between roost trees for female northern myotis bats and male Indiana bats in burned and unburned forests. One replicated, controlled, before-and-after study in the USA found that female northern myotis home ranges and core areas did not differ in size between burned and unburned forests, but home ranges were closer to burned forest than unburned forest. One replicated, site comparison study in the USA found that home ranges of female Rafinesque’s big-eared bats were located similar distances to burned and unburned forest, and male home ranges were closer to unburned forest. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1006https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1006Fri, 20 Dec 2013 17:26:46 +0000Collected Evidence: Collected Evidence: Crop production: Plant or maintain ground cover in orchards or vineyardsCrop yield (11 studies) Grapes (8 studies): Two replicated, randomized, controlled studies from France and the USA found lower grape yields in plots that were seeded with grass between the vine rows, compared to plots with bare soil between the vine rows, in some or all comparisons. Six replicated, randomized, controlled studies from Italy, Portugal, Spain, and the USA found similar grape yields in plots with or without ground cover between the vine rows. Other crops (3 studies): Two replicated, randomized, controlled studies from Portugal found higher chestnut yields in plots with resident vegetation, compared to plots without ground cover, but found no difference in chestnut yields between plots with seeded cover crops and plots without ground cover. One of these studies also found higher mushroom yields in plots with resident vegetation, compared to plots without ground cover. One replicated, randomized, controlled study from Chile found lower avocado yields in plots that were seeded with grasses and legumes, compared to plots with bare soil. Crop quality (8 studies) Grapes (6 studies): Five replicated, randomized, controlled studies from Italy, Portugal, and the USA found similar sugar contents in grapes with or without ground cover between the vine rows. Three of these studies found similar pH levels, and two of these studies found no differences in titratable acidity, but two of these studies found lower titratable acidity in grapes with ground cover between the vine rows. One replicated, randomized, controlled study from the USA found heavier grapes with ground cover between the vine rows, but two replicated, randomized, controlled studies from Italy and Spain did not. Two replicated, randomized, controlled studies from Portugal and Spain found other differences in grape quality with ground cover between the vine rows. Other crops (2 studies): One replicated, randomized, controlled study from Portugal found larger chestnuts in plots with ground cover, compared to plots without ground cover. One replicated, randomized, controlled study from Chile found no difference in avocado quality in plots with or without ground cover. Implementation options (6 studies) Ground cover (5 studies) Grapes (3 studies): One replicated, randomized, controlled study from the USA found similar grape yields in plots with different types of ground cover. However, this study found lighter-weight clusters of grapes in plots with seeded cover crops, compared to resident vegetation, in one of three years, and found inconsistent differences in cluster weights between plots with different types of seeded cover crops. Two replicated, randomized, controlled studies from Spain and the USA found other differences in grape quality between plots with different types of ground cover. Other crops (2 studies): Two replicated, randomized, controlled studies from Portugal found lower chestnut yields in plots with seeded cover crops, compared to resident vegetation. One of these studies also found smaller chestnuts and lower mushroom yields. Tillage (2 studies): One replicated, randomized, controlled study from the USA found higher grape yields, and heavier grape clusters, in plots without tillage between the vine rows, in one of six comparisons. Another replicated, randomized, controlled study from the USA found similar grape yields, with or without tillage between the vine rows. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1352https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1352Thu, 23 Mar 2017 09:24:58 +0000Collected Evidence: Collected Evidence: Soil: Add slurry to the soilOrganic matter (4 studies): Three studies (two replicated, randomized, controlled; one meta-analysis) from Spain and multiple Mediterranean countries found similar amounts of organic matter in soils with or without added slurry. One replicated, randomized, controlled study from Spain found more organic matter in soils with added slurry, compared to soils without it, in some comparisons. Nutrients (4 studies): Two replicated, randomized, controlled studies from Spain found more nitrate in soils with added slurry, compared to soils without it. Two replicated, randomized, controlled studies from Portugal and Spain found similar amounts of nitrate in soils with or without added slurry. One of these studies also found more ammonium, but another one did not. Soil organisms (2 studies): One replicated, randomized, controlled study from Spain found more microbial biomass in soils with added slurry, compared to soils without it, but another one did not. Soil erosion and aggregation (1 study): One replicated, randomized, controlled study from Spain found more stable soils in plots with added slurry, compared to plots without it, in some comparisons. Greenhouse gases (8 studies) Carbon dioxide (3 studies): Of three replicated, randomized, controlled studies from Spain, two studies found higher carbon dioxide emissions in soils with added slurry, compared to soils without it, but one study did not. Methane (4 studies): One replicated, randomized, controlled study from Spain found that less methane was absorbed by soils with added slurry, compared to soils without it. Three replicated, randomized, controlled studies from Spain found similar methane fluxes in soils with or without added slurry. Nitrous oxide (6 studies): Five replicated, randomized, controlled studies from Spain found higher nitrous oxide emissions in soils with added slurry, compared to soils without it, in some or all comparisons. One replicated, randomized, controlled study from Spain found similar nitrous oxide emissions in soils with or without added slurry. Implementation options (3 studies): One replicated, randomized, controlled study from Spain found no differences in organic matter or greenhouse-gas emissions between plots with different amounts of slurry. One replicated, randomized, controlled study from Spain found similar amounts of nitrogen in soils with or without added slurry. One replicated, randomized, controlled study from Spain found similar nitrous oxide emissions in soils with digested or untreated pig slurry. One replicated, randomized, controlled study from Spain found similar carbon dioxide and methane emissions in soils with digested or untreated slurry.Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1365https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1365Tue, 09 May 2017 14:27:06 +0100Collected Evidence: Collected Evidence: Soil: Use crop rotationsOrganic matter (9 studies): Five replicated, controlled studies (two randomized) from Italy, Portugal, and Spain found less organic matter in soils with crop rotations, compared to continuous crops, in some comparisons. One replicated, controlled study from Syria found more organic matter in soils with crop rotations, compared to continuous crops, in some comparisons. Three replicated, controlled studies from Spain found similar amounts of organic matter in soils with or without crop rotations. Nutrients (5 studies) Nitrogen (5 studies): One replicated, randomized, controlled study from Australia found more nitrogen in soils with crop rotations, compared to continuous crops, in one of four comparisons. One replicated, controlled study from Italy found less nitrogen in soils with crop rotations, compared to continuous crops, in some comparisons. One replicated, randomized, controlled study from Spain found inconsistent differences in nitrogen in soils with or without crop rotations. Two replicated, randomized, controlled studies from Portugal and Spain found similar amounts of nitrogen in soils with or without crop rotations. Phosphorus (2 studies): Two replicated, randomized, controlled studies from Portugal and Spain found less phosphorus in soils with crop rotations, compared to continuous crops, in some comparisons. pH (2 studies): Two replicated, randomized, controlled studies from Portugal and Spain found similar pH levels in soils with or without crop rotations. Soil organisms (3 studies) Microbial biomass (2 studies): One replicated, controlled study from Italy found more microbial biomass in soils with crop rotations, compared to continuous crops, in some comparisons. One replicated, randomized, controlled study from Spain found less microbial biomass in soils with crop rotations, compared to continuous crops, in some comparisons. Bacteria and fungi (1 study): One replicated, randomized, controlled study from Portugal found more fungi, but similar amounts of bacteria, in soils with crop rotations, compared to continuous crops. Soil erosion and aggregation (4 studies): One replicated, controlled study from Syria found higher water-stability in soils with crop rotations, compared to continuous crops. One replicated, randomized, controlled study from Spain found lower water-stability in soils with crop rotations, compared to continuous crops, in some comparisons. One replicated, randomized, controlled study from Spain found inconsistent differences in water-stability in soils with or without crop rotations. One replicated, randomized, controlled study from Spain found no differences in water-stability. Greenhouse gases (4 studies): One replicated, controlled study from Italy found higher carbon dioxide emissions from soils with crop rotations, compared to continuous crops, in some comparisons. One replicated, randomized, controlled study from Spain found similar carbon dioxide emissions from soils with or without crop rotations. One replicated, randomized, controlled study from Australia found lower nitrous oxide and methane emissions from soils with crop rotations, compared to continuous crops, but another one found no differences in nitrous oxide emissions. Implementation options (2 studies): Two studies from Syria and the USA found similar amounts of nitrogen in soils with two-year or four-year rotations. One of these studies also found similar amounts of organic matter.Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1368https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1368Mon, 15 May 2017 14:21:47 +0100Collected Evidence: Collected Evidence: Reintroduce primates into habitat with predators Two before-and-after studies in Brazil found that most golden lion tamarins reintroduced into habitat with predators, alongside other interventions, did not survive over one to seven years but reproduced succesfully. Three studies, including two before-and-after studies, in the Congo, The Gambia and Guinea, found that most chimpanzees reintroduced into habitat with predators, alongside other interventions, survived over one to five years or increased population numbers. One before-and-after study in Gabon found that most western lowland gorillas reintroduced into habitat with predators, alongside other interventions, survived over nine months. One before-and-after study in Madagascar found that most black-and-white ruffed lemurs reintroduced into habitat with predators did not survive over five years. One study in Madagascar found that all reintroduced lemurs survived over 30 months after being released into habitat with predators, along with other interventions. One study in Gabon found that most mandrills reintroduced into habitat with predators, alongside other interventions, survived over 30 years. Two before-and-after studies in South Africa found that most vervet monkeys reintroduced into habitat with predators, alongside other interventions, survived over six months. Two studies, including one before-and-after study, in Vietnam and Indonesia found that most lorises reintroduced into habitat with predators, alongside other interventions, were assumed dead within approximately one year after being released. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1593https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1593Fri, 20 Oct 2017 14:16:39 +0100Collected Evidence: Collected Evidence: Sow seeds Five of six studies (including three replicated, randomized, controlled studies, one site comparison study and one controlled study) in the UK, South Africa, and the USA found that sowing seeds of shrubland species increased shrub cover. One of six studies in the UK found no increase in shrub cover. One replicated site comparison in the USA found in sites where seed containing Wyoming big sagebrush was sown the abundance of the plant was higher than in sites where it was not sown. One replicated, randomized, controlled study in the USA found that shrub seedling abundance increased after seeds were sown. One study in the USA found very low germination of hackberry seeds when they were sown. One replicated, randomized, controlled study in the USA found that the community composition of shrublands where seeds were sown was similar to that found in undisturbed shrublands. One randomized, controlled study in the UK found an increase in the cover of heathland plants when seeds were sown. One replicated, randomized, controlled study in South Africa found that sowing seeds increased plant cover. One replicated, randomized, controlled study in the USA found that areas where seeds were sown did not differ significantly in native cover compared to areas where shrubland plants had been planted. One controlled study in the USA found higher plant diversity in areas where seeds were sown by hand than in areas where they were sown using a seed drill. Two of three studies (one of which was a replicated, randomized, controlled study) in the USA found that sowing seeds of shrubland species resulted in an increase in grass cover. One randomized, controlled study in the UK found no changes in the cover of grasses or forbs. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1698https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1698Mon, 23 Oct 2017 11:05:08 +0100Collected Evidence: Collected Evidence: Parrot’s feather: Use of herbicides - other herbicides One replicated, controlled laboratory study in New Zealand found that the application of dichlobenil reduced the growth of parrot’s feather. Two replicated, randomized, controlled field studies in Portugal and New Zealand found that the application of dichlobenil reduced cover less than the combined application of the herbicides 2,4-D and MCPA eight days after treatment but not 45 days after treatment and that plants treated with dichlobenil presented lower vegetation cover soon after herbicide application but cover later increased to levels close to pre-treatment. Three laboratory studies (including two replicated, controlled studies and one randomized, controlled study) in the USA found that the herbicides imazamox and imazapyr reduced the growth of parrot’s feather. One replicated, randomized, controlled field study in Portugal and one replicated, controlled, laboratory study in the USA reported reduced parrot’s feather biomass after treatment with glyphosate. One replicated, randomized, controlled field study in Portugal found that the application of gluphosinate-ammonium reduced the biomass of parrot’s feather. Three replicated, controlled laboratory studies in New Zealand and the USA found that treatment with fluridone, clopyralid and copper chelate did not reduce growth of parrot’s feather. One replicated, controlled laboratory study in the USA found that the application of flumioxazin reduced the growth of parrot’s feather. One replicated, randomized, controlled laboratory study in the USA found that the application of florpyrauxifen-benzyl reduced the growth of parrot’s feather. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1699https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1699Mon, 23 Oct 2017 11:11:47 +0100Collected Evidence: Collected Evidence: Cut/mow herbaceous plants to maintain or restore disturbance Fourteen studies evaluated the effects on peatland vegetation of cutting/mowing to maintain or restore disturbance. All 14 studies were in fens or fen meadows. Most studies examined the effect of annual mowing regimes, but three examined the effect of single cuts. N.B. Cutting/mowing in peatlands with no history of disturbance is considered as a separate action. Plant community composition (7 studies): Six replicated studies in fens and fen meadows in the UK, Belgium, Germany and the Czech Republic reported that mowing altered the overall plant community composition (compared to no mowing, before mowing or grazing). One site comparison study in Poland reported that mowing a degraded fen (along with other interventions) made the plant community more similar to a target fen meadow. Characteristic plants (5 studies): Four studies (including one replicated, paired, controlled, before-and-after) in fens and fen meadows in Switzerland, Germany, the Czech Republic and Poland found that cutting/mowing increased cover of fen- or wet meadow-characteristic plants. One replicated before-and-after study in fens in the UK found that a single mow typically had no effect on cover of fen-characteristic plants. In Poland and the UK, the effect of mowing was not separated from the effects of other interventions. Moss cover (6 studies): Of six studies (five replicated, paired, controlled) in fens or fen meadows, four in Belgium, Switzerland and the Czech Republic found that mowing increased total moss or bryophyte cover. Two studies in Poland and the UK found that a single mow typically had no effect on bryophyte cover (total or hollow-adapted mosses). Herb cover (8 studies): Six replicated studies (three also randomized and controlled) in fens and fen meadows in Belgium, Germany, Poland and the UK found that mowing reduced cover or abundance of at least one group of herbs (including bindweed, reeds, sedges, purple moor grass and grass-like plants overall). One before-and-after study in a fen in Poland found that mowing (along with other interventions) increased sedge cover. One replicated, randomized, paired, controlled study in fen meadows in Switzerland found that mowing had no effect on overall herb cover. Tree/shrub cover (3 studies): Of three replicated studies in fens, two in the UK found that a single mow (sometimes along with other interventions) reduced shrub cover. However, one study in Poland found that a single mow had no effect on shrub cover. Vegetation structure (7 studies): In the following studies, vegetation structure was measured 6–12 months after the most recent cut/mow. Three replicated studies in fens in Poland and the UK reported that a single mow (sometimes along with other interventions) had no, or no consistent, effect on vegetation height. One replicated, paired, site comparison study in fen meadows in Switzerland found that mowing reduced vegetation height. Three studies (including two replicated, paired, site comparisons) in fen meadows in Switzerland, Poland and Italy found mixed effects of mowing on vegetation biomass (total, sedge/rush, moss or common reed). One replicated, paired, site comparison study in Germany reported that mown fen meadows had similar vegetation structure to grazed meadows. Overall plant richness/diversity (11 studies): Eight studies in fens and fen meadows in the UK, Belgium, Switzerland, Germany, the Czech Republic and Poland found that mowing/cutting increased plant species richness (compared to no mowing, before mowing or grazing). Three studies (including two replicated, randomized, paired, controlled) in fens in Poland and the UK found that a single mow (sometimes along with other interventions) typically had no effect on plant species richness and/or diversity. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1759https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1759Mon, 27 Nov 2017 21:35:31 +0000Collected Evidence: Collected Evidence: Release captive-bred mammals into fenced areas Fourteen studies evaluated the effects of releasing captive-bred mammals into fenced areas. Nine studies were in Australia and one each was in Jordan, South Africa, the USA, Saudi Arabia and Senegal. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (14 STUDIES) Abundance (5 studies): Four studies (one replicated) and a review in Australia, Jordan and Senegal found that after releasing captive-bred animals into fenced areas, a population of burrowing bettongs increased, a population of Arabian oryx increased six-fold in 12 years, a population of dorcas gazelle almost doubled over four years, three populations of eastern barred bandicoot initially increased and abundance of eastern barred bandicoots increased. Reproductive success (6 studies): Four studies and a review in South Africa, Australia, Saudi Arabia and Senegal found that following release of captive-bred animals into fenced areas (in some cases with other associated management), African wild dogs, three populations of eastern barred bandicoot, dorcas gazelle and most female black-footed rock-wallabies reproduced, and Arabian gazelles started breeding in the year following the first releases. A study in Australia found that four of five mammal populations released into a predator-free enclosure and one released into a predator-reduced enclosure reproduced, whereas two populations released into an unfenced area with ongoing predator management did not survive to reproduce. Survival (10 studies): A study in Australia found that four of five mammal populations released into a predator-free enclosure and one population released into a predator-reduced enclosure survived, whereas two populations released into an unfenced area with ongoing predator management did not. Six studies (one controlled before-and-after study and two replicated studies) in Australia and the USA found that following release of captive-bred animals into fenced areas (in some cases with other associated management), a burrowing bettong population, three eastern barred bandicoot populations and over half of black-footed rock-wallabies survived between one and eight years, most captive-bred hare-wallabies survived at least two months, at least half of black-footed ferrets survived more than two weeks, and bandicoots survived at five of seven sites up to three years after the last release. One study in Australia found that following release into fenced areas, a captive-bred population of red-tailed phascogales survived for less than a year. A study in South Africa found that captive-bred African wild dogs released into fenced reserves in family groups had high survival rates. A randomized, controlled study in Australia found that captive-bred eastern barred bandicoots released into a fenced reserve after time in holding pens had similar post-release survival compared to bandicoots released directly from captivity. Condition (1 study): A randomized, controlled study in Australia found that captive-bred eastern barred bandicoots released into a fenced reserve after time in holding pens had similar post-release body weight compared to those released directly from captivity. BEHAVIOUR (0 STUDIES)Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2521https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2521Mon, 08 Jun 2020 09:55:37 +0100Collected Evidence: Collected Evidence: Facilitate tidal exchange to restore/create brackish/salt marshes from other land uses Fourteen studies evaluated the effects, on vegetation, of facilitating tidal exchange to restore/create brackish/salt marshes from other land uses or habitat types. Seven studies were in the UK. Five studies were in the USA. There was one study in each of Australia and the Netherlands. There was overlap in the sites used in four of the studies. VEGETATION COMMUNITY Overall extent (3 studies): Three before-and-after studies in Australia, the UK and the Netherlands reported increases in the overall extent of salt marsh vegetation over 3–10 years after restoring tidal exchange. Community types (3 studies): One replicated, paired, site comparison study in the UK reported that restored marshes, developing after 2–13 years of tidal exchange, contained a different type of salt marsh plant community to natural marshes in four of four cases. Two before-and-after studies in the UK and the Netherlands reported increases in the frequency or coverage of salt marsh plant communities after restoring tidal exchange, reaching 93–100% after 9–10 years. Community composition (4 studies): Four site comparison studies (two replicated, one paired) in the UK and the USA reported that after facilitating tidal exchange on freshwater wetlands or farmland, the overall plant community composition remained somewhat different from natural brackish/salt marshes for up to 30 years. Three of the studies reported increasing community similarity to natural marshes over 11–30 years of tidal exchange. Overall richness/diversity (6 studies): Two site comparison studies of brackish/salt marshes in the USA and the UK reported that overall plant species richness was similar in marshes developing after 4–11 years of tidal exchange, and in nearby natural marshes. Two site comparison studies (one replicated) of salt marshes in the UK reported that marshes developing after 1–14 years of tidal exchange (sometimes along with other interventions) had lower plant species richness or diversity than nearby natural marshes. Two before-and-after studies in the UK compared the number of plant/algae species present in salt marshes that developed over 1–9 years after restoring tidal exchange to the number of plant species present before intervention. In one study there were more species after intervention, but in the other study there were fewer. Characteristic plant richness/diversity (2 studies): One replicated, site comparison study of salt marshes in the UK reported that marshes developing after 1–14 years of tidal exchange contained a similar number of salt-tolerant plant species to natural marshes. One before-and-after study in the Netherlands reported that all 23 target brackish/salt marsh species were present in the study site 10 years after restoring regular tidal exchange: more than were present before restoration. VEGETATION ABUNDANCE Overall abundance (6 studies): Two site comparison studies (one replicated) of salt marshes in the UK reported that marshes developing after 1–14 years of tidal exchange (sometimes along with other interventions) had lower overall vegetation cover than nearby natural marshes. One before-and-after study in the UK reported that 99% of salt marsh quadrats were vegetated nine years after restoring tidal exchange, compared to 100% in the freshwater wetland that previously occupied the site and 43% one summer after restoration. Three studies in the USA and the UK simply quantified the overall cover of vegetation present in sites for up to 15 years after facilitating tidal exchange (sometimes along with other interventions). Characteristic plant abundance (1 study): One site comparison study in the USA reported that some plant species diagnostic of natural brackish marshes were absent from a marsh that had developed over >30 years of restored tidal exchange. Individual species abundance (6 studies): Six studies quantified the effect of this action on the abundance of individual plant species. For example, three site comparison studies of salt marshes in the UK reported that cover of saltmarsh grass Puccinellia maritima was similar or lower in marshes developing after 1–14 years of tidal exchange (sometimes along with other interventions) than in nearby natural marshes. In contrast, in these studies, cover of glassworts Salicornia was higher in restored than natural marshes. VEGETATION STRUCTURECollected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3207https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3207Fri, 09 Apr 2021 07:49:08 +0100Collected Evidence: Collected Evidence: Use environmentally-sensitive material on subtidal artificial structures Fourteen studies examined the effects of using environmentally-sensitive material on subtidal artificial structures on the biodiversity of those structures. Seven studies were on open coastlines in the United Arab Emirates, Italy, Israel, southeast Spain, and in France, the UK, Portugal and Spain. Three were in marinas in northern Israel and the UK, two were in estuaries in southeast Australia and eastern USA, one was in a lagoon in Mayotte, and one was in a port in Germany. COMMUNITY RESPONSE (11 STUDIES) Overall community composition (11 studies): Six of 11 replicated, controlled studies (including eight randomized, three paired sites and one before-and-after study) in Australia, the United Arab Emirates, Italy, Israel, the USA, the UK, Spain and Germany found that using shell-concrete or quarried rock in place of standard-concrete on subtidal artificial structures, or using ECOncreteTM in place of standard-concrete or fibreglass, along with creating texture, grooves, holes, pits and/or small ledges, altered the combined macroalgae and invertebrate community composition on structure surfaces. Three studies found that using quarried rock or blast-furnace-cement-concrete in place of standard-concrete did not alter the community composition, while one found mixed effects depending on the type of rock tested and the site. One found that using different cement mixes in concrete (including some with recycled cements) altered the community composition of native species, but not non-natives. Three of the studies also reported that ECOncreteTM surfaces with added habitats supported mobile invertebrate, non-mobile invertebrate and/or fish species that were absent from standard-concrete or fibreglass structure surfaces. Overall richness/diversity (7 studies): Three of seven replicated, controlled studies (including five randomized, two paired sites and one before-and-after study) in Italy, Israel, the USA, the UK and Spain found that using quarried rock, shell-concrete or recycled-cement-concrete in place of standard-concrete on subtidal artificial structures had mixed effects on the combined macroalgae and invertebrate species richness on structure surfaces, depending on the site, surface orientation or type of cement tested. One of the studies, along with one other, found that using shell-concrete or quarried rock did not increase the species diversity and/or richness, while one found that using recycled cement did not increase the non-native species richness. Three studies found that using ECOncreteTM, along with creating texture, grooves, holes, pits and/or small ledges, did increase the species diversity and/or richness on and around structures. Algal richness/diversity (1 study): One replicated, randomized, controlled study in the UK found that using recycled-cement-concrete in place of standard-concrete on subtidal artificial structures did not increase the diatom species richness on structure surfaces. POPULATION RESPONSE (11 STUDIES) Overall abundance (7 studies): Three of seven replicated studies (including six controlled, four randomized and one paired sites study) in the United Arab Emirates, Italy, Israel, the USA, the UK, Spain, and in France, the UK, Portugal and Spain found that using quarried rock or shell-concrete in place of standard-concrete on subtidal artificial structures did not increase the combined macroalgae and invertebrate abundance on structure surfaces. Two studies found mixed effects, depending on the type of quarried rock or concrete tested and/or the location. One found that using ECOncreteTM in place of fibreglass, along with creating textured surfaces, increased the live cover and biomass, while one found that different ECOncreteTM and standard-concrete mixes supported different cover and inorganic biomass but similar organic biomass. Algal abundance (6 studies): Four of six replicated, controlled studies (including four randomized and one paired sites study) in Australia, the United Arab Emirates, Italy, Israel and the UK found that using quarried rock or recycled-cement-concrete in place of standard-concrete on subtidal artificial structures did not increase the abundance of brown, turf or coralline macroalgae, canopy macroalgae recruits or diatoms on structure surfaces. Two studies found that using quarried rock or using ECOncreteTM, along with creating grooves, holes and pits, had mixed effects on macroalgal abundance, depending on the species group and/or site. One of the studies found that using quarried rock increased red and green macroalgal abundance. Invertebrate abundance (6 studies): Three of six replicated, controlled studies (including four randomized and one paired sites study) in Austalia, the United Arab Emirates, Italy, Israel and the UK found that using quarried rock in place of concrete on subtidal artificial structures, or using ECOncreteTM, along with creating grooves, holes and pits, had mixed effects on the abundance of non-mobile invertebrates, mobile invertebrates or coral recruits on structure surfaces, depending on the type of rock tested, the species group and/or the site. One of the studies, along with one other, found that using quarried rock did not increase the abundance of sponges, bryozoans, ascidians, mussels, barnacles, or Serpulid tubeworms, but in one it decreased Spirorbid tubeworm abundance. One study found that using shell-concrete increased bivalve abundance. One found that different ECOncreteTM and standard-concrete mixes supported different coral abundance. Fish abundance (1 study): One replicated, controlled study in Israel found that using ECOncreteTM in place of standard-concrete on subtidal artificial structures, along with creating grooves, holes and pits, had mixed effects on fish abundances, depending on the species group. BEHAVIOUR (1 STUDY) Use (1 study): One study in Mayotte reported that basalt rock surfaces created on a concrete subtidal artificial structure, along with small and large swimthroughs, were used by juvenile spiny lobsters and groupers, sea firs, and adult fishes from five families. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3470https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3470Thu, 16 Sep 2021 19:51:58 +0100Collected Evidence: Collected Evidence: Create groove habitats (1–50 mm) on intertidal artificial structures Fourteen studies examined the effects of creating groove habitats on intertidal artificial structures on the biodiversity of those structures. Seven studies were in estuaries in southeast Australia, the UK and Hong Kong, four were on open coastlines in the UK and the Netherlands, two were on island coastlines in the Singapore Strait, and one was in a port in the Netherlands. COMMUNITY RESPONSE (11 STUDIES) Overall community composition (3 studies): Two of three replicated, controlled studies (including one randomized and two before-and-after studies) in Australia and the UK found that creating groove habitats on intertidal artificial structures did not alter the combined macroalgae and invertebrate community composition on structure surfaces. However, one of these studies reported that grooves supported macroalgae, mobile and non-mobile invertebrate species that were absent from structure surfaces without grooves. One study found that creating grooves did alter the community composition. Fish community composition (1 study): One replicated, randomized, controlled study in Singapore found that groove habitats created on an intertidal artificial structure, along with pits, altered the fish community composition on and around structure surfaces, and supported species that were absent from surfaces without grooves and pits. Overall richness/diversity (8 studies): Three of six replicated, controlled studies (including two randomized and two before-and-after studies) in the UK and Singapore found that creating groove habitats on intertidal artificial structures, along with pits in one study, increased the combined macroalgae and invertebrate species richness and/or diversity on structure surfaces. Two studies found that creating grooves did not increase their species richness. One found that creating grooves, along with pits, had mixed effects on species richness depending on the site. One of the studies found that increasing the density and fragmentation of grooves, along with pits, had mixed effects on species richness. Two replicated studies (including one randomized, paired sites study) in Hong Kong and Australia found that grooves supported higher species richness than small ridges or ledges created in between them, but one found that species diversity in grooves vs ridges varied depending on the groove depth. Algal richness/diversity (1 study): One replicated, paired sites, controlled study in Australia found that creating groove habitats on intertidal artificial structures did not increase the macroalgal species richness on structure surfaces. Invertebrate richness/diversity (3 studies): Two replicated, controlled studies (including one randomized and one paired sites study) in Australia found that creating groove habitats on intertidal artificial structures did not increase the species richness of mobile or non-mobile invertebrates or limpets on structure surfaces. One replicated study in Australia found that grooves supported higher mobile invertebrate species richness than small ledges created in between them. Fish richness/diversity (2 studies): One replicated, randomized, controlled study in Singapore found that creating groove habitats on an intertidal artificial structure, along with pits, increased the fish species richness on and around structure surfaces. One replicated study in Australia found that grooves supported similar fish species richness to small ledges created in between them. POPULATION RESPONSE (9 STUDIES) Overall abundance (4 studies): Two of three replicated, controlled studies (including one randomized and two before-and-after studies) in the UK and Singapore found that creating groove habitats on intertidal artificial structures, along with pits in one study, increased the combined macroalgae and invertebrate abundance on structure surfaces. One found that creating grooves did not increase their abundance. One replicated study in Australia found that grooves supported similar abundances to small ledges created in between them. Algal abundance (2 studies): Two replicated, paired sites, controlled studies in the Netherlands reported that creating groove habitats on intertidal artificial structures did not increase the macroalgal abundance on structure surfaces. Invertebrate abundance (6 studies): Three of four replicated, controlled studies (including two randomized and two paired sites studies) in Australia, the Netherlands and the UK found that creating groove habitats on intertidal artificial structures did not increase the invertebrate, limpet or chiton abundances on structure surfaces. One study found that creating grooves, along with pits, had mixed effects on mobile invertebrate and barnacle abundances, depending on the site. One replicated, paired sites, controlled study in Australia reported that grooves supported non-mobile invertebrates more frequently than structure surfaces without grooves, but not mobile invertebrates. One replicated study in Australia found that grooves supported higher mobile invertebrate and oyster abundances than small ledges created in between them. Fish abundance (2 studies): One replicated, randomized, controlled study in Singapore found that creating groove habitats on an intertidal artificial structure, along with pits, increased the fish abundance on and around structure surfaces. One replicated study in Australia found that grooves supported similar fish abundance to small ledges created in between them. BEHAVIOUR (2 STUDIES) Use (1 study): One replicated, paired sites, controlled study in the Netherlands reported that groove habitats created on an intertidal artificial structure were used by mussels and periwinkles. Fish behaviour change (1 study): One replicated, randomized, controlled study in Singapore found that creating groove habitats on an intertidal artificial structure, along with pits, increased the number of bites fishes took from structure surfaces. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3473https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3473Mon, 20 Sep 2021 10:03:37 +0100Collected Evidence: Collected Evidence: Cease livestock grazing: Grassland & shrubland Fifteen studies evaluated the effects of ceasing livestock grazing in grassland and shrubland on reptile populations. Eight studies were in the USA, three were in Australia, two were in the UK and one was in each of New Zealand and Egypt. COMMUNITY RESPONSE (6 STUDIES) Richness/diversity (6 studies): Four of six studies (including one replicated, controlled, before-and-after study) in the USA and Australia found that ungrazed and grazed areas had similar reptile species richness, combined reptile and amphibian or reptile and small mammal species richness. One study found that ungrazed sites had higher species richness than grazed sites. The other study found that fencing areas to exclude grazers had mixed effects on lizard species richness. POPULATION RESPONSE (15 STUDIES) Abundance (15 studies): Seven of 14 studies (including one replicated, controlled, before-and-after study) in the USA, New Zealand, Australia, Egypt and the UK found that ceasing grazing (in one case after eradicating invasive mice3 and in one case after burning11) had mixed effects on reptile or lizard abundance. Four studies found that ungrazed areas had a higher abundance of lizards or smooth snakes than grazed areas. The other three studies found that ungrazed and grazed areas had a similar abundance of reptiles, reptiles and small mammals or Texas tortoises. One replicated, randomized, site comparison study in the USA found that areas with fencing that excluded both grazing and recreational vehicle use had more Agassiz’s desert tortoises than areas with less restrictions on grazing or vehicle use. Survival (2 studies): One of two replicated studies (including one controlled study) in the USA found that areas with fencing that excluded grazing and recreational vehicle use had lower death rates of Agassiz’s desert tortoises than areas with less restrictions on grazing or vehicle use. The other study found that in areas where grazing was ceased and where grazing was rotational, survival of Texas tortoises was similar. Condition (1 study): One replicated, controlled study in the USA found that in areas where grazing was ceased and where grazing was rotational, size and growth of Texas tortoises was similar. BEHAVIOUR (1 STUDY) Behaviour change (1 study): One site comparison study in Egypt found that in areas protected from grazing with fences, Be’er Sheva fringe-fingered lizards spent less time moving and were observed further away from the nearest vegetation compared to in areas with grazing and low-impact watermelon farming. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3498https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3498Mon, 06 Dec 2021 13:47:23 +0000Collected Evidence: Collected Evidence: Install tunnels/culverts/underpasses under roads/railways Fifteen studies evaluated the effects of installing tunnels/culverts/underpasses under roads/railways on reptile populations. Four of the studies were in the USA, four were in Australia, three were in Spain, two were in Canada and one was in each of Australia, Europe and North America and South Africa. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (3 STUDIES) Survival (3 studies): Two site comparison studies (including one before-and-after study) in Australia and South Africa found a similar number of reptile road mortalities with or without culverts or wildlife underpasses. One replicated study in Spain found that the number of underpasses in an area did not affect the number of reptile road mortalities. BEHAVIOUR (12 STUDIES) Use (12 studies): Six studies (including four replicated studies and one replicated, before-and-after study) and one review in Spain, Australia, the USA and Australia, Europe and North America found that crossing structures, including tunnels, culverts, underpasses, pipes and trenches under roads and railways were used by reptiles, lizards, snakes and/or tortoises. One review in Australia, Europe and North America also found that wildlife underpasses were used by reptiles in only one of 13 studies. Three of four replicated studies (including one before-and-after study) in the USA and Canada found that desert tortoises, painted and snapping turtles and rattlesnakes and garter snakes showed a willingness to enter some, or all types of tunnel. The other study found that only 9% of painted turtles entered a culvert during a choice experiment. One site comparison study in Australia found that the area under an overpass was used by five reptile species. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3508https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3508Tue, 07 Dec 2021 11:55:41 +0000Collected Evidence: Collected Evidence: Use prescribed burning: Grassland & shrubland Fourteen studies evaluated the effects of using prescribed burning in grassland and shrubland on reptile populations. Seven studies were in the USA, four were in Australia and one was in each of South Africa, Argentina and France. COMMUNITY RESPONSE (6 STUDIES) Community composition (1 study): One replicated, before-and-after study in Australia found that reptile species composition was different before and immediately after burning in three grass types and remained different after vegetation grew back in one of three grass types. Richness/diversity (5 studies): Two of three studies (including one replicated, controlled, before-and-after study) in South Africa, Argentina and the USA found that areas with annual burning had similar reptile species richness and diversity compared to unburned areas or that richness was similar across areas with a range of burn frequencies. The other study found that burned areas had higher reptile species richness than unburned areas. One replicated, site comparison study in Australia found that areas burned 1–4 years earlier had lower reptile species richness than areas burned 11–15 years earlier. One replicated, site comparison study in the USA found that areas with different burn frequencies had similar reptile species richness and diversity. POPULATION RESPONSE (11 STUDIES) Abundance (11 studies): Three of six studies (including three replicated, randomized, controlled studies) in the USA and Argentina found that burned areas had a similar abundance of lizards, snakes and lizards and combined reptiles and amphibians compared to unburned areas. Two studies found that burning had mixed effects on the abundance of different reptile species and western yellow-bellied racer snakes.The other study found that burned areas had more eastern massasauga rattlesnakes than unburned areas. One replicated, site comparison study in Australia found that areas burned 1–4 years earlier had a lower abundance of reptiles than areas burned 11–15 years earlier. One controlled before-and-after study in the USA found that a burned area had a similar number of four snake species compared to when the area was managed by mowing. One site comparison study in France found that one reptile species was less abundant in areas managed by burning than areas grazed by sheep, whereas the abundance of five other species was similar in all areas. One replicated, before-and-after study in Australia found that immediately after burning, the abundance of reptiles was lower than before burning, but was similar after vegetation grew back. One replicated, randomized, site comparison study in Australia found that small-scale patch burning was associated with increased abundance of sand goanna burrows. BEHAVIOUR (1 STUDY) Use (1 study): One replicated, randomized, controlled study in Australia found that some rocky outcrops that were burned were recolonized by pink-tailed worm-lizards. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3651https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3651Thu, 09 Dec 2021 17:11:07 +0000Collected Evidence: Collected Evidence: Translocate adult or juvenile reptiles: Snakes Fourteen studies evaluated the effects of translocating snakes on their populations. Seven studies were in the USA, two were in Antigua, two were global and one was in each of Canada, South Korea and Australia. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (12 STUDIES) Abundance (6 studies): One of two global reviews reported that 15 of 47 reptile translocations (number of snake species not provided) resulted in stable or growing populations (both wild-caught and captive bred reptiles or snakes). The other review reported that the outcome of one indigo snake reintroduction was unknown. One replicated study in the USA found that five of 13 translocations of snakes resulted in established populations. Three studies in Canada and Antigua reported that 3–7 years after translocations of red-sided garter snakes and Antiguan racer snakes, greater numbers were counted. Reproductive success (3 studies): One global review reported that breeding occurred in nine of 22 reptile translocations (of both wild-caught and captive bred animals). Two studies in Antigua reported successful reproduction in translocated populations of Antiguan racer snakes three years after release. Survival (8 studies): Three controlled studies in the USA and Australia found that translocated timber rattlesnakes, northern water snakes and dugite snakes had lower survival than resident snakes, and in one study no translocated snakes survived a year. One controlled study in the USA found that ratsnakes held in captivity for 1–7 years before release had lower survival compared to snakes held for 7–18 days or resident snakes. Four studies (including one replicated, controlled study) in Canada, the USA and South Korea reported that 12–45% of snakes survived for three months to eight years after release. Condition (1 study): One controlled study in the USA found that translocated northern water snakes had similar growth rates compared to resident snakes. BEHAVIOUR (5 STUDIES) Behaviour change (5 studies): Three of five controlled studies in the USA found that differences in movement and home range size of translocated and resident hognose snakes, ratsnakes and dugite snakes were mixed. The other two studies found that translocated timber rattlesnakes and northern water snakes had larger home ranges than residents. One study also found that translocated timber rattlesnakes had higher daily movements than resident snakes. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3716https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3716Mon, 13 Dec 2021 15:01:40 +0000Collected Evidence: Collected Evidence: Release captive-bred reptiles into the wild: Tortoises, terrapins, side-necked & softshell turtles Fourteen studies evaluated the effects of releasing captive-bred tortoises terrapins, side-necked & softshell turtles into the wild. Five studies were in the USA, three were in Italy, two were in the Seychelles, and one was in each of Madagascar, Australia and Spain and Minorca and one was global. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (13 STUDIES) Abundance (1 study): One global review found that when using recruitment to the adult population as a measure of success, 32% of reptile translocations/releases (releases of captive individuals were 7% of total projects) were successful. Occupancy/range (1 study): One review in Australia found that two of three releases of captive-bred Western swamp tortoises were classified as successful. Reproductive success (2 studies): Two studies (including one replicated study) in Italy reported evidence of a gravid female and successful reproduction following release of captive-bred European pond turtles. Survival (11 studies): Six of nine studies (including two replicated, controlled studies) in Madagascar, the Seychelles, the USA and Italy reported that 66–100% of 5–80 captive-bred tortoises and turtles released into the wild survived over monitoring periods of six months to two years. Two studies reported that 16–20% of 5 and 246 individuals survived over two years. The other study reported that some of over 250 individuals (number not given) were recaptured over a year of monitoring. One study also found captive-bred alligator snapping turtles that were older at their time of release had higher survival than younger turtles. One replicated study in Italy found that annual survival of released captive-bred European pond turtles was 67–91%. One replicated study in Spain and Minorca found that survival of captive-bred Hermann’s tortoises was higher after three years after release into the wild compared to 1–2 years after release. The study also found that after three years, survival of released tortoises was similar to that of wild tortoises in one population, but lower in a second population. Condition (2 studies): One of two controlled studies (including one replicated study) in the USA found that released captive-bred juvenile alligator snapping turtles grew at a similar rate and achieved higher body condition than juveniles that remained in captivity. The other study found that released alligator snapping turtles had similar body conditions compared to individuals that remained in captivity. BEHAVIOUR (1 STUDY) Behaviour change (1 study): One randomized study in the USA found that captive-bred Blanding’s turtles released into open water habitat had larger home ranges than those released into places dominated by cattail or willows. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3770https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3770Wed, 15 Dec 2021 11:07:11 +0000Collected Evidence: Collected Evidence: Clear or open patches in forests Fourteen studies evaluated the effects on butterflies and moths of clearing or opening patches in forests. Five studies were in the UK, two were in each of Finland and Japan one was in each of Sweden, the USA and Canada and the Czech Republic, and one was a review across Europe. COMMUNITY RESPONSE (6 STUDIES) Community composition (1 study): One replicated, site comparison study in the UK found that wider woodland rides (and coppiced woodland) contained more unique species of macro-moth than standard width rides or mature forest. Richness/diversity (6 studies): Three replicated studies (including one controlled study, one site comparison study and one paired sites, controlled study) in the UK, Japan and the Czech Republic found that cleared patches in forests had a greater species richness of butterflies but a lower species richness of moths than unmanaged patches, coppiced woodland or closed canopy forest. One of these studies also found that the species richness of butterflies declined over the first three years after clearing. One of two replicated, site comparison studies in the UK and Canada found that larger, but not smaller, cleared patches supported a higher species richness of butterflies than undisturbed forest. The other study found that both wider and standard width rides had a similar species richness of macro-moths to mature forest. One replicated, site comparison study in Japan found that cleared forest patches had a similar species richness of butterflies to semi-natural grassland, although six species were only observed in cleared patches, compared to 15 species only observed in grassland. POPULATION RESPONSE (10 STUDIES) Abundance (10 studies): Five studies (including one replicated, controlled, before-and-after study, one replicated, controlled study and one replicated, site comparison study and two before-and-after studies) in the UK, Finland, Sweden and Japan found that cleared patches in forests, which were also managed with coppicing and grazing, had a higher abundance of butterflies generally, and chequered blue, woodland brown, high brown fritillary and small pearl-bordered fritillary specifically, than before management, or than unmanaged or coppiced areas. One of these studies also found that the abundance of butterflies declined over the first three years after clearing. One of two replicated, site comparison studies in the UK and Canada found that larger, but not smaller, cleared patches had a higher abundance of butterflies than undisturbed forest. The other study found that wider rides had a lower abundance of macro-moths than standard width rides or mature forest. One replicated, site comparison study in the UK found that patches cleared 2–4 years ago had a greater abundance of heath fritillary than patches cleared 7–11 years ago or patches in their first year after clearance. One study in Finland reported that, in an area with selected clearance of pines, a translocated population of baton blue butterflies increased in number over two years. One review across Europe reported that clearing small patches in forests benefitted 19 out of 67 butterfly species of conservation concern. Survival (1 study): One study in Finland reported that, in an area with selected clearance of pines, a translocated population of baton blue survived for at least two years. BEHAVIOUR (2 STUDY) Use (2 studies): One paired sites study in the USA found that orange sulphur butterflies, but not pine whites, flew into areas with selective clearance of pines more often than other areas. One replicated, before-and-after, site comparison study in the UK reported that in cleared patches in forests, which were also managed with cutting, grazing and ride widening, pearl-bordered fritillary and Duke of Burgundy breeding sites increased compared to before management. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3938https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3938Sat, 13 Aug 2022 14:56:39 +0100Collected Evidence: Collected Evidence: Reduce grazing intensity on grassland by reducing stocking density Fourteen studies evaluated the effects on butterflies and moths of reducing grazing intensity on grassland by reducing stocking density. Four studies were in the UK, two were in each of Sweden and Germany, one was in each of the USA, Belgium and the Netherlands, Europe and Switzerland. COMMUNITY RESPONSE (8 STUDIES) Richness/diversity (8 studies): Five of eight replicated studies (including two randomized, controlled studies and six site comparison studies) in the UK, Sweden, Germany, the USA and Switzerland found that grasslands grazed with lower stocking densities of sheep, cattle or a mix of sheep, cattle and horses had a greater species richness of adult butterflies, all moths and burnet moths than grassland grazed at higher stocking densities. However, one of these studies also found that butterfly and burnet moth caterpillar species richness was similar at sites with low and high stocking densities. Two of the other studies found that grasslands grazed with lower stocking densities of cattle and horses or unspecified grazing animals had a similar species richness of butterflies and burnet moths to grassland grazed at higher stocking densities. The other study found that, in one of two study years, grasslands grazed with cattle at a low density had lower species richness than grasslands grazed at moderate density. POPULATION RESPONSE (12 STUDIES) Abundance (11 studies): Eight replicated studies (including four controlled studies and four site comparison studies) in the UK, Germany, the USA and Sweden found that grasslands grazed with lower stocking densities of sheep, cattle or both (in one case combined with a later start to grazing) had a greater abundance of all butterflies, butterflies with grass host plants, all moths, burnet moths, their caterpillars or specific species (in two cases as part of combined invertebrate counts) than grasslands grazed at higher stocking densities. The three studies on caterpillars only found a higher abundance at two out of three sites or in earlier or later sampling periods, and one of the studies found that sites with low and high intensity grazing had a similar abundance of butterfly and burnet moth caterpillars. Two replicated, site comparison studies in Sweden and Switzerland found that grasslands grazed with lower stocking densities of cattle and horses or unspecified grazing animals had a similar abundance of butterflies and burnet moths to grassland grazed at higher stocking densities. One review of studies in Europe reported that reducing grazing intensity benefitted 41 out of 67 butterfly species of conservation concern, but did not distinguish between reducing stocking density and seasonal removal of livestock. Survival (1 study): One site comparison study in Belgium and the Netherlands reported that the survival of Glanville fritillary caterpillar nests was similar between grasslands with low and high stocking density of sheep. Condition (1 study): One site comparison study in Belgium and the Netherlands found that after 6–10 days of sheep grazing, fewer Glanville fritillary caterpillar nests were damaged in a grassland with lower stocking density than in a grassland with higher stocking density, but there was no difference after two months. BEHAVIOUR (0 STUDIES)Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3959https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3959Sun, 14 Aug 2022 10:37:16 +0100