Conservation Evidence: Evidence Data

Collected Evidence: Collected Evidence: Undersow spring cereals, with clover for example A total of fifteen studies from the UK, Austria, Denmark, Finland and Switzerland (including four replicated, controlled and randomised studies and two reviews) looked at the effects of undersowing spring cereals on biodiversity. Eleven studies (including seven replicated trials, of which one controlled and three randomized and controlled, and one review) found that undersowing spring cereals benefited some birds, plants, insects, spiders and earthworms. These benefits to farmland wildlife included increases in barnacle goose abundance, densities of singing Eurasian skylark and nesting dunnock, arthropod abundance and species richness, and bumblebee, butterfly, earthworm, ground beetle, spider or springtail abundances. Five studies from Austria, Finland and the UK (including three replicated studies of which one was also controlled and randomized, and a review) found that undersowing spring cereals did not benefit invertebrates, plants, grey partridge population indicators, or nesting densities of two out of three farmland bird species. One replicated study from the UK found only one out of five bird species was found more frequently on undersown wheat stubbles than conventionally managed barley. Collected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F136https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F136Fri, 18 Nov 2011 15:24:58 +0000Collected Evidence: Collected Evidence: Control mammalian predators on islands for seabirds We found 16 before-and-after studies, one paired sites study and one literature review from around the world, all describing positive seabird responses to the removal or control of mammalian predators (mainly rats Rattus spp. and feral cats Felis catus) from islands. Of these 18 studies, seven found either large population increases or recolonisations following predator eradication or control. Two of these found only partial population increases or recolonisations: a study from Alaska. Twelve studies found increases in reproductive success and survival or decreases in predation and mortality following predator control. In one case there was also a small population increase. Rats and mice Mus musculus were controlled in twelve studies, mostly examining burrow-nesting seabirds; cats in eight, mostly on ground or cliff-nesting seabirds; and other species in two. Collected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F375https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F375Tue, 07 Aug 2012 15:57:05 +0100Collected Evidence: Collected Evidence: Provide artificial nesting sites for owls Three studies from the UK appeared to show increases in local populations of owls following the installation of artificial nests, although the authors from one note that they could not rule out birds merely switching from natural nest sites. Another UK study found that providing nesting sites when renovating buildings maintained barn owl Tyto alba populations, whilst they declined at sites without nests. Four studies from the USA and the UK found high levels of breeding success in artificial nests, three finding equal or higher productivity than natural nests. A replicated, controlled study from the USA found lower productivity from artificial nests, whilst a replicated, controlled study from Finland found that artificial nests were only successful in the absence of larger owls and a replicated, controlled study from Hungary found that fledglings from artificial nests were less likely to be found alive after one year. Four studies from the USA and Europe found that artificial nests were used at least as frequently as natural nesting sites. Five studies from across the world found that owls used artificial nests, with one finding that use increased over time, although only for one of two species. Three studies found that owls differentiated between nests in different positions, whilst five studies found that different designs of nests differed in occupancy or productivity. Three studies found occupancy did not differ between designs and two found no differences in productivity for different designs. Collected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F490https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F490Mon, 03 Sep 2012 15:06:04 +0100Collected Evidence: Collected Evidence: Reduce chemical inputs in grassland management A total of 16 studies (including five reviews) investigated the effects of reducing inputs in permanent grasslands. Six studies from the Netherlands, Switzerland and the UK (including one review and four replicated studies of which one was also controlled and one a randomized and controlled before-and-after trial) found that stopping fertilizer inputs in permanent grassland resulted in an increase in plant species richness, reduced the rate of plant species loss and attracted a higher abundance or species richness of some or all invertebrates studied. One review from the Netherlands found that low fertilizer input grasslands favour common meadow bird species. One review found a study showing that densities of some invertebrates were higher in unfertilized plots compared with those receiving nitrogen inputs. Two replicated, controlled trials from the Czech Republic and the UK (one randomized) found that applying fertilizer to permanent grasslands reduced plant species richness or diversity and that the effects on plant communities were still apparent 16 years after the cessation of fertilizer application. Four studies from Ireland, the Netherlands and the UK (including two replicated trials of which one randomized and one controlled and a review) found that reducing fertilizer inputs on grassland had no clear or rapid effect on plant species richness. A review found no clear effect of reducing fertilizer inputs on the density of soil-dwelling invertebrates. One replicated study found that fertilizer treatment only affected seed production of a small number of meadow plants. One replicated study from the UK found lower invertebrate abundance on plots with reduced fertilizer inputs but the differences were not significant. Collected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F694https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F694Sat, 01 Dec 2012 17:52:25 +0000Collected Evidence: Collected Evidence: Create beetle banksNatural enemies in fields: Six studies from Canada, the UK and USA (three replicated, controlled, of which two were also randomised) examined the effects on predator numbers in adjacent crops. A review found that predators increased in adjacent crops, but one study found effects varied with time and another found no effect. Two studies found small or slow movements of predators from banks to crops. One study found greater beetle activity in fields but this did not improve pest predation. Natural enemies on banks: Four studies and a review found more invertebrate predators on beetle banks than in surrounding crops, but one of these found that effects varied with time. Eight studies from the UK and USA (including two randomised, replicated, controlled trials and two reviews) compared numbers of predatory invertebrates on beetle banks with other refuge habitats. Two studies found more natural enemies on beetle banks, but one of these found only seasonal effects. One review found similar or higher numbers of predators on beetle banks and four studies found similar or lower numbers. Pests: A replicated, randomised study and a review found the largest pest reductions in areas closest to a beetle bank or on the beetle bank itself. One review found fewer pests in fields with than without a beetle bank. Economics: One replicated, randomised, controlled trial and a review showed that beetle banks could make economic savings if they prevented pests from reaching a spray threshold or causing 5% yield loss. Beetle bank design: Two studies from the UK found certain grass species held higher numbers of predatory invertebrates than others. Crops studied were barley, field bean, maize, oats, pea, radish, rapeseed, soybean, wheat and pasture.Collected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F729https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F729Thu, 30 May 2013 14:45:59 +0100Collected Evidence: Collected Evidence: Use prescribed fire or modifications to burning regime in forests Eight of 14 studies (including three randomized, replicated, controlled studies) in Australia, North America and the USA found no effect of prescribed forest fires on amphibian abundance or numbers of species. Four found that forest fires had mixed effects on amphibian abundance depending on species, species and year or season of burn. Three found that fires increased amphibian abundance or numbers of species. One found that abundance decreased with fires. Two studies (including one randomized, replicated, controlled study) in the USA found that numbers of amphibian species and abundance increased or abundance decreased with time since prescribed forest fires. One before-and-after study in the USA found that spotted salamander hatching success increased following a prescribed forest fire. Collected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F877https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F877Thu, 12 Sep 2013 12:56:53 +0100Collected Evidence: Collected Evidence: Use antifungal treatment to reduce chytridiomycosis infection Twelve of 16 studies (including four randomized, replicated, controlled studies) in Europe, Australia, Tasmania, Japan and the USA found that antifungal treatment cured or increased survival of amphibians with chytridiomycosis. Four studies found that treatments did not cure chytridiomycosis, but did reduce infection levels or had mixed results. Six of the eight studies (including two randomized, replicated, controlled studies) in Japan, Tasmania, the UK and USA testing treatment with itraconazole found that it was effective at curing amphibians of chytridiomycosis. One study found that it reduced infection levels and one found mixed effects. Six studies found that specific fungicides caused death or other negative side effects in amphibians. Collected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F882https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F882Fri, 13 Sep 2013 13:44:14 +0100Collected Evidence: Collected Evidence: Use hormone treatment to induce sperm and egg release during captive breeding One review and nine of 10 replicated studies (including two randomized, controlled studies) in Austria, Australia, China, Latvia, Russia and the USA found that hormone treatment of male amphibians stimulated or increased sperm production (Mansour, Lahnsteiner & Patzner 2010, Silla 2011) or resulted in successful breeding in captivity. One found that hormone treatment of males and females did not result in breeding. Four found that the amount and viability of sperm produced was affected by the type, amount or number of doses of hormone. One review and nine of 14 replicated studies (including six randomized and/or controlled studies) in Australia, Canada, China, Ecuador, Latvia and the USA found that hormone treatment of female amphibians had mixed results, with 30–71% of females producing viable eggs following treatment, or with egg production depending on the combination, amount or number of doses of hormones. Three found that hormone treatment stimulated egg production or successful breeding in captivity. Two found that hormone treatment did not stimulate or increase egg production. Five replicated studies (including one controlled study) in Canada, Latvia and the USA found that eggs induced by hormone treatment were raised successfully to tadpoles, toadlets or froglets in captivity. Two replicated studies, one of which was small, in Ecuador and the USA found that most toads died before or soon after hatching. Collected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F883https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F883Fri, 13 Sep 2013 15:54:08 +0100Collected Evidence: Collected Evidence: Thin trees within forests: effects on mature trees Eleven of 12 studies (including two replicated, randomized, controlled studies) in Brazil, Canada, and the USA found that thinning trees in forests decreased the density and cover of trees. One study found no effect of thinning on tree density. Five of six studies (including one replicated, controlled, before-and-after study) in Australia, Sweden and the USA found that thinning trees in forests increased tree size. One found mixed effects of thinning on tree size. One replicated, controlled study in the USA found that thinning trees in forests decreased tree species richness and diversity. One replicated, site comparison study in the USA found that thinning reduced the number of conifers killed by beetles. Two replicated, controlled studies in the USA found no effect of thinning on bark-beetle caused tree mortality. Collected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F1209https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F1209Thu, 19 May 2016 15:02:55 +0100Collected Evidence: Collected Evidence: Use prescribed fire: effects on young trees Five of 15 studies (including four replicated, randomized, controlled studies) from Canada, France and the USA found that prescribed fire increased the density and biomass of young trees. Two studies found that fire decreased new tree density. Eight found no effect or mixed effects depending on the tree species, location and fire frequency. Two of the above studies found mixed effects of prescribed fire on species diversity of young trees depending on the location. Two replicated, controlled studies from the USA found mixed effects of prescribed fire on the survival of young trees. Collected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F1220https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F1220Fri, 20 May 2016 14:45:40 +0100Collected Evidence: Collected Evidence: Water: Use reduced tillage in arable fieldsWater use (3 studies): Two replicated, randomized, controlled studies from Spain and Turkey found that crops used water more efficiently in plots with reduced tillage, compared to conventional tillage, in some comparisons. One replicated, randomized, controlled study from Egypt found that crops used water more efficiently in plots with less-frequent tillage (one pass with a plough, compared to two), but crops used water less efficiently in plots with shallow tillage, compared to deep tillage. Water availability (14 studies) Water content (12 studies): Six controlled studies (five replicated and randomized) from Egypt and Spain found more water in soils with reduced tillage, compared to conventional tillage, in some or all comparisons. Two of these studies also found less water in soils with reduced tillage, compared to conventional tillage, in some comparisons. Two replicated, randomized, controlled studies from Lebanon and the USA found less water in soils with reduced tillage, compared to conventional tillage, in some comparisons. Four controlled studies from Egypt, Italy, and Spain (three of which were replicated and randomized), found similar amounts of water in soils with reduced tillage or conventional tillage, in all comparisons. Water loss (2 studies): One replicated, controlled study from France found that less water was lost through drainage from soils with reduced tillage, compared to conventional tillage, during the growing season, but more water was lost during the fallow season, in some comparisons. One replicated, randomized, controlled study from Egypt found that less water was lost through runoff from soils with less-frequent tillage (one pass with a plough, compared to two), but more water was lost through runoff from soils with shallow tillage, compared deep tillage. Water infiltration (3 studies): One replicated, randomized, controlled study from Egypt found that water infiltration rates were faster in soils with reduced tillage, compared to conventional tillage, in some comparisons. Two replicated, controlled studies from Spain and the USA found that water infiltration rates were similar in soils with reduced tillage or conventional tillage. Pathogens and pesticides (1 study): One replicated, randomized, controlled study from France found that less herbicide was leached from soils with reduced tillage, compared to conventional tillage. Nutrients (0 studies) Sediments (0 studies) Implementation options (2 studies): One replicated, randomized, controlled study from Egypt found more water and faster water infiltration rates in soils that were tilled at slower tractor speeds, but found that water losses and water-use efficiencies were similar in plots that were tilled at different tractor speeds. One replicated, randomized, controlled study from Turkey found that water-use efficiencies were similar in plots with different types of reduced tillage (rototilling and disking, compared to double disking).Collected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F1386https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F1386Mon, 15 May 2017 15:58:07 +0100Collected Evidence: Collected Evidence: Treat sick/injured animals Two before-and-after studies in Brazil found that most reintroduced golden lion tamarins died despite being treated when sick or injured, alongside other interventions. One study in Brazil found that one out of four reintroduced black lion tamarins died after being release despite receiving treatment, alongside other interventions. One review on reintroduced lar gibbons in Thailand found that their population declined by 6% seventeen months after release despite having medical treatment available when sick or injured, alongside other interventions. One study in Malaysia found that 98% of translocated orangutans, some of which received treatment for injuries along with other interventions, survived capture and subsequent release. One controlled study, also in Malaysia, found that a population of reintroduced orangutans decreased by 33% over 33 years despite receiving treatment when sick or injured, alongside other interventions. Four studies, including two before-and-after studies, in Liberia, the Republic of Congo and The Gambia found that most reintroduced chimpanzees that were treated when sick, alongside other interventions, survived for at least 1-5 years and in one case the population increased. One study in Senegal found that a young chimpanzee was reunited with its mother after being treated for injuries, alongside other interventions. One before-and-after study in Uganda found that treatment for mange, alongside other interventions, cured some infected mountain gorillas. One study in Rwanda, Uganda and the Democratic Republic of Congo and one before-and-after, site comparison study in the Republic of Congo and Gabon found that most western lowland gorillas treated when sick or injured, alongside other interventions, survived over 4–41 years. Two before-and-after studies in South Africa and Indonesia found that most reintroduced or translocated primates that were treated when sick, alongside other interventions, survived over six months. However, two before-and-after studies in Madagascar and Kenya found that most reintroduced or translocated primates did not survived over five years or their population size decreased despite treated when sick, alongside other interventions. Collected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F1550https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F1550Thu, 19 Oct 2017 18:35:05 +0100Collected Evidence: Collected Evidence: Amphibians: Use hormone treatment to induce sperm and egg releaseFor summarised evidence see Smith, R.K. and Sutherland, W.J. (2014) Amphibian conservation: Global evidence for the effects of interventions. Exeter, Pelagic Publishing. Key messages and summaries are available here: http://www.www.conservationevidence.com/actions/883Collected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F1896https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F1896Fri, 19 Jan 2018 15:08:37 +0000Collected Evidence: Collected Evidence: Release translocated/captive-bred mammals into area with artificial refuges/breeding sites Seventeen studies evaluated the effects of releasing translocated or captive-bred mammals into areas with artificial refuges or breeding sites. Five studies were in the USA, three were in Australia, three were in Spain, two were in the UK and one was in each of Ireland, South Africa, Hungary and Slovakia, the Czech Republic and Poland. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (15 STUDIES) Abundance (5 studies): Two of three studies (two replicated, two controlled) in Spain and the USA found that translocation release sites with artificial burrows provided had higher abundances of European rabbits and densities of California ground squirrels compared to those without. The other study found that abundance of European rabbits following translocation was similar with and without artificial burrows provided. A replicated, controlled study in the USA found that after translocating black-tailed prairie dogs to areas with artificial burrows, colonies increased in size. A before-and-after study in Spain found that translocating European rabbits into areas with artificial refuges to supplement existing populations did not alter rabbit abundance, although two of three populations persisted for at least three years. Reproductive success (4 studies): Three studies in Australia, Ireland and the UK found that released captive-bred sugar gliders, most translocated female red squirrels and some translocated pine martens provided with nest boxes and supplementary food reproduced. A study of 12 translocation projects in Slovakia, the Czech Republic and Poland found that translocated European ground squirrels released initially into enclosures or burrows with retention caps reproduced after release, whereas those without enclosures or burrows dispersed from release sites. Survival (9 studies): Five of eight studies in Australia, the USA, UK, Ireland and South Africa found that at release sites with artificial refuges, and in some cases food provided, a population of captive-bred sugar gliders survived at least three years, two of three populations of red-tailed phascogales survived for more than four years, most translocated black bears survived at least one year and over half translocated red squirrels and pine martens survived 8-12 months. Three studies found that at release sites with artificial refuges, food and in one case water provided, no translocated red squirrels survived more than five months, all translocated rock hyraxes died within three months and most translocated Tipton and Heermann’s kangaroo rat spp. died within five days. A randomised, replicated, controlled study in Hungary found that translocated European ground squirrels released into plugged artificial burrows had higher recapture rates than those released into unplugged artificial burrows. BEHAVIOUR (3 STUDIES) Use (2 studies): Two studies in Australia found that released captive-bred sugar gliders used artificial nest boxes provided. Behaviour change (1 study): A replicated, before-and-after study in the USA found that translocated Utah prairie dogs released into an area with artificial burrows, after the control of native predators, tended to leave the release site and spent more time being vigilant than before. Collected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F2453https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F2453Tue, 02 Jun 2020 11:09:26 +0100Collected Evidence: Collected Evidence: Use herbicide to control problematic plants: freshwater marshes Seventeen studies evaluated the effects, on vegetation, of using herbicide to control problematic plants in freshwater marshes. Twelve studies were in the USA. Two studies were in Australia. There was one study in each of Canada, Mexico and the UK. There was overlap in the sites used in two studies. Two pairs of studies in Australia and the USA used the same general study area, but different plots or experimental set-ups. VEGETATION COMMUNITY Overall extent (3 studies): Two replicated, randomized, controlled, before-and-after studies in the USA found that marshes sprayed with herbicide had lower live vegetation coverage but greater dead vegetation coverage than unsprayed marshes, after 1–2 years. Overall vegetation coverage was lower in sprayed than unsprayed marshes in one study, but similar in sprayed and unsprayed marshes in the other. One study of a dune slack in the UK simply reported an increase in overall vegetation coverage between one and two years after clearing scrub (by cutting and applying herbicide). Overall richness/diversity (6 studies): Three studies (including one replicated, randomized, paired, controlled) in ephemeral marshes/wet meadows in the USA reported that spraying invaded vegetation with herbicide (sometimes along with other interventions) typically increased total plant species richness 1–5 growing seasons later. Two replicated, randomized, paired, controlled studies (one also before-and-after) in freshwater marshes/wet meadows in the USA and Mexico found that plots treated with herbicide (sometimes along with other interventions) had similar overall plant species richness and diversity to untreated plots, after 4–8 months or three years. One study of a dune slack in the UK simply reported a small increase in total plant richness between one and two years after clearing scrub (by cutting and applying herbicide). Characteristic plant richness/diversity (3 studies): Two before-and-after studies of floodplain marshes in the USA reported that cover of wet-prairie indicator species was higher 1–4 years after applying herbicide than before. However, one of these studies reported that the total cover of non-invasive, wetland-characteristic herbs was similar or lower 2–3 years after applying herbicide than before. One study of a dune slack in the UK simply reported an increase the number of slack-characteristic plant species present between one and two years after clearing scrub (by cutting and applying herbicide). Native/non-target richness/diversity (3 studies): One controlled, before-and-after study in a reed-dominated freshwater marsh in the USA found that applying herbicide (along with cutting/mowing) increased non-reed species richness three years later. One replicated, controlled, before-and-after study in cattail-invaded marshes in the USA reported that marshes sprayed with herbicide contained no living native plants one year later: fewer than were present before spraying and in unsprayed marshes. One study of a dune slack in the UK simply reported an increase in native plant richness between one and two years after clearing scrub (by cutting and applying herbicide). VEGETATION ABUNDANCE Overall abundance (4 studies): Three replicated studies (two also randomized, paired, controlled) in freshwater marshes/wet meadows in the USA and Mexico found that applying herbicide (sometimes along with other interventions) had no clear or significant effect on overall vegetation abundance four months to three years later. Cover and density were similar to untreated plots and/or pre-treatment levels. One replicated, randomized, paired, controlled study in the USA found that wet meadows sprayed with herbicide contained less total vegetation biomass than unsprayed marshes, 2–3 growing seasons later. Native/non-target abundance (7 studies): Four studies (including one replicated, randomized, paired, controlled, before-and-after) in marshes/wet meadows in the USA and Australia found that spraying invaded plots with herbicide (sometimes along with other interventions) did not reduce – and often increased – the abundance of native or non-target vegetation 1–3 growing seasons later. One replicated, controlled, before-and-after study in cattail-invaded marshes in the USA reported that marshes sprayed with herbicide contained no living native plants one year later: density and biomass were lower than before spraying and in unsprayed marshes. One replicated, randomized, paired, controlled study in an alligatorweed-invaded marsh in the USA found that spraying vegetation with herbicide had no significant effect on native plant biomass after 1–2 growing seasons. One study of a floodplain marsh in Australia simply reported non-target vegetation cover for up to four years after treating mimosa-invaded vegetation with herbicide (along with other interventions). Herb abundance (4 studies): Two replicated, randomized, paired, controlled studies in wet meadows in the USA found that treating a problematic plant species with herbicide (sometimes along with physical removal) had no significant effect on cover of forbs, grass-like plants or sedges after 2–3 growing seasons. One replicated, randomized, paired, controlled study in a loosestrife-invaded marsh in Canada found that the density of sedges and grasses was not lower in herbicide-sprayed plots, than in unsprayed plots, after 2–3 years. The precise effect depended on dose of herbicide used. One study of a floodplain marsh in Australia simply reported grass/sedge cover for up to four years after treating mimosa-invaded vegetation with herbicide (along with other interventions). Algae/phytoplankton abundance (1 study): One replicated, randomized, controlled study in a reed-invaded marsh in the USA reported that free-growing filamentous algae were more common in plots sprayed with herbicide than unsprayed plots, approximately one year later. However, spraying with herbicide had no significant effect on the density or biomass of biofilm algae. Individual species abundance (3 studies): Three studies quantified the effect of this action on the abundance of individual plant species, other than the species being controlled. For example, one replicated, randomized, paired, controlled study in a grass-invaded marsh in Mexico found that five of five monitored native species had similar cover in herbicide-sprayed and unsprayed plots after 4–8 months. Two of the studies do not distinguish between the effects of applying herbicide and other interventions. VEGETATION STRUCTURECollected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F3120https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F3120Sun, 04 Apr 2021 17:19:04 +0100Collected Evidence: Collected Evidence: Restore/create freshwater marshes or swamps (multiple actions) Seventeen studies evaluated the effects, on vegetation, of using >3 combined actions to restore/create freshwater marshes or swamps. Fourteen studies were in the USA. There was one study in each of Canada, the UK and East Africa. There was overlap in the sites used in three studies. VEGETATION COMMUNITY Overall extent (1 study): One before-and-after study in Canada reported that the area of emergent vegetation in a marsh was greater after 5–6 years of intervention than in the year before. Community composition (5 studies): Two replicated, site comparison studies in the USA found that restored/created freshwater wetlands contained different overall plant communities to natural or reference wetlands, after 1–8 years. Two site comparison studies in the USA reported similarity in species composition between restored/created and natural wetlands. Similarity ranged from 35% to 79% after 1–5 years. One study in the USA simply quantified the plant community composition of different pools within a marsh, two years after its creation. Overall richness/diversity (16 studies): Three studies (including one replicated, before-and-after, site comparison) of freshwater wetlands in the USA and Canada reported that multiple restoration actions increased overall or emergent plant species richness over 1–6 years. Another replicated, before-and-after, site comparison study in the USA reported that the effect of restoration on plant species richness varied between years. Two replicated, site comparison studies in the USA found that restored/created wetlands had similar plant species richness to natural or reference wetlands, after 1–8 years. One site comparison study in the USA reported that a created wetland contained fewer plant species than nearby natural marshes, after two years. Nine studies (four replicated, one before-and-after) in the USA and the UK simply quantified overall plant species richness and/or diversity approximately 1–10 years after intervention. Characteristic plant richness/diversity (6 studies): One replicated, before-and-after, site comparison study of freshwater wetlands in the USA reported that multiple restoration actions increased the richness of wetland-characteristic plant species over three subsequent years. Five studies (two replicated) in the USA simply quantified wetland-characteristic plant richness up to 10 years after intervention. VEGETATION ABUNDANCE Overall abundance (4 studies): Two replicated, before-and-after studies (one also a site comparison) of freshwater wetlands in the USA reported that multiple restoration actions reduced overall vegetation cover over the five subsequent years. Two replicated studies in the USA simply quantified overall vegetation cover for up to six years after intervention. Characteristic plant abundance (3 studies): Two replicated, before-and-after studies (one also a site comparison) of freshwater wetlands in the USA reported that multiple restoration actions did not increase the cover of wetland-characteristic vegetation over three subsequent years. One of the studies also monitored in the fifth (wetter) year after restoration, and reported greater cover of wetland-characteristic vegetation than before restoration. One replicated study on the same set of wetlands in the USA simply quantified wetland-characteristic vegetation cover for up to three years after intervention. Herb abundance (3 studies): One replicated, site comparison study in the USA found that restored wet prairies had similar grass and forb cover to remnant prairies after 3–8 years. Another replicated, site comparison study in the USA reported that created dune slacks had greater cover of annual herbs after three years than mature natural slacks, but similar cover of perennial herbs and floating aquatic herbs. One replicated, before-and-after study in the USA reported greater herb cover 1–5 years after restoration of freshwater wetlands than before. Tree/shrub abundance (3 studies): One replicated, site comparison study in the USA reported that created dune slacks had similar cover of trees and shrubs, after three years, to mature natural slacks. One replicated, before-and-after study in the USA reported lower cover of woody vegetation 1–5 years after restoration of freshwater wetlands than before. One replicated study in the USA simply quantified woody plant cover 1–2 years after intervention. Individual species abundance (10 studies): Ten studies quantified the effect of this action on the abundance of individual plant species. For example, the replicated, site comparison study in East Africa reported that the biomass of papyrus Cyperus papyrus in created marshes was within the range of natural marshes in the region after 18 months. VEGETATION STRUCTURECollected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F3192https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F3192Wed, 07 Apr 2021 12:22:17 +0100Collected Evidence: Collected Evidence: Directly plant trees/shrubs: freshwater wetlands Seventeen studies evaluated the effects, on vegetation, of directly planting trees/shrubs in freshwater wetlands. Fifteen studies were in the USA. Two were in Australia. Two of the studies took place in the same site, but used different experimental set-ups. VEGETATION COMMUNITY Community composition (2 studies): Two replicated studies of freshwater wetlands in the USA found that planting trees/shrubs (sometimes along with other interventions) had no significant effect on aspects of plant community composition, after 1–11 years. Specifically, planted and unplanted wetlands had a similar proportion of species in different plant groups and relative abundance of different plant groups. Overall richness/diversity (1 study): One replicated, randomized, controlled, before-and-after study in depressional wetlands in the USA found that wetlands sparsely planted with tree seedlings contained a similar number of plant species, after 1–4 years, to unplanted wetlands. VEGETATION ABUNDANCE Overall abundance (2 studies): Two replicated studies (one site comparison; one randomized, controlled, before-and-after) of freshwater wetlands in the USA found that planting trees/shrubs (sometimes along with other interventions) had no significant effect on overall vegetation cover (both ground and canopy, separately or combined) after 1–11 years. Herb abundance (1 study): One study in a former firing range in the USA simply quantified herb cover approximately 1–2 years after reprofiling the site and planting trees/shrubs. Tree/shrub abundance (1 study): One study in a former firing range in the USA simply quantified woody plant cover approximately 1–2 years after reprofiling the site and planting trees/shrubs. VEGETATION STRUCTURE Visual obstruction (1 study): One replicated, site comparison study in the USA found that swamps created by planting trees/shrubs (after reprofiling) had less horizontal vegetation cover, after 7–11 years, than nearby swamps recovering naturally from logging. Height (6 studies): One replicated, site comparison study in the USA found that swamps created by planting trees/shrubs (after reprofiling) contained shorter woody vegetation, after 7–11 years, than nearby swamps recovering naturally from logging. Herbaceous vegetation, however, was of similar height. Five studies (four replicated) in freshwater wetlands in the USA simply quantified the height of trees and shrubs over 1–6 growing seasons after they were planted; in four of these studies, the average height typically increased over time. Diameter (1 study): One study in a freshwater wetland in the USA reported an increase in the diameter of surviving trees over the year after they were planted. Basal area (1 study): One replicated, site comparison study in the USA found that swamps created by planting trees/shrubs (after reprofiling) had a lower vegetation basal area, after 7–11 years, than nearby swamps recovering naturally from logging. OTHER Survival (15 studies): Fifteen studies (including eight replicated) in the USA and Australia quantified survival of individual trees/shrubs planted in freshwater wetlands. Survival rates ranged from 0% to 100% after 4–66 months. Seven of the studies (including six replicated) in the USA and Australia reported 0% survival of planted vegetation in at least some cases, after 1–6 growing seasons. Proposed factors affecting survival included elevation/water levels, the season of planting, protection from herbivores, root pruning, extreme weather, and if/how invasive vegetation was removed before planting. Growth (2 studies): Two studies monitored true growth of individual trees/shrubs (rather than changes in average height of survivors). The two studies, in freshwater wetlands in the USA, reported that planted trees grew in diameter and/or height over their first 1–2 growing seasons. Collected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F3258https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F3258Sat, 10 Apr 2021 13:27:32 +0100Collected Evidence: Collected Evidence: Add fertilizer to soil before or after seeding/planting Seventeen studies examined the effects of adding fertilizer to soil before or after seeding/planting on grassland vegetation. Nine studies were in North America, six studies were in Europe, one study was in China, and one was in Brazil. VEGETATION COMMUNITY (3 STUDIES) Overall richness/diversity (3 studies): One replicated, randomized, paired, controlled study in Spain found that adding fertilizer alongside sowing of non-native plant seeds increased plant diversity in 40% of cases. Two replicated, controlled studies in Spain and Italy found that plant species richness and diversity were not altered by organic matter or fertilizer addition alongside seeding. VEGETATION ABUNDANCE (13 STUDIES) Overall abundance (8 studies): Six of nine replicated, controlled studies (five of which were also randomized and paired) in North America and Europe found that adding fertilizer alongside sowing or planting increased vegetation cover in all or some cases. Three studies found no change in vegetation cover or plant density. Characteristic plant abundance (1 study): One replicated, randomized, paired, controlled study in the UK found that adding fertilizer and sowing seeds increased the abundance of specialist grassland species. Sown/planted species abundance (3 studies): Two replicated, randomized, controlled studies in the USA found that adding fertilizer after sowing seeds did not alter the density of sown forbs. One replicated, randomized, paired, controlled study in the USA found that adding fertilizer after sowing seeds increased the cover but not the density of four sown plant species. Grass abundance (1 study): One replicated, controlled study in the USA found that adding fertilizer and sowing seeds increased the biomass of three native grass species. VEGETATION STRUCTURE (0 STUDIES) OTHER (4 STUDIES) Germination/Emergence (1 study): One replicated, randomized, paired, controlled study in China found that adding fertilizer and sowing seeds did not increase seedling emergence or density. Survival (3 studies): Three replicated, controlled, paired studies (one of which was randomized) in the UK, China and Brazil found that adding fertilizer alongside sowing seeds did not alter the survival of seedlings. Growth (1 study): One replicated, randomized, controlled study in the USA found that adding fertilizer after planting native prairie plants reduced the diameter of prairie lupine plants and did not alter the growth of six other plant species. Collected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F3427https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F3427Mon, 28 Jun 2021 10:37:44 +0100Collected Evidence: Collected Evidence: Protect habitat: All reptiles (excluding sea turtles) Seventeen studies evaluated the effects of protecting habitat on reptile populations (excluding sea turtles). Four studies were in the USA, two were in each of Australia and Brazil, and one was in each of Canada, Madagascar, South Africa, Spain, Hong Kong, Argentina, the borders of Zambia and Zimbabwe, Pakistan and Mexico. COMMUNITY RESPONSE (5 STUDIES) Richness/diversity (5 studies): Three of five studies (including two replicated, site comparison studies) in the USA, South Africa, Australia, Pakistan and Mexico found mixed effects of protected areas on reptile species richness and combined reptile and amphibian species richness. The other two studies found that protected areas had higher reptile species richness than unprotected farmland. POPULATION RESPONSE (16 STUDIES) Abundance (13 studies): Six of 11 studies (including five replicated, site comparison studies) in the USA, Canada, Hong Kong, Mexico, Australia, South Africa, Argentina, the border of Zambia and Zimbabwe and Pakistan found that protected areas had a higher abundance of reptiles, tortoises, Nile crocodiles and combined reptiles and amphibians than areas with less or no protection. Four studies found mixed effects of protection on the abundance of reptiles and big-headed turtles. The other study found that water bodies in protected areas had fewer eastern long-necked turtles than those in suburban areas. One site comparison study in Brazil found that areas with community-based management of fishing practices, which included protecting river turtle nesting beaches, had more river turtles than areas that did not manage fishing practices. One site comparison study in Madagascar found that the abundance of different sized radiated tortoises in a protected area was more similar to that of an exploited population than to an unexploited population. Occupancy/range (2 studies): One replicated, site comparison study in Argentina found that Argentine tortoises were found in one of two protected areas and two of three unprotected areas. One before-and-after study in Brazil found that most reptile species were still present 20 years after an area was protected. Survival (2 studies): One replicated, randomized, site comparison study in the USA found that in areas with greater protections, survival of Agassiz’s desert tortoises was higher than in areas with less protections. One replicated, site comparison study in Spain found that roads running through protected areas had more reptile road deaths than roads in unprotected areas. Condition (4 studies): Two of three site comparison studies (including one replicated study) in the USA, Australia and Hong Kong found that protected areas had larger red-eared sliders and big-headed turtles compared to areas where harvesting was allowed or was thought to be occurring illegally. The other study found that eastern long-necked turtles in protected areas grew slower and were smaller than turtles in suburban areas. One site comparison study in Madagascar found that radiated tortoises in a protected area had similar genetic diversity compared to populations outside of the protected area. BEHAVIOUR (1 STUDY) Use (1 study): One replicated study in the USA found that a protected area was used by common chuckwallas. Collected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F3661https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F3661Fri, 10 Dec 2021 10:53:15 +0000Collected Evidence: Collected Evidence: Translocate adult or juvenile reptiles: Lizards Seventeen studies evaluated the effects of translocating lizards on their populations. Six studies were in New Zealand, three were in the Bahamas, two were in Australia, two were global and one was in each of the Caribean, St. Lucia, Turks and Caicos Islands and Anguilla. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (16 STUDIES) Abundance (10 studies): Three of four reviews that were global and in New Zealand and the Caribean reported that 13–32% of reptile or lizard translocations resulted in stable or growing populations (both wild-caught and captive bred animals). The other review reported that populations from eight of 13 iguana translocations survived for at least 5–20 years. Two of six studies (include one site comparison study) in St. Lucia, the Bahamas and New Zealand reported that translocated lizard populations increased over 3–10 years. Two studies reported that translocated populations remained stable for one and 6–12 years. One study reported that a translocated population declined over 1–2 years. The other study reported that a translocated population of iguanas survived for at least 40 years. Reproductive success (5 studies): Two reviews that were global and in New Zealand reported that breeding occurred in 20% and at least 30% of lizard translocations (both wild-caught and captive bred animals). Three studies (including one replicated study) in New Zealand, Turks and Caicos Islands and the Bahamas reported successful reproduction in a translocated Whitaker’s skink population, a Turks and Caicos Rock Iguana population and one of two San Salvador rock iguana populations after 14 months to five years. Survival (10 studies): Seven of eight studies (including one replicated, controlled study) in New Zealand, Turks and Caicos Islands, Australia, the Bahamas and Anguilla found that 40–85% of translocated lizards survived for at least 3 months to seven years or that no mortality was reported in the first year after release. The other study reported that at least one lesser Antillean iguana survived for at least two years. One review in New Zealand found that 9% of lizard translocations (both wild-caught and captive-bred animals) resulted in complete failure (no individuals survived). One site comparison study in New Zealand found that 1–2 years after a translocation of shore skinks, individuals representing three of four pattern types originally released still survived. Condition (1 study): One replicated, controlled study in Australia found that 67% of Napoleon’s skinks gained weight following release. BEHAVIOUR (2 STUDIES) Use (1 study): One replicated, controlled study in Australia found that all six Napoleon’s skinks translocated to restored mining sites moved into unmined forest within a week of release. Behaviour change (1 study): One replicated, before-and-after, controlled study in Australia found that provision of artificial burrows and supplementary food affected the use of bare ground areas by pygmy blue tongue lizard translocated into enclosures. Collected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F3719https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F3719Mon, 13 Dec 2021 15:36:46 +0000Collected Evidence: Collected Evidence: Breed reptiles in captivity: Snakes – Colubrids Eighteen studies evaluated the effects of breeding colubrid snakes in captivity. Ten studies were in the USA, two were the UK, two were in unknown locations and one was in each of Costa Rica, Taiwan, India and Australia. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (18 STUDIES) Reproductive success (18 studies): Seventeen studies in the USA, Costa Rica, the UK, Taiwan, Australia, India and unknown locations reported that 1–2 female colubrid snakes produced 1–12 clutches of 3–16 eggs. Ten of those studies reported hatching success of 67–100%, two reported hatching success of 25% and two reported that hatching success varied from 0–75%. Two of the studies reported that at least 18–20 eggs hatched successfully. One study also found that captive-bred offspring produced two clutches of 3–4 eggs and all hatched successfully. One study in the USA reported that three female San Francisco garter snakes produced broods of 9–35 young. Survival (5 studies): Five studies in the USA and the UK found that 2–20 captive-bred snakes survived for at least 1–3 months and 2–3 years in captivity, and that from six broods of 9–35 captive-bred San Francisco garter snakes, six young died within four months of birth. BEHAVIOUR (0 STUDIES)Collected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F3748https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F3748Tue, 14 Dec 2021 13:03:41 +0000Collected Evidence: Collected Evidence: Head-start wild-caught reptiles for release: Tortoises, terrapins, side-necked & softshell turtles Eighteen studies evaluated the effects of head-starting wild-caught tortoises, terrapins, side-necked and softshell turtles for release. Thirteen studies were in the USA, two were in Venezuela and one was in each of the Galápagos, Poland and Madagascar. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (18 STUDIES) Abundance (1 study): One controlled study in Venezuela found that 57% of captured giant sideneck river turtles were head-started individuals. Survival (13 studies): Two of three studies (including one replicated, controlled study) in the USA and Poland found that head-started European pond turtles and desert tortoises had similar survival compared to wild turtles or hatchlings released directly into the wild. The other study found that head-started northern redbelly turtles had higher survival than wild hatchling turtles. This study also found that in the first year of release, larger head-started turtles had higher survival, but in year 2–3 survival was similar for all sizes. Four of 12 studies (including nine replicated studies) in the Galápago, the USA, Madagascar and Venezuela reported that 50–100% of head-started individuals survived for three months to 1–5 years after release. Three of the studies reported that 6–43% of individuals survived for 1–3 years. Two of the studies reported that six of six, two of 10 and nine of 10 radio-tracked individuals survived 3–12 months. Two of the studies reported that annual survival was 80–100% or 3–100% in the year following release but 82–100% in subsequent years. The other study reported that some giant sideneck river turtles survived up to 14 years. Two studies also reported that survival during the captive phase was 91–100%. One study also found that more tortoises head-started in outdoor seaside pens died than did those from indoor pens. One replicated, controlled study in Venezuela found that survival of Arrau turtles during the captive phase was lower for turtles from relocated nests compared to those from nests that were not moved. Condition (5 studies): One of two replicated studies in the USA found that two-year-old head-started gopher tortoises were larger at their time of release than two-year-old tortoises released in to the wild directly after hatching. The other study found that Agassiz’s desert tortoise hatchlings grew more slowly in captivity than tortoises in the wild. Two studies (including one replicated study) in the USA found that Alabama red-bellied cooters and wood turtles grew during 12–16 months in captivity, and wood turtles showed no signs of shell malformation. One controlled study in Venezuela found that the size distribution of released head-started giant sideneck river turtles was similar to that of wild turtles when newly released individuals were excluded. BEHAVIOUR (1 STUDY) Use (1 study): One study in the USA found that 81% of desert tortoises established home ranges within 13 days of release. Collected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F3776https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F3776Wed, 15 Dec 2021 12:31:41 +0000Collected Evidence: Collected Evidence: Relocate nests/eggs for artificial incubation: Tortoises, terrapins, side-necked & softshell turtles Seventeen studies evaluated the effects of relocating nests/eggs for artificial incubation on tortoise, terrapin, side-necked & softshell turtle Ten studies were in the USA, two were in each of the Galápagos and China and one was in each of Brazil, Venezuela and Thailand. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (17 STUDIES) Reproductive success (16 studies): Two of three replicated controlled studies (including one randomized study) in Brazil, Venezuela and the USA found that Hilaire’s side-necked turtle and bog turtle nests relocated for artificial incubation had higher hatching success, or likely had higher success, than natural nests.The other study found that yellow-headed sideneck turtle nests relocated for artificial incubation had lower hatching success than natural nests and nests moved to an on-beach hatchery. One replicated study in the Galápagos reported that hatching success of five subspecies of giant tortoise nests relocated for artificial incubation was 35–100%, compared to 76–85% for natural nests of two sub species. Six of eight studies (including four replicated studies) in the USA and China reported that hatching success for artificially incubated eggs, including eggs recovered from road-killed turtles, was 60–97%, or that 314 hatchlings emerged, and 14 eggs did not hatch. One study also found that eggs collected from the wild had similar hatching success compared to oxytocin-induced eggs. The other two studies reported that hatching success of eggs or clutches was 39–54%. One replicated study in the Galápagos reported that hatching success of giant tortoise nests relocated for artificial incubation may have been higher for nests relocated longer after laying. One replicated study in the USA found that high levels of CO2 during artificial incubation of pond slider and Mississippi map turtle eggs resulted in lower hatching success compared to low CO2. One replicated, randomized study in China found that hatching success of artificially incubated Chinese three-keeled pond turtle eggs was similar across all temperatures tested. One randomized study in the USA found that hatching success of artificially incubated snapping turtle eggs was highest at intermediate levels of soil moisture. Survival (3 studies): Two studies (including one replicated study) in the USA reported that after relocating smooth softshell turtle and gopher tortoise nests for artificial incubation, two of 314 and three of 36 hatchlings died soon after emergence. One randomized study in the USA found that survival of artificially incubated snapping turtle hatchlings was lower at high soil moisture levels compared to intermediate moisture levels. Condition (4 studies): One replicated, randomized, controlled study in Brazil found that Hilaire’s side-necked turtle nests relocated for artificial incubation produced heavier hatchlings that were larger in four of five measures compared to hatchlings from natural nests. Two replicated studies (including one randomized study) in China found that modifying incubation temperatures of Chinese three-keeled pond turtle or Asian yellow pond turtle eggs had mixed effects on hatchling size and mobility or different effects on growth depending on the population eggs were sourced from. One replicated study in Thailand found that artificially incubating snail-eating turtle eggs at higher temperatures resulted in more embryos with physical deformities. BEHAVIOUR (0 STUDIES) OTHER (1 STUDY) Offspring sex ratio (1 study): One replicated study in the USA found that high levels of CO2 during artificial incubation of pond slider and Mississippi map turtle eggs resulted in a lower proportion of male hatchlings compared to low CO2 Collected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F3796https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F3796Wed, 15 Dec 2021 17:42:36 +0000Collected Evidence: Collected Evidence: Use rotational burning Seventeen studies evaluated the effects on butterflies and moths of using rotational burning. Twelve studies were in the USA, one was in South Africa and one was in Japan. COMMUNITY RESPONSE (5 STUDIES) Community composition (1 study): One replicated, site comparison study in the USA found that prairies managed by rotational burning (every 1–6 years) and grazing had a different community composition of butterflies to prairies managed by rotational burning or grazing alone. Richness/diversity (5 studies): Two replicated, site comparison studies in the USA and Japan found that pine-oak barrens and semi-natural grasslands managed by rotational burning every 2 years or 2–5 years (sometimes combined with rotational mowing) had a higher species richness of butterflies than unmanaged sites or sites managed by annual burning or mowing. However, one of these studies also found that the species richness of grassland butterflies was lower in prairies managed by rotational burning than in unmanaged prairies in one of two regions. Two replicated, site comparison studies in the USA found that the species richness of butterflies was higher on prairies burned more than one or four years ago than on prairies burned in the last one or two years under rotational burning management. One replicated, site comparison study in the USA found that prairies managed by rotational burning (every 1–6 years) and grazing had a similar species richness of butterflies to prairies managed by rotational burning or grazing alone, but a lower diversity of butterflies than sites managed by rotational burning only. One replicated, randomized, controlled study in the USA found that species richness of butterflies did not differ between prairies managed with annual rotational burning or complete burning. POPULATION RESPONSE (15 STUDIES) Abundance (15 studies): Four replicated studies (including one paired, controlled study and three site comparison studies) in the USA found that under rotational burning management the total abundance of prairie specialist, grassland and all butterflies, and of most insects including butterflies and moths, was higher on prairies burned more than one, two or four years ago, or longer ago, than on prairies burned in the last one or two years, or recently. One of these studies also found that the abundance of grassland and generalist butterflies was highest in the third year after burning, and migrant butterflies in the first year after burning. Two of these studies6,8, and an additional replicated, site comparison study in the USA found that the total abundance of butterflies, and of most insects including butterflies and moths, was higher in pine-oak barrens and prairies managed by rotational burning every 2–5 years, 2–3 years or 1–6 years than at unmanaged sites or sites managed by rotational burning or grazing alone. One of these studies also found that the abundance of butterflies was lower in prairies managed by rotational burning than in unmanaged prairies in one of two regions. Four of six replicated studies in the USA (including five site comparison studies and one randomized, controlled study) found that rotational burning in prairies, pine barrens and grasslands had mixed effects on butterflies, compared to unmanaged, hayed, grazed, mowed or completely burned sites. The fifth study found that prairies managed by rotational burning had more strongly declining populations of grass-skipper butterflies than unmanaged pine barrens or lightly managed fields. The sixth study found that for three fritillary species rotational burning in prairies did not affect abundance, but for three others, in at least one region surveyed, abundance was lower in prairies managed by rotational burning, sometimes in combination with haying, grazing and/or mowing, than in prairies managed with only haying or grazing, or in unmanaged prairies. One replicated, site comparison study in the USA reported that Karner blue butterfly abundance was similar in rotationally burned and unmanaged oak savannas and prairies. One site comparison study in the USA reported that regal fritillary abundance was higher in grasslands and oak barrens managed by rotational burning every three years (following restoration by seeding) than on unmanaged sites or remnant prairies. One replicated, site comparison study in the USA found that the abundance of regal fritillary was higher in rotationally burned prairies four years after the last burn than one or eight years after the last burn. One replicated, randomized, paired, controlled study in the USA found that, in June, the abundance of regal fritillaries in prairies burned on rotation that spring was lower than in prairies burned 1–2 years ago, but in July the abundance was higher in recently burned prairies. Survival (1 study): One replicated study in South Africa found that populations of Karkloof blue persisted for at least a year following rotational burning. BEHAVIOUR (0 STUDIES)Collected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F3883https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F3883Mon, 25 Jul 2022 15:05:14 +0100Collected Evidence: Collected Evidence: Manage hedgerows to benefit wildlife (e.g. no spray, gap-filling and laying) Seventeen studies evaluated the effects of managing hedgerows to benefit wildlife on butterflies and moths. Fourteen studies were in the UK, and one was in each of Belgium, Costa Rica and Italy. COMMUNITY RESPONSE (9 STUDIES) Richness/diversity (9 studies): Three replicated, site comparison studies in the UK and Costa Rica found that hedgerows with trees or a more complex structure had a higher species richness or diversity of butterflies and macro-moths than simpler hedgerows without trees. Three of six replicated studies (including three randomized, paired, controlled studies, one randomized, site comparison, and two site comparison studies) in the UK and Italy found that hedgerows cut to allow incremental growth had a higher diversity of caterpillars and pupae than hedgerows cut to the same size, that hedgerows kept between 1–2 m tall had a higher species richness of butterflies than hedgerows kept below 1 m tall and that fields with hedgerows of a larger volume had higher species richness of butterflies than those with hedgerows of a smaller volume, but only in one of two study years. The other three studies found that hedgerows managed according to agri-environment scheme prescriptions (including less frequent or winter cutting, gap-filling and restricted mowing, in one case in combination with other agri-environment scheme habitat) had a similar species richness of butterflies and moths to conventionally managed hedgerows. POPULATION RESPONSE (17 STUDIES) Abundance (17 studies): Four of six replicated studies (including four randomized, paired, controlled studies, one controlled study, and one paired, site comparison study) in the UK found that hedgerows cut once every 2–3 years, cut in autumn, or cut to allow incremental growth, had a higher abundance of adult butterflies and moths, moth caterpillars and pupae and brown hairstreak eggs than hedgerows cut to the same size every winter. However, one of these studies also found that hedgerows cut to allow incremental growth had a similar abundance of moth caterpillars and pupae to hedgerows cut to the same size. The other two studies found that hedgerows managed by gap-filling and cutting every three years had a similar abundance of moths to conventionally managed hedgerows, and that hedgerows cut in winter, or less frequently in autumn, had more concealed moth caterpillars, but a similar abundance of free-living caterpillars, to hedgerows cut annually in autumn. Three of five replicated, site comparison studies (including one paired study) in the UK and Costa Rica found that hedgerows with trees had a similar total abundance of macro-moths to hedgerows without trees. The other two studies found that hedgerows with trees, or with a more complex structure, had a higher abundance of butterflies and pale shining brown moths than simple hedgerows. Two replicated, site comparison studies in Belgium and Italy found that hedgerows managed with scalloped edges, or maintained at below 1 m tall, had more brown hairstreak eggs and a higher abundance of adult butterflies, than hedgerows with straight edges or allowed to grow over 2 m tall. One of two studies (including one controlled and one replicated, site comparison study) in the UK found that laid or coppiced hedgerows had a higher abundance of butterflies than unmanaged hedgerows. The other study found that managed hedgerows had a lower abundance of caterpillars than remnant hedgerows. One replicated, randomized, site comparison study in the UK found that butterfly abundance was higher in fields with hedgerows of a larger volume, but only in one of two study years. One replicated, site comparison study in the UK found that field margins next to hedgerow trees had a higher abundance of most shrub- and tree-feeding, but not grass- and herb-feeding, moth species than margins away from hedgerow trees. BEHAVIOUR (0 STUDIES)Collected Evidencehttps%3A%2F%2Fconservationevidencejournal.com%2Factions%2F3975https%3A%2F%2Fconservationevidencejournal.com%2Factions%2F3975Thu, 18 Aug 2022 09:18:48 +0100