Conservation Evidence: Evidence Data

Collected Evidence: Collected Evidence: Plant dedicated floral resources on farmlandFourteen trials in Europe and North America have recorded substantial numbers of wild bees foraging on perennial or annual sown flowering plants in the agricultural environment. Ten trials (eight replicated) have monitored bees foraging on patches sown with a high proportion of phacelia Phacelia tanacetifolia on farmland and all but one found substantial numbers of foraging wild (non-Apis) bees, particularly bumblebees Bombus spp. Six of these trials recorded the number of foraging bee species, which ranged from eight to 35. One replicated trial shows that phacelia is not very attractive to wild bees in Greece. One replicated controlled trial in the UK showed that planted perennial leguminous herbs, including clovers, were more attractive to bumblebees in landscapes with a greater proportion of arable farming. Four replicated trials have quantified the wider response of wild bee populations to planted flower patches by measuring reproductive success, numbers of nesting bees or numbers foraging in the surrounding landscape. One trial showed that planted patches of bigleaf lupine Lupinus polyphyllus in commercial apple orchards in Novia Scotia, Canada, significantly enhanced the reproductive success of blue orchard mason bees Osmia lignaria. One trial in the Netherlands showed that bee numbers and species richness are not higher in farmland 50-1,500 m away from planted flower patches. Two trials in Germany found no or relatively few species of solitary bee nesting on set-aside fields sown with phacelia or clover respectively. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F17https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F17Thu, 20 May 2010 20:02:31 +0100Collected Evidence: Collected Evidence: Scare birds from fish farms One before-and-after study from Israel found that the population of pygmy cormorants in the area increased after birds were scared away from fish farms, possibly due to lower persecution. One of two studies that examined fish stocks found that fewer fish were taken from a farm when heron distress calls were played. The other study, a literature review, found no evidence for the effects of scaring birds on fish stocks. Two replicated studies from Belgium and Australia found that using foot patrols to disturb birds from fish farms did not reduce the number of birds present or fish consumption. Ten of eleven studies from across the world, three controlled, found evidence that playing distress calls or using other acoustic deterrents (some with flashes of light) reduced the number of birds at fish farms, or changed bird behaviours. One of these involved underwater broadcasting. One study found effects were only temporary and five found that birds became habituated to noises. Four studies, one replicated and controlled, two before-and-after, found that acoustic deterrents were not effective in scaring birds. Five of seven studies, one controlled, found evidence that visual deterrents (including inflatable ‘Scarey Man’ scarecrows) reduced the number of birds at fish farms. Three found evidence for habituation to deterrents and three studies found no evidence that visual deterrents were effective. Two studies examined other deterrents, finding that trained raptors were effective but that the effects of helicopters and ultra-light aircraft were either inconclusive or very temporary. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F244https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F244Wed, 18 Jul 2012 11:00:04 +0100Collected Evidence: Collected Evidence: Use streamer lines to reduce seabird bycatch on longlines A total of eight studies and two literature reviews from coastal and pelagic fisheries across the world found strong evidence for reduced seabird bycatch on longlines when streamer lines were used. A replicated, controlled trial from the sub-Antarctic Indian Ocean found no reduction in bycatch rates when using streamer lines, whilst five studies were inconclusive, uncontrolled or had weak evidence for reductions. The effect of streamer lines appears to vary between seabird species: northern fulmars Fulmarus glacialis were consistently caught at lower rates when streamers were used but shearwaters Puffinus spp. and white-chinned petrels Procellaria aequinoctialis were caught at similar rates with and without streamers in one study each. The three studies that investigated the use of multiple streamer lines all found that fewer birds were caught when two streamer lines were used, compared to one, with even fewer caught when three were used. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F285https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F285Tue, 24 Jul 2012 14:37:19 +0100Collected Evidence: Collected Evidence: Restore or create forests Thirteen of 15 studies from across the world found that bird communities in restored forests were similar to original forests or that species returned to restored sites, that species recovered significantly better than ats unrestored site, that species richness, diversity or abundances increased over time or that restoration techniques themselves improved over time. Nine of the studies found that some species did not return to restored sites, or were less common than in original forests. One study also found that overall territory density decreased over time and another found that territory densities were similar between sites planted with oak Quercus spp. saplings and unplanted sites. One study from the USA found that productivity of birds was similar in restored and natural forests. Another found that productivity was lower. A study from the USA found that fast-growing cottonwood forests less than ten years old held more territories and had higher diversity than similarly-aged oak forests. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F360https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F360Mon, 30 Jul 2012 16:58:06 +0100Collected Evidence: Collected Evidence: Maintain upland heath/moorland Of 15 individual studies from the UK, eight (including three replicated, controlled trials, of which one also randomized) found that appropriate management can help to maintain the conservation value of upland heath or moorland. Of these eight studies, four tested the effectiveness of excluding or reducing grazing. Impacts included increases in the abundance of Scottish primrose and other broadleaved plant species, heather cover and numbers of true bugs, biomass of arthropods associated with the bird diet, number and diversity of moths and benefits to black grouse. Among other treatments, repeated cutting and grazing by goats were found to be effective in controlling the dominance of certain grass species. A review found management under the Environmentally Sensitive Areas scheme had broadly positive effects on moorland birds and a reduction in grazing benefited most bird species and increased heath vegetation and heather cover. A replicated before-and-after study found that moorland management under the Environmentally Sensitive Area scheme maintained the number of plant species in two out of three areas. Three studies (including one before-and-after trial) reported mixed results for invertebrates or birds, where management to maintain upland heath or moorland benefited some but not all species or where the effect depended on the vegetation type. Treatments tested included reducing grazing intensity and grouse moor management (burning and predator control). Four studies (including one controlled site comparison and two reviews) found that reducing the intensity of livestock grazing reduced the abundance of soil organisms including invertebrates, bacteria or fungi. A randomized, replicated before-and-after study found that heather cover declined over nine years on a moorland site managed under the Environmentally Sensitive Areas scheme in which grazing intensity had increased. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F647https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F647Wed, 17 Oct 2012 17:51:16 +0100Collected Evidence: Collected Evidence: Restore wetland Seventeen studies investigated the effectiveness of wetland restoration for amphibians. Ten site comparison studies (including eight replicated studies) in Canada and the USA compared amphibian numbers in restored and natural wetlands. Eight found that amphibian abundance, numbers of species and species composition were similar. Two found that the number of species or abundance was lower and species composition different in restored wetlands. One found that restored wetlands were used more or less depending on the habitat surrounding natural wetlands. One global review found that in 89% of cases, restored and created wetlands had similar or higher amphibian abundance or numbers of species to natural wetlands. Seven of nine studies (including six site comparison and/or replicated studies) in Canada, Taiwan and the USA found that wetland restoration increased numbers of amphibian species, with breeding populations establishing in some cases. Three found that numbers of species or abundance did not increase with restoration. Two found mixed effects, with restoration maintaining or increasing abundance of individual species. Three replicated studies (including two site comparison studies) in the USA found that numbers of species in restored wetlands were affected by wetland size, proximity to source ponds and seasonality, but not wetland age. Three studies (including two replicated, site comparison studies) in Taiwan and the USA found that restored wetlands were colonized by three to eight amphibian species. One before-and-after study in the USA found that three target species did not recolonize restored wetlands. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F879https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F879Thu, 12 Sep 2013 15:34:57 +0100Collected Evidence: Collected Evidence: Use prescribed fire: effects on mature trees Four of eight studies (including two replicated, randomized, controlled studies) from the USA found that prescribed fire decreased tree cover, density and diversity. One study found it increased tree cover and three found no effect or mixed effects of prescribed fire on cover and density of trees. Seven studies from the USA (including one replicated, randomized, controlled study) found that prescribed fire increased tree mortality. One of three studies from the USA (including one replicated, controlled study) found that prescribed fire increased tree size while two found no effect of prescribed fire on tree size. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1217https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1217Fri, 20 May 2016 14:09:36 +0100Collected Evidence: Collected Evidence: Log/remove trees within forests: effects on mature trees Three of seven studies (including two replicated, controlled studies) in Bolivia, Central African Republic, China, Finland, Malaysia, Uganda and the USA found that logging trees in forests decreased the density and cover of trees. Two found it increased tree density and two found no effect of logging on tree density. Three of six studies (including one replicated, randomized, controlled study) in Bolivia, Canada, China, Kenya, Malaysia and the USA found that logging trees in forests increased tree size. Two found it decreased tree size and one found no effect of logging on tree size. Two of four studies (including one paired site study) in Bolivia, China, Mexico and Papua New Guinea found that logging trees in forests decreased tree species richness and diversity. One study found it increased diversity and one found no effect of logging on tree species diversity. One replicated, controlled study in Canada found that logging trees in forests increased tree mortality rate. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1271https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1271Mon, 13 Jun 2016 08:55:36 +0100Collected Evidence: Collected Evidence: Crop production: Use no tillage instead of reduced tillageCrop yield (15 studies) Cereals (7 studies): Three replicated, randomized, controlled studies from Spain found higher cereal yields in plots with no tillage, compared to reduced tillage. One of these studies also found lower cereal yields in some comparisons. One replicated, randomized, controlled study from Spain found lower cereal yields in plots with no tillage, compared to reduced tillage, in some comparisons. Three replicated, randomized, controlled studies from Australia, Lebanon, and Spain found similar cereal yields in plots with no tillage or reduced tillage, in all comparisons. Fruits and vegetables (3 studies): Three replicated, randomized, controlled studies from Italy found lower fruit or vegetable yields in plots with no tillage, compared to reduced tillage, in some comparisons. Two of these studies also found higher yields, in some comparisons. Legumes (3 studies): Two replicated, controlled studies from Italy and Spain found higher legume yields in plots with no tillage, compared to reduced tillage, in some or all comparisons. One replicated, controlled study from Lebanon found similar legume yields in plots with no tillage, compared to reduced tillage. Oilseeds (1 study): One replicated, randomized, controlled study from Spain found lower sunflower seed yields in plots with no tillage, compared to reduced tillage, in some comparisons. Crop residues (6 studies): Three replicated, controlled studies from Lebanon and Spain found higher straw yields in plots with no tillage, compared to reduced tillage, in some or all comparisons. One replicated, randomized, controlled study from Spain found lower straw yields in plots with no tillage, compared to reduced tillage. Two replicated, controlled studies from Italy and Spain found similar straw yields in plots with no tillage or reduced tillage. Crop quality (3 studies): One replicated, randomized, controlled study from Spain found larger peas, and more peas in a pod, in plots with no tillage, compared to reduced tillage, in one of four comparisons. One replicated, controlled study from Italy found similarly sized faba beans, and similar numbers of beans in a pod, in plots with no tillage, compared to reduced tillage. One replicated, randomized, controlled study from Spain found differences in the nutritional values of sunflower seeds in plots with no tillage, compared to reduced tillage. · Crop yield (15 studies) o Cereals (7 studies): Three replicated, randomized, controlled studies from Spain2,4,13 found higher cereal yields in plots with no tillage, compared to reduced tillage. One of these studies10410417Angás, P.Lampurlanés, J.Cantero-Martínez, C.Tillage and N fertilization: Effects on N dynamics and Barley yield under semiarid Mediterranean conditionsSoil and Tillage ResearchSoil and Tillage Research59-71871Conservation tillageNitrogen fertilizationN fertilizer efficiencyPhysiological N use efficiency20065//0167-1987http://www.sciencedirect.com/science/article/pii/S0167198705000991http://dx.doi.org/10.1016/j.still.2005.02.0362 also found lower cereal yields in some comparisons. One replicated, randomized, controlled study from Spain868617López-Garrido, R.Madejón, E.León-Camacho, M.Girón, I.Moreno, F.Murillo, J. M.Reduced tillage as an alternative to no-tillage under Mediterranean conditions: A case studySoil and Tillage ResearchSoil and Tillage Research40-47140Tillage systemsSoil conditionsCrop performanceSeed qualitySunflower20147//0167-1987http://www.sciencedirect.com/science/article/pii/S0167198714000300http://dx.doi.org/10.1016/j.still.2014.02.00811 found lower cereal yields in plots with no tillage, compared to reduced tillage, in some comparisons. Three replicated, randomized, controlled studies from Australia19119117Manalil, SudheeshFlower, KenSoil water conservation and nitrous oxide emissions from different crop sequences and fallow under Mediterranean conditionsSoil and Tillage ResearchSoil and Tillage Research123-129143AustraliaDroughtFallowNitrous oxide201411//0167-1987http://www.sciencedirect.com/science/article/pii/S0167198714001214http://dx.doi.org/10.1016/j.still.2014.06.00612, Lebanon777717Yau, S. K.Sidahmed, M.Haidar, M.Conservation versus Conventional Tillage on Performance of Three Different CropsAgronomy JournalAgronomy Journal269-2761022010Madison, WIAmerican Society of Agronomyhttp://dx.doi.org/10.2134/agronj2009.024210.2134/agronj2009.0242English3, and Spain848417Hernanz, J. L.López, R.Navarrete, L.Sánchez-Girón, V.Long-term effects of tillage systems and rotations on soil structural stability and organic carbon stratification in semiarid central SpainSoil and Tillage ResearchSoil and Tillage Research129-141662Long-term effectTillageCrop rotationAggregate stabilitySoil organic carbonSemiarid conditions20027//0167-1987http://www.sciencedirect.com/science/article/pii/S0167198702000211http://dx.doi.org/10.1016/S0167-1987(02)00021-11 found similar cereal yields in plots with no tillage or reduced tillage, in all comparisons. o Fruits and vegetables (3 studies): Three replicated, randomized, controlled studies from Italy9,10,15 found lower fruit or vegetable yields in plots with no tillage, compared to reduced tillage, in some comparisons. Two of these studies9,15 also found higher yields, in some comparisons. o Legumes (3 studies): Two replicated, controlled studies from Italy10710717Giambalvo, DarioRuisi, PaoloSaia, SergioDi Miceli, GiuseppeFrenda, Alfonso SalvatoreAmato, GaetanoFaba bean grain yield, N2 fixation, and weed infestation in a long-term tillage experiment under rainfed Mediterranean conditionsPlant and SoilPlant and Soil215-227360120122012//1573-5036http://dx.doi.org/10.1007/s11104-012-1224-510.1007/s11104-012-1224-57 and Spain838317Santín-Montanyá, M. I.Zambrana, E.Fernández-Getino, A. P.Tenorio, J. L.Dry pea (Pisum sativum L.) yielding and weed infestation response, under different tillage conditionsCrop ProtectionCrop Protection122-12865DiversityLegume-cropsSemi-arid conditionsYieldWeeds201411//0261-2194http://www.sciencedirect.com/science/article/pii/S0261219414002373http://dx.doi.org/10.1016/j.cropro.2014.07.017 Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1358https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1358Fri, 05 May 2017 11:33:13 +0100Collected Evidence: Collected Evidence: Water: Use no tillage in arable fieldsWater use (1 study): One replicated, randomized, controlled study from Spain found that barley used water more efficiently in plots without tillage, compared to plots with tillage, in some comparisons. Water availability (14 studies): Nine controlled studies (eight replicated and randomized) from Spain and the USA found more water in soils without tillage, compared to soils with tillage, in some or all comparisons. One replicated, randomized, controlled study from Lebanon found less water in soils without tillage, compared to soils with tillage, in some comparisons. Three replicated, controlled studies (two randomized) from Spain and the USA sometimes found more water, and sometimes found less water, in soils without tillage, compared to soils with tillage. One replicated, randomized, controlled study from Spain found lower porosity in soils without tillage, compared to soils with tillage, in some comparisons. Pathogens and pesticides (0 studies) Nutrients (0 studies) Sediments (0 studies)Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1384https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1384Mon, 15 May 2017 15:49:43 +0100Collected Evidence: Collected Evidence: Reduce number of livestock Two before-and-after trials in the UK and South Africa and one replicated, controlled study in the UK found that the reducing or stopping grazing increased the abundance or cover of shrubs. Two site comparison studies in the UK found that cover of common heather declined in sites with high livestock density, but increased in sites with low livestock density. One site comparison study in the Netherlands found that dwarf shrub cover was higher in ungrazed sites. One replicated, randomized, before-and-after study in Spain found that reducing grazing increased the cover of western gorse. One randomized, controlled trial and one before-and-after trial in the USA found that stopping grazing did not increase shrub abundance. One site comparison study in France found that ungrazed sites had higher cover of ericaceous shrubs, but lower cover of non-ericaceous shrubs than grazed sites. One site comparison study in the UK found that reducing grazing had mixed effects on shrub cover. One replicated, randomized, controlled study in the UK found that reducing grazing increased vegetation height. However, one replicated, controlled, paired site, site comparison study in the UK found that reducing grazing led to a reduction in the height of heather plants. Two site comparison studies in France and the Netherlands found that ungrazed sites had a lower number of plant species than grazed sites. One replicated, controlled, paired, site comparison study in Namibia and South Africa found that reducing livestock numbers increased plant cover and the number of plant species. One controlled study in Israel found that reducing grazing increased plant biomass. However, one randomized, site comparison on the island of Gomera, Spain found that reducing grazing did not increase plant cover and one replicated, controlled study in the UK found that the number of plant species did not change . One replicated, controlled study in the UK found no change in the cover of rush or herbaceous species as a result of a reduction in grazing. Two site comparison studies in France and the Netherlands found that grass cover and sedge cover were lower in ungrazed sites than in grazed sites. One randomized, controlled study in the USA found a mixed effect of reducing grazing on grass cover. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1607https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1607Sun, 22 Oct 2017 09:51:03 +0100Collected Evidence: Collected Evidence: Allow shrubland to regenerate without active management Five before-and-after trials (two of which were replicated) in the USA, UK, and Norway, found that allowing shrubland to recover after fire without any active management increased shrub cover or biomass. One replicated, paired, site comparison in the USA found that sites that were allowed to recover without active restoration had similar shrub cover to unburned areas. One controlled, before-and-after trial in the USA found no increase in shrub cover. One before-and-after trial in Norway found an increase in heather height. One before-and-after trial in Spain found that there was an increase in seedlings for one of three shrub species. Two replicated, randomized, controlled, before-and-after trials in Spain and Portugal found that there was an increase in the cover of woody plant species. One before-and-after study in Spain found that cover of woody plants increased, but the number of woody plant species did not. One replicated, before-and-after study in South Africa found that the height of three protea species increased after recovery from fire. One before-and-after trial in South Africa found that there was an increase in vegetation cover, but not in the number of plant species. One before-and-after trial in South Africa found an increase in a minority of plant species. Two before-and-after trials in the USA and UK found that allowing shrubland to recover after fire without active management resulted in a decrease in grass cover or biomass. One controlled, before-and-after trial in the USA found an increase in the cover of a minority of grass species. One before-and-after study in Spain found that cover of herbaceous species declined. One replicated, before-and-after study in the UK found mixed effects on cover of wavy hair grass. One controlled, before-and-after trial in the USA found no increase in forb cover. One replicated, randomized, controlled before-and-after trial in Spain found that herb cover declined after allowing recovery of shrubland after fire. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1679https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1679Mon, 23 Oct 2017 09:08:16 +0100Collected Evidence: Collected Evidence: Hold translocated mammals in captivity before release Fifteen studies evaluated the effects of holding translocated mammals in captivity before release. Four studies were in the USA, two were in Australia and one was in each of India, Canada, Switzerland, Croatia and Slovenia, the USA and Canada, the UK, France, Spain and South Africa. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (13 STUDIES) Abundance (2 studies): Two studies (one replicated, before-and-after study) in Croatia and Slovenia and the USA found that following translocation, with time in captivity prior to release, Eurasian lynx established an increasing population and Allegheny woodrat numbers in four of six sites increased over the first two years. Reproductive success (4 studies): Four studies in Croatia and Slovenia, Spain, the USA and Canada and Australia found that following translocation, with time in captivity prior to release, Eurasian lynx established a breeding population, and swift foxes, European otters and red-tailed phascogales reproduced. Survival (10 studies): Two studies (one controlled) in the UK and USA found that being held for longer in captivity before release increased survival rates of translocated European hedgehogs and, along with release in spring increased the survival rate of translocated Canada lynx in the first year. Four of six studies in India, the USA and Canada, the USA, France, South Africa and Australia found that following translocation, with time in captivity prior to release, most swift foxes and greater Indian rhinoceroses survived for at least 12-20 months, 48% of Eurasian lynx survived for 2–11 years and red-tailed phascogales survived for at least six years. The other two studies found that most kangaroo rats and all rock hyraxes died within 5-87 days. A replicated, controlled study in Canada found that translocated swift foxes that had been held in captivity prior to release had higher post-release survival rates than did released captive-bred animals. Condition (3 studies): A randomised, controlled study in Australia found that holding translocated eastern bettongs in captivity before release did not increase their body mass after release compared to animals released directly into the wild. A controlled study the UK found that being held for longer in captivity before release, reduced weight loss after release in translocated European hedgehogs. A study in Spain found that offspring of translocated European otters that were held in captivity before release, had similar genetic diversity to donor populations. Occupancy/range (2 studies): A study in the USA found that most translocated and captive-bred mountain lions that had been held in captivity prior to release established home ranges in the release area. A study in Croatia and Slovenia and review in Switzerland found that following translocation, with time in captivity prior to release, the range of Eurasian lynx increased over time. BEHAVIOUR (0 STUDIES)Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2458https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2458Tue, 02 Jun 2020 11:23:58 +0100Collected Evidence: Collected Evidence: Provide supplementary food during/after release of translocated mammals Sixteen studies evaluated the effects of providing supplementary food during/after release of translocated mammals. Four studies were in the UK, two were in each of the USA, France, Australia and Argentina, and one was in each of Italy, Spain, Ireland and South Africa. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (15 STUDIES) Abundance (2 studies): A controlled study in Spain found that providing supplementary food during translocation did not increase European rabbit abundance. A study in France found that following supplementary feeding in a holding pen prior to release, a translocated deer population increased over six years. Reproductive success (4 studies): Three studies (one replicated) in the USA, Italy and Ireland found that having been provided with supplementary food in holding pens prior to release, translocated black-tailed prairie dogs, a pair of Eurasian badgers and most female red squirrels reproduced in the wild. A study in the UK found that some translocated pine martens released from holding pens and then provided with supplementary food and nest boxes bred in the first year after release. Survival (10 studies): Six of 10 studies (including one replicated and one controlled study) in the UK, France, Italy, Ireland, South Africa, USA, Argentina and Australia found that at sites with supplementary food in holding pens before (and in two cases after) release, translocated populations of black-tailed prairie dogs, approximately half of female roe deer and over half of red squirrels, Eurasian badgers, pine martens and released rehabilitated or captive reared giant anteaters survived for between one month and at least two years. Four studies found that at translocation release sites with provision of supplementary food, in most cases artificial refuges and in one case water, no red squirrels, rock hyraxes or burrowing bettongs survived over 2-5 months and most translocated Tipton and Heermann’s kangaroo rat spp. died within five days. A controlled study in France found that translocated European rabbits provided with supplementary food in holding pens for three days prior to release had higher female (but not male) survival rates immediately following release compared to those released directly. A controlled study in the UK found that survival of translocated and rehabilitated European hedgehogs that were provided with supplementary food after release varied with release method. Condition (2 studies): One of three studies (including one replicated, one controlled and two before-and-after studies) in the UK and Australia found that translocated common dormice gained weight after being provided with supplementary food. One found that translocated eastern bettongs did not have increased body weights after provision of supplementary food in fenced enclosures prior to release. The other found that translocated and rehabilitated European hedgehogs provided with food after release all lost body mass, with effects varying with release method. BEHAVIOUR (2 STUDIES) Use (1 study): A controlled study in Australia found that supplementary feeding stations were visited by translocated burrowing bettongs. Behaviour change (1 study): A controlled study in Argentina found that after being provided with supplementary food and kept in holding pens, released captive-bred giant anteaters were less nocturnal than wild-born rehabilitated and released individuals. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2470https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2470Wed, 03 Jun 2020 14:59:22 +0100Collected Evidence: Collected Evidence: Provide supplementary food during/after release of captive-bred mammals Fifteen studies evaluated the effects of providing supplementary food during/after release of captive-bred mammals. Four studies were in Australia, two were in each of the USA, China and Argentina, and one was in each of Poland, the UK, Oman and Saudi Arabia. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (14 STUDIES) Abundance (5 studies): Four studies (one replicated, one before-and-after study) and one review in Poland, Oman, China and Australia found that following provision of supplementary food (and in one case water) to released captive-bred animals, populations of European bison increased more than six-fold over 20 years, Arabian oryx increased over 14 years, eastern-barred bandicoots increased for the first five years before declining, Père David's deer increased more than six-fold over 12 years and Przewalski’s horses (enclosed in winter) increased over 11 years. Reproductive success (9 studies): Eight studies (including two replicated and one before-and-after study) and one review in Poland, the UK, China, the USA, Australia and Saudi Arabia found that following the provision of supplementary food (and in one case water or artificial nests) after release of captive-bred animals, some from holding pens, European bison, European otters, Père David's deer, eastern-barred bandicoots, Przewalski’s horses and some captive-bred red wolves successfully reproduced, Arabian gazelles started breeding in the year following releases and sugar gliders established a breeding population. Survival (6 studies): Four of six studies (one controlled, before-and-after study) in the UK, USA, Argentina and Australia found that following the provision of supplementary food (and in one case water or nest boxes) after release of captive-bred animals, many from holding pens, 19% of red wolves survived for at least seven years, Eurasian otters survived for at least two years, over half the giant anteaters (some rehabilitated) survived for at least six months and hare-wallabies survived at least two months. Two of the studies found that red-tailed phascogales survived for less than a year and most Mexican wolves survived less than eight months. BEHAVIOUR (1 STUDY) Behaviour change (1 study): A controlled study in Argentina found that after being provided with supplementary food and kept in holding pens, released captive-bred giant anteaters were less nocturnal in their activity patterns than released wild-born rehabilitated individuals. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2527https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2527Mon, 08 Jun 2020 14:23:58 +0100Collected Evidence: Collected Evidence: Install wildlife warning reflectors along roads Fifteen studies evaluated the effects on mammals of installing wildlife warning reflectors along roads. Nine studies were in the USA, three were in Austalia, two were in Germany and one was in Denmark. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (10 STUDIES) Abundance (1 study): A before-and-after study in Australia found that when warning reflectors were installed (along with speed restrictions, reflective wildlife signs, rumble strips, wildlife escape ramps and an educational pamphlet) a small population of eastern quoll re-established in the area. Survival (10 studies): Five of eight controlled or before-and-after studies in the USA and Germany found that wildlife warning reflectors did not reduce collisions between vehicles and deer. Two studies found that vehicle-deer collisions were reduced by reflectors and one found that collisions were reduced in rural areas but increased in suburban areas. A before-and-after study in Australia found that when warning reflectors were installed (along with speed restrictions, reflective wildlife signs, rumble strips, wildlife escape ramps and an educational pamphlet) vehicle collisions with Tasmanian devils, but not eastern quolls, decreased. A review of two studies in Australia found mixed responses of mammal road deaths to wildlife warning reflectors. BEHAVIOUR (5 STUDIES) Behaviour change (5 studies): Three of four studies (including three controlled studies), in the USA, Denmark and Germany, found that wildlife warning reflectors did not cause deer to behave in ways that made collisions with vehicles less likely (such as by avoiding crossing roads). The other study found that deer initially responded to wildlife reflectors with alarm and flight but then became habituated. A replicated, controlled study in Australia found that one of four reflector model/colour combinations increased fleeing behaviour of bush wallabies when lights approached. The other combinations had no effect and none of the combinations affected red kangaroos. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2591https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2591Thu, 11 Jun 2020 09:30:25 +0100Collected Evidence: Collected Evidence: Exclude or remove livestock from historically grazed brackish/salt marshes Fifteen studies evaluated the effects, on vegetation, of excluding or removing livestock from historically grazed brackish/salt marshes. There were five studies in Germany. There were two studies in the UK, Denmark and the Netherlands. There was one study in each of the USA, Sweden, France and Argentina. Livestock were sheep, cattle, sheep and cattle, cattle and horses, or unspecified. There was overlap in the sites used in two studies. Two other studies took place in one marsh, but with different experimental set-ups. VEGETATION COMMUNITY Overall extent (1 study): One controlled study of a salt marsh in Germany reported that in a plot fenced to exclude cattle for eight years, the total vegetated area was greater than in a plot that remained grazed. Community types (1 study): One site comparison study of brackish and salt marshes in Germany reported that reducing (or stopping) grazing affected the nature of transitions between vegetation types over time, but that the precise effect varied with environmental conditions. Community composition (5 studies): Three paired studies (two also replicated and controlled) in brackish/salt marshes in France, Argentina and the Netherlands reported that the effect of excluding livestock for 5–30 years on the overall plant community composition depended on plot elevation/flooding regime. In one of these studies, the effect of livestock exclusion was not separated from the effect of general legal protection. Two studies in one salt marsh in Denmark reported that excluding livestock had little effect on the identity of plant species in the community after six years. Overall richness/diversity (6 studies): Two studies (one controlled, one before-and-after) in one salt marsh in Denmark reported that excluding sheep and cattle for 6–7 years had no effect on overall plant species richness. One replicated, paired, controlled study in a salt marsh in the Netherlands reported that plots fenced to exclude cattle for seven years had lower plant species richness than areas that remained grazed. Two controlled studies (one also replicated and paired) in salt marshes in Germany found that the effect of removing sheep on overall plant species richness depended on the scale of measurement and the grazing intensity used for comparison – with inconsistent results across these studies even for similar scales and intensities. One paired, site comparison study of salt marshes in Argentina found that the effect of excluding cattle (along with legal protection) increased plant species richness at lower elevations, but did not significantly affect plant diversity at any elevation. VEGETATION ABUNDANCE Overall abundance (4 studies): Three studies (two controlled, one before-and-after) in salt marshes in the UK and Denmark reported that excluding livestock for 2–6 years maintained or increased overall vegetation abundance (although in one study, only by a small amount). One controlled study in a salt marsh in Germany found that a paddock left ungrazed for 16–18 years had greater overall vegetation cover than lightly or heavily grazed paddocks, but lower cover than a moderately grazed paddock. Individual species abundance (11 studies): Eleven studies quantified the effect of this action on the abundance of individual plant species. For example, five studies (four controlled, one before-and-after) on salt marshes in the UK, Denmark, Germany and the Netherlands reported that excluding livestock for 2–8 years reduced (or prevented increases in) cover of saltmarsh grass Puccinellia maritima. However, two controlled studies (one also replicated and paired) on salt marshes in Denmark and Sweden reported greater saltmarsh grass cover in areas fenced to exclude livestock for 1–6 years than in areas that remained grazed. Four studies (three controlled, one before-and-after) on salt marshes in Denmark and Germany reported that excluding or removing livestock for 4–16 years increased cover of sea purslane Halimione portulacoides. VEGETATION STRUCTURE Height (5 studies): Five controlled studies (two also replicated and paired) in salt marshes in Sweden and Germany, and brackish wet grassland in the UK, found that ungrazed plots (livestock excluded or removed) contained taller vegetation than plots that remained grazed. Vegetation was surveyed after one month, 1–8 years or 16–22 years. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2967https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2967Thu, 25 Mar 2021 14:15:09 +0000Collected Evidence: Collected Evidence: Use prescribed fire to maintain or restore disturbance: freshwater marshes Fifteen studies evaluated the effects, on vegetation, of using prescribed fire to maintain or restore disturbance in freshwater marshes. Ten studies were in the USA. Two studies, based on one experimental set-up, were in the Netherlands. There was one study in each of the UK, Romania and South Africa. VEGETATION COMMUNITY Community composition (4 studies): Of four replicated, controlled studies (three also before-and-after) in freshwater wetlands in the USA, two found that burning (sometimes along with other interventions) significantly affected the overall plant community composition in the following 2–5 years. The other two studies found that burning had no clear or significant effect on the overall plant community composition over the following two years. One of these studies also found that the plant community in burned marshes was less similar to pristine local marshes than the plant community in unburned marshes, after two years. Overall richness/diversity (8 studies): Four replicated, paired, controlled studies in freshwater marshes/wet meadows in the UK and the USA found that burning had no significant effect on overall plant species richness and/or diversity over 1–2 growing seasons. However, three replicated, paired, controlled studies in the UK and the USA reported that burning increased plant species richness or diversity after 1–3 growing seasons. Two replicated studies (including one paired, site comparison) in the USA and South Africa reported that burning reduced plant species richness or diversity after 1–3 growing seasons. However, the study in the USA also reported that burning increased richness after 4–8 growing seasons. VEGETATION ABUNDANCE Overall abundance (5 studies): Four studies (including two randomized, paired, controlled, before-and-after) in freshwater marshes/wet meadows in the USA found that prescribed burning had no significant effect on overall vegetation abundance (biomass or cover) after 1–3 growing seasons. One replicated, randomized, paired, controlled study in a freshwater marsh in the USA reported that burned plots contained less vegetation biomass, one year after the latest burn, than unburned plots. Characteristic plant abundance (1 study): One replicated, randomized, controlled, before-and-after study of overgrown freshwater marshes in the USA reported that of 26 plant taxa that became more frequent after burning (along with other interventions), 16 were obligate wetland taxa. Herb abundance (1 study): One replicated, paired, site comparison study of sedge meadows in the USA found that burned meadows typically contained similar cover of herbaceous plant groups (grasses, sedges/rushes and forbs) to unburned meadows, after 1–8 growing seasons. Tree/shrub abundance (2 studies): One replicated, randomized, paired, controlled, before-and-after study in a degraded, shrubby wet prairie the USA found that over three years, burning reduced woody plant cover. One replicated, before-and-after study of freshwater marshes within a forest plantation in South Africa reported that burning never increased overall tree density five months later, although the precise effect apparently depended on site wetness. Algae/phytoplankton abundance (1 study): One controlled study in a freshwater marsh in the USA found that burned plots contained a greater abundance (cover and biomass) of surface-encrusting algae, over the following 72 days, than unburned plots. Individual species abundance (9 studies): Nine studies quantified the effect of this action on the abundance of individual plant species. The nine studies (including eight controlled or site comparison) in the Netherlands, the UK, the USA, Romania and South Africa reported mixed effects of burning on dominant herbaceous species, depending on the species, metric, site conditions and/or time after burning. VEGETATION STRUCTURE Height (5 studies): Four studies (including one replicated, randomized, paired, controlled) – in reedbeds in the UK and Romania, a marsh in the USA and freshwater marshes within a forest plantation in South Africa – found that burned plots contained shorter vegetation than unburned plots in the subsequent growing season. One study in a marsh in the USA reported that over the 50 days after prescribed burning, the average height of sawgrass Cladium jamaicense increased. Diameter/perimeter/area (3 studies): Two replicated, paired, controlled studies in reedbeds in the Netherlands and the UK found that common reed Phragmites australis stems were typically thicker in spring-burned plots than unburned plots, in the subsequent growing season. However, one site comparison study of reedbeds in Romania found that common reed stems were thinner in winter-burned plots than unburned plots, in the following spring. OTHER Survival (1 study): One replicated, randomized, paired, controlled, before-and-after study in a degraded, shrubby wet prairie the USA found that woody plants had a lower survival rate, after one year, in burned plots than in unburned plots. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3054https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3054Fri, 02 Apr 2021 08:55:35 +0100Collected Evidence: Collected Evidence: Create grooves and small protrusions, ridges or ledges (1–50 mm) on intertidal artificial structures Sixteen studies examined the effects of creating groove habitats and small protrusions, ridges or ledges on intertidal artificial structures on the biodiversity of those structures. Five studies were on island coastlines in the Singapore Strait, seven were in estuaries in northwest USA, southeast Australia and Hong Kong, and one was in each of a marina in northern Israel and a port in southeast Spain. One was on an open coastline and in an estuary in the UK, and one was in 14 estuaries and bays worldwide. COMMUNITY RESPONSE (14 STUDIES) Overall community composition (9 studies): Three of five replicated, randomized, controlled studies (including one paired sites, before-and-after study) in Singapore and Israel found that creating groove habitats and small ridges/ledges on intertidal artificial structures, along with holes and environmentally-sensitive material in one, altered the combined macroalgae and invertebrate community composition on structure surfaces. Two studies found that creating grooves and small ridges, along with pits in one, had mixed effects on the community composition depending on the site, the presence of water-retaining and light-shading covers, and the size and arrangement of grooves and ridges. In contrast, one of the studies found that varying the size and arrangement had no significant effect. One of the studies, along with four other replicated, randomized, controlled studies in Singapore, Hong Kong and Australia, reported that groove habitats and small ridges/ledges, along with pits or holes and environmentally-sensitive material in two studies, supported species that were absent from structure surfaces without grooves and ridges/ledges. Overall richness/diversity (11 studies): Six of 11 replicated, randomized, controlled studies (including one paired sites, before-and-after study) in Singapore, the USA, Israel, the UK, Hong Kong, Australia and worldwide found that creating groove habitats and small ridges/ledges on intertidal artificial structures, along with pits or holes and environmentally-sensitive material in two studies, increased the combined macroalgae and invertebrate species diversity and/or richness on structure surfaces. Five studies found that creating grooves and small protrusions/ridges/ledges, along with large ledges or using environmentally-sensitive material in two, had mixed effects on species diversity and/or richness, depending on the depth/height of grooves and ridges, the presence of large ledges on structure surfaces, the shore level, species group and site. One of the studies found that varying the size and arrangement of grooves and ridges increased the species richness, while one found that effects depended on the shore level. One of the studies found that partially-covering grooves and ridges with water-retaining and light-shading covers increased the species richness. Algal richness/diversity (2 studies): One of two replicated, randomized, controlled studies in Singapore and worldwide found that creating groove habitats and small ridges on intertidal artificial structures had mixed effects on the macroalgal species richness on structure surfaces, depending on the size of grooves and ridges and the location. One study found that creating grooves and ridges, along with pits, increased the species richness, regardless of their size and arrangement. Invertebrate richness/diversity (2 studies): One of two replicated, randomized, controlled studies in Australia and worldwide found that creating groove habitats and small ridges on intertidal artificial structures had mixed effects on the mobile and non-mobile invertebrate species richness on structure surfaces, depending on the size of grooves and ridges and the location. One study found that creating grooves and small ledges increased the mobile invertebrate species richness. Fish richness/diversity (3 studies): Two of three replicated, randomized, controlled studies in Australia found that creating groove habitats and small ridges/ledges on intertidal artificial structures did not increase the fish species richness on and around structure surfaces. One study found that creating grooves and ridges had mixed effects on fish species richness depending on the site. POPULATION RESPONSE (13 STUDIES) Overall abundance (6 studies): Two of six replicated, randomized, controlled studies in Singapore, the USA and Australia found that creating groove habitats and small ridges/ledges on intertidal artificial structures did not increase the combined macroalgae and invertebrate abundance on structure surfaces. Two studies found that creating grooves and small protrusions/ridges, along with large ledges in one, and when partially-covered with water-retaining and light-shading covers in the other, did increase abundance. Two found that creating grooves and small ridges/ledges, along with pits in one, had mixed effects on abundance depending on the size and arrangement of grooves and ridges/ledges, the shore level and/or the site. Algal abundance (3 studies): Two of three replicated, randomized, controlled studies in Singapore, the USA and worldwide found that creating groove habitats and small protrusions/ridges on intertidal artificial structures, along with large ledges in one, had mixed effects on rockweed or combined macroalgal abundance, depending on the presence of large ledges on structure surfaces, the depth/height of grooves and ridges, the shore level and/or the site. One study found that creating grooves and small ridges, along with pits, did not increase the macroalgal abundance, regardless of the size and arrangement of grooves and ridges. Invertebrate abundance (7 studies): Five of seven replicated, randomized, controlled studies in the USA, Singapore, the UK, Hong Kong, Australia and worldwide found that creating groove habitats and small protrusions/ridges/ledges on intertidal artificial structures, along with large ledges or using environmentally-sensitive material in two, had mixed effects on mobile invertebrate, non-mobile invertebrate, limpet, mussel, juvenile oyster and/or barnacle abundances, depending on the depth/height of grooves and ridges, the presence of large ledges or water-retaining and light-shading covers, the shore level, and/or the site. Two studies found that creating grooves and small ridges/ledges increased oyster but not mobile invertebrate abundance on structure surfaces. Fish abundance (4 studies): Three replicated, randomized, controlled studies and one before-and-after study in Australia and the USA found that creating groove habitats and small ridges/ledges on intertidal artificial structures, along with large ledges in one study, did not increase combined fish or juvenile salmon abundances on and around structure surfaces. BEHAVIOUR (3 STUDIES) Use (1 study): One replicated study in Spain reported that grooves and small protrusions created on an intertidal artificial structure were colonized by a number of microalgal species. Fish behaviour change (2 studies): One replicated, randomized, controlled study in Australia found that creating groove habitats and small ledges on intertidal artificial structures increased the time benthic fishes spent interacting with structure surfaces but decreased the number of bites they took and did not change pelagic fish behaviour. One before-and-after study in the USA reported that creating grooves and small protrusions, along with large ledges, increased juvenile salmon feeding activity around the structure.Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3474https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3474Mon, 20 Sep 2021 14:40:44 +0100Collected Evidence: Collected Evidence: Install barriers and crossing structures along roads/railways Sixteen studies evaluated the effects of installing barriers and crossing structures along roads/railways on reptile populations. Five studies were in the USA, three were in each of Spain, Australia and Canada and one was in each of France and South Africa. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (8 STUDIES) Survival (8 studies): Four of seven studies (including one randomized, controlled, before-and-after study and one review) in the USA, Australia, Canada and South Africa found that installing fencing and crossing structures did not reduce road mortalities of reptiles, and in one case the percentage of mortalities may have increased. Two studies found that areas with fencing and crossing structures had fewer road mortalities of turtles and overall reptiles. One study found that reptile road mortalities still occurred in in areas with roadside barrier walls and culverts. One replicated, before-and-after study in Canada found that following installation of tunnels and guide fencing, along with signs for motorists, there were fewer road mortalities of eastern massasauga rattlesnakes. BEHAVIOUR (12 STUDIES) Use (12 studies): Six studies (including two replicated studies and one review) in Spain, France, the USA and Australia found that crossing structures with fencing that were not specifically designed for wildlife were used by lizards, snakes, tortoises, turtles and alligators and ophidians. One study also found that the addition of fencing around crossing structures did not affect the number of reptile crossings. Three studies (including one replicated and one before-and-after study and one review) in the USA and Spain found that wildlife crossing structures with fencing were used by gopher tortoises and 12 snake species, American alligators and lacertid lizards. One study also found that an American alligator did not use the wildlife crossing structure. Two before-and-after studies (including one controlled study) in Canada found mixed effects of installing roadside fencing and culverts on road use by turtles and snakes. One replicated study in Spain found that use of different crossing structures depended on species group. One replicated study in Australia found that reptiles used wildlife underpasses or culverts for only 1% of road crossings. One replicated, before-and-after study in Canada found that following installation of tunnels and guide fencing, along with signs for motorists, fewer eastern massasauga rattlesnakes were found crossing the road. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3507https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3507Tue, 07 Dec 2021 10:03:45 +0000Collected Evidence: Collected Evidence: Protect nests and nesting sites from predation using artificial nest covers: Sea turtles Fifteen studies evaluated the effects of protecting nests and nesting sites from predation using artificial nest covers on sea turtle populations. Six studies were in the USA, two were in each of Turkey and Australia, and one was in each of Greece, Qatar, Indonesia, Cape Verde and Costa Rica. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (15 STUDIES) Reproductive success (15 studies): Eight of 14 studies (including 10 replicated, controlled studies) in the USA, Turkey, Qatar, Indonesia, Cape Verde, Australia and Costa Rica found that sea turtle, loggerhead, hawksbill and artificial sea turtle nests with artificial covers were predated less frequently than nests with no covers. Three studies found that covering sea turtle nests had mixed effects on predation, depending on predator species or year. One study found that loggerhead turtle nests with artificial covers were predated more frequently than nests with no covers. One study found that olive ridley turtle nests with and without artificial covers were all predated. The other study found that predation attempts of green and hawksbill turtle nests with artificial covers were similar compared to nests with no cover, but that predation success was affected by the cover design. Three studies also found that sea turtle and loggerhead turtle nests with artificial covers had higher hatching success than nests with no covers. One study also found that loggerhead turtle nests with artificial covers had similar hatching and emergence success compared to nests with no covers. One replicated, controlled study in Greece found that covering loggerhead turtle nests had mixed effects on hatching success compared to nests with no covers. BEHAVIOUR (0 STUDIES)Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3686https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3686Fri, 10 Dec 2021 16:10:02 +0000Collected Evidence: Collected Evidence: Relocate nests/eggs for artificial incubation: Sea turtles Fifteen studies evaluated the effects of relocating nests/eggs for artificial incubation on sea turtle populations. Three studies were in Suriname and the USA, two were in each of Costa Rica, Malaysia, the Dominican Republic and Mexico and one was in the Cayman Islands. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (12 STUDIES) Reproductive success (12 studies): One of four controlled studies (including three replicated studies) in Suriname, the Dominican Republic, the USA found that kemp’s ridley nests relocated for artificial incubation had higher hatching success than natural nests. One of the studies found that leatherback turtle nests relocated for artificial incubation had lower hatching success than natural nests. One of the studies found that hawksbill turtle nests relocated for artificial incubation had similar hatching success compared to natural nests. The other study found that hatching success of leatherback and green turtle nests relocated for artificially incubation was similar to natural nests above the high tide line and may have been higher than for natural nests washed over by sea swells. This study also found higher embryo mortality in artificially incubated nests compared to natural nests. Three studies (including one randomized, controlled study) in the USA, Mexico and Malaysia found that loggerhead, olive ridley and leatherback turtle nests relocated for artificial incubation had similar hatching success compared to nests relocated to an on-beach hatchery. One study also found that careful handling of eggs during the first five days of incubation did not affect hatching success. Four studies (including one replicated study) in Surinam, Ascension Island and Costa Rica, the Cayman Islands, the USA and Mexico reported that hatching success of green, loggerhead and olive ridley turtle nests relocated for artificial incubation varied from 26% to >90%. One study also reported that hatching success from two trials was 30% and 58% in foam-packed boxes and 26% and 48% in sand-packed boxes. One study also reported that hatching success was 60–89% in 14 of 18 years. One replicated, randomized, controlled study in Costa Rica found that olive ridley turtle eggs artificially incubated in low oxygen conditions had lower hatching success than those in normal oxygen conditions. Condition (2 studies): One replicated, controlled study in Suriname found that leatherback and green turtle nests relocated for artificial incubation had more instances of embryo deformities than natural nests. One randomized, controlled study in Mexico found that relocating olive ridley nests for artificial incubation had mixed effects on hatchling size and movement compared to those relocated to an on-beach hatchery. BEHAVIOUR (0 STUDIES) OTHER (3 STUDIES) Offspring sex ratio (3 studies): Three replicated studies (including two controlled studies) in Suriname and Malaysia found that green turtle and leatherback turtle nests relocated for artificial incubation produced fewer female hatchlings than eggs from natural nests and/or that all sexed hatchlings that were artificially incubated were male. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3795https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3795Wed, 15 Dec 2021 17:02:44 +0000Collected Evidence: Collected Evidence: Relocate nests/eggs for artificial incubation: Lizards Fifteen studies evaluated the effects of relocating nests/eggs for artificial incubation on lizard populations. Five studies were in China, two were in each of India, Spain, the USA and New Zealand and one was in each of Namibia and Taiwan. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (15 STUDIES) Reproductive success (12 studies): One replicated, controlled study in Namibia found that artificially incubated white-throated savanna monitor eggs had higher hatching success than eggs in natural nests. Three of four studies (including one replicated, controlled study) in the USA, Spain, Taiwan and China reported hatching success of 56–96% for artificially incubated eggs from wild lizards. The other study reported that hatching success varied between 11–76%. One replicated, randomized study in India found that hatching success of artificially incubated garden lizard eggs was lower for eggs incubated in cotton wool compared to those incubated in soil or sand. One replicated study in the USA found that artificially incubated eastern collared lizard eggs that had been laid in captivity in artificial nests had higher hatching success than those laid outside of the artificial nests. Two of five replicated studies (including one randomized, controlled study) in India, Spain and China found that hatching success of artificially incubated lizard eggs was lower at higher incubation temperatures. Two studies found that hatching success was similar across all incubation temperatures. The other study found that hatching success was not affected by temperature fluctuations during artificial incubation. Survival (2 studies): One replicated, randomized study in New Zealand found that survival of artificially incubated lizards was higher for individuals incubated at higher temperatures. One replicated, randomized study in Spain found that survival of artificially incubated common chameleon hatchlings was affected by incubation temperature but not moisture levels. Condition (7 studies): Three of five replicated studies (including three randomized studies) in Spain, New Zealand and China found that the size or morphology of artificially incubated lizard hatchlings was similar across all incubation temperatures or was not affected by temperature fluctuations. One study found that growth of artificially incubated common chameleon hatchlings was lower for individuals incubated at higher temperatures. The other study found that lizards from eggs incubated at higher temperatures had higher sprint speeds than those incubated at lower temperatures. One replicated, controlled study in Namibia reported that white-throated savanna monitors from artificially incubated eggs were similar in size to hatchlings from natural nests. One replicated, randomized study in India found that artificially incubating garden lizard eggs in cotton wool, soil or sand resulted in similar sized hatchlings. BEHAVIOUR (0 STUDIES)Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3798https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3798Wed, 15 Dec 2021 18:33:49 +0000Collected Evidence: Collected Evidence: Translocate to re-establish populations in known or believed former range Sixteen studies evaluated the effects of translocating butterflies and moths to re-establish populations within their former range. Seven studies were in the UK, two were reviews across the UK and Ireland, two studies were in Finland and one study was in each of the USA, Australia, the Netherlands, Belgium and the Netherlands and the UK and Sweden. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (16 STUDIES) Abundance (13 studies): Eight studies in the UK, Finland, the USA, Australia, the Netherlands and Belgium and the Netherlands reported that translocated populations of adult butterflies and Fisher’s estuarine moth eggs persisted for 2–12 years and increased in abundance (sometimes in areas where coppicing, selective felling, planting, fencing, host plant translocation, invasive plant removal, sheep grazing, scrub clearance or unspecified habitat restoration were conducted before or after release). Three studies (including two replicated studies) in the UK and Finland reported that some translocated populations of silver-studded blue and clouded Apollo adults, and belted beauty moth eggs and caterpillars, persisted for 1–49 years (in one case where vegetation had been removed before release), increased in abundance and colonized new sites, but other populations died out within 0–7 years. One of two reviews across the UK and Ireland found that 25% of translocated and released captive-bred butterfly populations survived for at least three years, but 38% died out in that time, and only 8% were known to have survived for more than 10 years. The other review reported that translocated populations of large copper adults and/or caterpillars (sometimes to areas planted with great water dock or where bushes had been cleared, or alongside the release of captive-bred individuals) survived for up to 38 years, but ultimately died out or had to be supplemented by further releases. Survival (2 studies): Two site comparison studies (including one replicated, paired study) in the UK found that the survival of large blue caterpillars was higher when translocated into Myrmica sabuleti nests without queen ants present than with queens present, and the survival of translocated large copper caterpillars was higher than the survival of released, captive-bred caterpillars. Condition (1 study): One site comparison in the UK and Sweden found that 19 years after translocation, large blue butterflies in the UK had similar genetic diversity to their Swedish source population. BEHAVIOUR (0 STUDIES)Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3909https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3909Wed, 10 Aug 2022 12:30:26 +0100Collected Evidence: Collected Evidence: Cease mowing on grassland to allow early succession Sixteen studies evaluated the effects on butterflies and moths of ceasing mowing on grassland to allow early succession. Three studies were in Germany, two were in each of the USA, Spain and the Czech Republic, and one was in each of Switzerland, Poland, Slovakia, Hungary, Japan, Russia and Italy. COMMUNITY RESPONSE (8 STUDIES) Community composition (3 studies): Two replicated, site comparison studies in the Czech Republic and Germany found that the community composition of butterflies and moths in grasslands which had been abandoned for >5 years or an unspecified length of time was similar to grasslands managed by mowing or grazing (results not distinguished). One replicated, controlled, before-and-after study in Spain found that after mowing and grazing was abandoned, over 6 years the butterfly community became dominated by generalist species, and species with fewer generations/year. Richness/diversity (7 studies): Five of seven replicated, site comparison studies in Germany, Poland, Japan, the Czech Republic, Russia and Italy found that grasslands which had been abandoned for 3–13 years, 10–20 years or an unspecified length of time, had a similar species richness of butterflies and burnet moths or all moths to grasslands managed by annual or unspecified frequency mowing, or mown within the last three years (in two studies mowing and grazing were not distinguished). One of these studies also found that grasslands abandoned for more than 50 years had lower species richness than grasslands mowed annually to up to 20 years ago, and another found that grasslands abandoned for 6–13 years had a lower species richness of butterflies than grasslands managed by traditional rotational mowing and burning. One of the studies found that meadows not cut all summer had a higher species richness of butterflies than meadows cut 1–3 times/summer. The other study found that grasslands abandoned for at least 5–20 years had a lower species richness of butterflies than grasslands managed by mowing or grazing (results not distinguished). POPULATION RESPONSE (14 STUDIES) Abundance (14 studies): Four replicated studies (including one randomized, paired, controlled study and three site comparison studies) in Germany, Spain, Slovakia and Hungary found that grasslands which had been abandoned for >1–20 years had a lower abundance of all butterflies or some species of butterfly and caterpillars, than grasslands managed by mowing once or twice per year (in two studies mowing and grazing were not distinguished). Four replicated, site comparison studies (including one paired study) in Germany, the Czech Republic, Russia and Italy found that grasslands which had been abandoned for >3 years, were temporarily abandoned, or were uncut all summer, had a higher abundance of all butterflies, 11 species of butterfly, Scotch argus adults and meadow neb moth caterpillars, than grasslands managed by mowing annually, 1–3 times/summer, or within the last three years. Two replicated studies (including one controlled, before-and-after study and one site comparison study) in Spain and Germany found that grasslands which had been abandoned for 1–6 years or an unspecified time period had a higher abundance of woodland and hedgerow butterflies and burnet moths, but a lower abundance of grassland or farmland species, than grasslands managed by mowing and/or grazing (results not distinguished). One of these studies also found that silver-studded blue went extinct in some abandoned meadows. Three replicated, site comparison studies in the USA and Poland found that in grasslands which had been abandoned for many years or 10 to over 50 years before abundance was mixed depending on butterfly species compared to grasslands managed by grazing or mowing. One replicated, site comparison study in Switzerland found that grasslands which had been abandoned for around six years had a similar abundance of heath fritillary adults and caterpillars to grasslands managed by annual mowing, but that grasslands abandoned for >25 years had a lower abundance of adults and no caterpillars. BEHAVIOUR (2 STUDIES) Use (2 studies): One replicated, paired, site comparison study in Germany found that grassland which had been abandoned for >5 years had a similar occurrence of hoary bell moth caterpillars to grassland managed by mowing. One replicated, site comparison study in Spain found that grizzled skipper and painted lady occurred less frequently, but small pearl-bordered fritillary occurred more frequently, in meadows which had been abandoned for at least 1–2 years than in meadows managed by mowing or grazing (results not distinguished). Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3957https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3957Sun, 14 Aug 2022 10:36:48 +0100