Collected Evidence: Collected Evidence: Raise water levels in ditches or grassland Seven studies from Denmark, the Netherlands and the UK (two replicated controlled studies and two before-and-after studies) found that raising water levels in ditches or grassland was associated with increased bird numbers, breeding bird numbers, plant species that favour wet conditions, and invertebrate numbers or biomass in agricultural landscapes. Two replicated studies from the Netherlands and the UK found that raising water levels resulted in a net loss of plant species and did not affect lapwing foraging rate. A review found three studies reporting that re-wetting soils on old arable fields is not an effective method of reducing nutrient levels and restoring species-rich grassland. A replicated study from the UK found that unflooded pastures contained a high biomass of soil macroinvertebrates of importance to breeding wading birds. A controlled, randomized study from the Netherlands found that raising the water level resulted in a more rapid establishment of species typical of wet grassland, than vegetation management. A review of agri-environment schemes from the UK found studies that suggested more expensive agri-environment scheme options for wetland habitats, such as controlling water levels, were more effective at providing good habitat for wading birds than easier-to-implement options. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F121https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F121Tue, 01 Nov 2011 21:14:13 +0000Collected Evidence: Collected Evidence: Manage ditches to benefit wildlife Five out of a total eight studies from the Netherlands and the UK (including one replicated, controlled paired study and three replicated site comparisons) looking at the effects of managing ditches on biodiversity, found that this intervention resulted in increased invertebrate biomass or abundance, plant species richness, emergent plant cover, amphibian diversity and abundance, bird visit rates and higher numbers of some bird species or positive impacts on some birds in plots with ditches managed under agri-environment schemes. One replicated controlled and paired study from the Netherlands found higher plant diversity on ditch banks along unsprayed edges of winter wheat compared to those sprayed with pesticides. Three studies from the Netherlands and the UK (including two replicated site comparisons) found that ditch management had negative or no clear effects on some farmland bird species or plants.  Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F135https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F135Thu, 17 Nov 2011 21:35:00 +0000Collected Evidence: Collected Evidence: Create scrapes and pools Three studies from Sweden and the UK (including two site comparisons one of which was replicated) found that the creation of scrapes and pools provided habitat for a range of plant, invertebrate or bird species and resulted in increased aquatic macroinvertebrate diversity. One of these studies found constructed pools supported locally or nationally scarce species of plant and water beetle. A study in Sweden found that a combination of large surface area, high shoreline complexity and shallow depth resulted in increased bird, bottom-dwelling invertebrate and aquatic plant diversity. However there were fewer fish species than in natural wetlands. Two replicated studies from Ireland and the UK (one controlled paired study and a site comparison) found that bird visit rates were higher but invertebrate numbers varied in ditch-fed paired ponds compared with dry controls and total macroinvertebrate and beetle richness did not differ between artificial and natural ponds, although communities did differ.  Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F153https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F153Sat, 14 Jan 2012 15:30:46 +0000Collected Evidence: Collected Evidence: Restore or create inland wetlands Of eleven studies captured, 11, from the mainland USA, Guam, Canada and Hawaii, found that birds used artificially restored or created wetlands. Two found that rates of use and species richness were similar or higher than on natural wetlands. One found that use rates were higher than on unrestored wetlands. Three studies from the USA and Puerto Rico found that restored wetlands held lower densities and fewer species of birds than natural wetlands. A replicated study from the USA found that least bittern productivity was similar in restored and natural wetlands. Two replicated studies examined wetland characteristics: one from the USA found that semi-permanent restored wetlands were used more than temporary or seasonal ones. A study from Hawaii found that larger restored wetlands were used more than smaller sites.  Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F366https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F366Mon, 06 Aug 2012 13:34:38 +0100Collected Evidence: Collected Evidence: Physically protect nests with individual exclosures/barriers or provide shelters for chicks of waders Three of 13 studies from the USA found higher productivity from nests protected by individual barriers than unprotected nests. Two studies from the USA and Sweden found no higher productivity from protected nests. Eight studies from the USA and Europe found higher hatching rates, or survival, or low predation of nests protected by individual barriers, although two of these found that higher hatching rates did not result in higher productivity. Two small studies from North America found no differences in predation or survival rates between protected and unprotected nests. A meta-analysis from the USA found that there were differences in the effectiveness of different exclosure designs.  Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F398https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F398Wed, 15 Aug 2012 14:32:17 +0100Collected Evidence: Collected Evidence: Provide artificial nesting sites for raptors Nine studies from North America and Spain found that raptors used artificial nesting platforms, although one describes low levels of use and another describes use increasing over time. Two studies from the USA describe increases in populations or population densities of raptors following the installation of artificial nesting platforms. Three studies describe successful use of platforms, whilst three describe lower productivity or failed nesting attempts, although these studies only describe a single nesting attempt each.  Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F488https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F488Mon, 03 Sep 2012 13:23:17 +0100Collected Evidence: Collected Evidence: Foster eggs or chicks of raptors with wild conspecifics Ten out of 11 studies from across the world found that fostering raptor chicks to wild conspecifics had high success rates. A single study from the USA found that only one of six eggs fostered to wild bald eagle Haliaeetus leucocephalus nests were hatched and raised. The authors suggest that the other eggs may have been infertile. A replicated study from Spain found that Spanish imperial eagle Aquila adalberti chicks were no more likely to survive to fledging if they were transferred to foster nests from three chick broods (at high risk from siblicide), compared to chicks left in three-chick broods. A replicated study from Spain found that young (15–20 years old) Montagu's harrier Circus pygargus chicks were successfully adopted, but three older (27–29 day old) chicks were rejected.  Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F510https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F510Thu, 06 Sep 2012 14:42:31 +0100Collected Evidence: Collected Evidence: Add lime to water bodies to reduce acidification One before-and-after study in the UK found that adding limestone to ponds resulted in establishment of one of three translocated populations of natterjack toads. One replicated, site comparison study in the UK found that species-specific habitat management that included adding limestone to ponds increased natterjack toad populations. One before-and-after study in the UK found that adding limestone to ponds temporarily increased breeding by natterjack toads. Three before-and-after studies (including one controlled, replicated study) in the Netherlands and UK found that adding limestone increased larval and/or egg survival of moor frogs and common frogs and resulted in metamorphosis of natterjack toads at two of three sites. Two before-and-after studies (including one controlled study) in the UK found that adding limestone to ponds resulted in high tadpole mortality and pond abandonment by natterjack toads and higher numbers of abnormal common frog eggs.  Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F748https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F748Thu, 18 Jul 2013 15:41:50 +0100Collected Evidence: Collected Evidence: Create ponds for amphibians Twenty-eight studies investigated the colonization of created ponds by amphibians in general (rather than by targeted species, which are discussed below). All of the studies found that amphibians used some or all created ponds. Nine site comparison studies (including seven replicated studies) in Australia, Canada, Spain, the UK and USA compared amphibian numbers in created and natural ponds. Five found that numbers of species or breeding species were similar or higher in created ponds, and numbers of ponds colonized were similar. Four found that species composition differed, and comparisons between abundance of individual species, juvenile productivity and size at metamorphosis differed depending on species. One found that numbers of species were similar or lower depending on the permanence of created water bodies. One found that populations in created ponds were less stable. One review and two replicated, before-and-after studies in Denmark and the USA found that amphibians established stable populations in 50–100% of created ponds. Six replicated studies (including one randomized study) in France, the Netherlands, UK and USA found that amphibians used 64–100% and reproduced in 64–68% of created ponds, or used 8–100% and reproduced in 2–62% depending on species. One review and 15 studies (including 12 replicated studies, one of which was randomized) in Europe and the USA found that created ponds were used or colonized by up to 15 naturally colonizing species, up to 10 species that reproduced, as well as by captive-bred amphibians. Five replicated studies (including three site comparison studies) in Denmark, Estonia, France, Italy and the USA found that pond creation, and restoration in three cases, maintained and increased amphibian populations or increased numbers of species. Seven studies (including one review) in Austria, Denmark, Poland, the Netherlands and USA found that use or colonization of or reproductive success in created ponds was affected by pond age, permanence, vegetation cover, surrounding landscape, distance to existing ponds and presence of fish.  Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F869https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F869Wed, 11 Sep 2013 09:16:41 +0100Collected Evidence: Collected Evidence: Create wetland Fifteen studies investigated the effectiveness of creating wetlands for amphibians. Five site comparison studies (including four replicated studies) in the USA compared created to natural wetlands and found that created wetlands had similar numbers of amphibian species, amphibian abundance or communities depending on depth as natural wetlands. Two of the studies found that created wetlands had fewer amphibian species or lower abundance and different communities compared to natural wetlands. One site comparison study in the USA found that created wetlands had similar numbers of species to adjacent forest. One global review and two site comparison studies (including one replicated study) in the USA combined created and restored wetlands and compared them to natural wetlands and found that numbers of amphibian species and abundance was higher or similar, or higher in 54% of studies and similar in 35% of studies reviewed compared to natural wetlands. Three site comparison studies (including one replicated study) in the USA found that certain amphibian species were only found in created or natural wetlands. One before-and-after study in Australia found that captive-bred green and golden bell frog tadpoles released into a created wetland did not establish a self-sustaining population. Five studies (including two replicated studies) in Kenya and the USA that investigated colonization of created wetlands found that four to 15 amphibian species used or colonized the wetlands. One global review and three studies (including two replicated studies) in the USA found that numbers of amphibian species and amphibian abundance in created wetlands were affected by wetland design, vegetation, water levels, surrounding habitat, fish presence and distance to source wetlands.  Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F880https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F880Fri, 13 Sep 2013 11:16:59 +0100Collected Evidence: Collected Evidence: Create artificial water sources Five studies evaluated the effects of creating artificial water sources for bats on bat populations. One study was in each of the USA, Germany, South Africa, Israel and Mexico. COMMUNITY RESPONSE (1 STUDY) Richness/diversity (1 study): One replicated, paired sites study in South Africa found a similar number of bat species over farm ponds and in grassland/crops, trees, vineyards or orchards. POPULATION RESPONSE (5 STUDIES) Abundance (5 studies): Five replicated studies (including four site comparisons and one paired sites study) in Israel, the USA, Germany, South Africa and Mexico found that bat activity (relative abundance) was similar or higher over reservoirs and waste water treatment pools, heliponds and drainage ditches, retention ponds and farm/cattle ponds compared to over natural wetlands, nearby vineyards, surrounding forest or grassland/crops, trees and orchards. BEHAVIOUR (0 STUDIES)Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F959https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F959Fri, 20 Dec 2013 10:14:31 +0000Collected Evidence: Collected Evidence: Procambarus crayfish control: Create barriers A before-and-after study conducted between 2007 and 2010 in Spain found that the use of concrete dams across a stream, specifically designed with features to prevent red swamp crayfish from crawling over them, were effective at containing spread of the population upstream.  Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1037https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1037Fri, 03 Jul 2015 15:18:00 +0100Collected Evidence: Collected Evidence: Asian clams: Reduce oxygen in the water A controlled laboratory study conducted in the USA found that Asian clams were resistant to extreme very low levels of oxygen, irrespective of water temperature or length of immersion in the test conditions.  Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1113https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1113Tue, 13 Oct 2015 14:45:11 +0100Collected Evidence: Collected Evidence: Other biodiversity: Restore habitat along watercoursesAmphibians (1 study): One replicated site comparison from the USA found similar numbers of amphibian species in restored and remnant sites. Birds (8 studies): Two replicated site comparisons from Spain and the USA found similar numbers of bird species in restored and remnant sites. Two replicated site comparisons from the USA found fewer bird species in restored riparian sites, compared to remnant sites. One replicated site comparison from Spain found similar numbers of birds and bird species in restored contaminated sites and uncontaminated sites. One replicated site comparison from the USA found that an endangered bird nested in restored sites, and had similar nesting success in restored and remnant sites. One replicated site comparison from the USA found that bird populations increased with the area of restored habitat in the landscape, in some comparisons. One replicated site comparison from the USA found similar levels of nest parasitism in restored and remnant sites. Fish (1 study): One before-and-after site comparison from the USA found differences in fish communities, before and after changing river flow. Invertebrates (3 studies): One replicated site comparison from the USA found fewer native ants, but similar numbers of invasive ants, in restored sites, compared to remnant sites. One before-and-after site comparison from the USA found similar numbers of freshwater invertebrates in restored and reference sites, after restoration. One replicated, before-and-after study from the USA found more invertebrates and invertebrate species in plots with added gravel, compared to plots without added gravel, in some comparisons. One replicated before-and-after study from France found relatively more alien species after restoring river flow. Mammals (2 studies): Two replicated site comparisons from the USA found similar numbers of mammal species in restored and remnant sites. Plants (11 studies) Abundance (6 studies): Four replicated site comparisons from Spain and the USA found lower plant cover in restored sites, compared to remnant sites. One of these studies also found higher cover of exotic plants, but another one did not. One replicated, paired site comparison from the USA found similar numbers of flowers in restored and remnant sites. One replicated site comparison from the USA found more seeds, but fewer native seed, in orchards next to restored riparian habitats, compared to orchards next to remnant habitats. One replicated site comparison from the USA found similar exotic plant cover in remnant and restored forests. Diversity (6 studies): Two replicated studies from the USA found fewer native plant species in restored forests, compared to remnant forests. One of these studies also found more exotic species, but another one did not. One replicated site comparison from the USA found more plant species in restored sites, compared to remnant sites. One replicated, paired site comparison from the USA found similar numbers of flower species in restored and remnant sites. One replicated site comparison from the USA found fewer seed species and native seed species in orchards next to restored riparian habitats, compared to remnant riparian habitats. One controlled study from the USA found different plant communities in restored and unrestored habitats. Survival (2 studies): One replicated study from the USA found that about one-third of planted willows survived for one year. One site comparison from the USA found that some species survived after planting, as part of riparian restoration, but others did not. Habitat suitability (1 study): One replicated site comparison from the USA found that vegetation at one of five sites met the criteria for Bell’s Vireo nesting habitat. Size (1 study): One replicated site comparison from the USA found smaller elderberry plants in restored sites. Reptiles (1 study): One replicated site comparison from the USA found similar numbers of reptile species in remnant and restored sites. Implementation options (7 studies) Plants (3 studies): One study from the USA found more tree, shrub, vine, and perennial species, higher canopy cover, and higher native tree cover, in older restored plots, compared to younger restored plots, but this study also found fewer annual plant species, lower vegetation cover, lower annual forb cover, and lower grass cover. One study from the USA found an increase in native species and overstorey cover in restored sites, over time, but it found similar numbers of species and overstorey cover in sites planted at different densities. One study from the USA found that willow cuttings planted on the stream bottom had a higher survival rate than those planted on the streambank or terrace. Birds (3 studies): Three studies from the USA found more birds or bird species in older restored plots, compared to younger restored plots. One of these studies also found that the populations of some bird species increased with tree-planting density. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1416https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1416Fri, 19 May 2017 09:54:10 +0100Collected Evidence: Collected Evidence: Create/preserve primate habitat on islands before dam construction We found no evidence for the effects of creating/preserving primate habitat on islands before dam construction on primate populations. 'No evidence' for an action means we have not yet found any studies that directly and quantitatively tested this action during our systematic journal and report searches. Therefore we have been unable to assess whether or not the action is effective or has any harmful impacts. Please get in touch if you know of such a study for this action.Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1455https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1455Tue, 17 Oct 2017 13:04:15 +0100Collected Evidence: Collected Evidence: Conduct veterinary screens of animals before reintroducing/translocating them One before-and-after study in Brazil found that most reintroduced golden lion tamarins did not survive over seven years, despite undergoing pre-release veterinary screens, alongside other interventions. One study in Brazil found that most reintroduced black lion tamarins that underwent veterinary screens, alongside other interventions, survived over four months. One before-and-after study in Malaysia found that 90% of reintroduced Müller's Bornean gibbons did not survive despite undergoing veterinary screens, alongside other interventions. One controlled study in Indonesia found that reintroduced Bornean agile gibbons that underwent veterinary screens, alongside other interventions, behaved similarly to wild gibbons. Two studies, including one controlled, in Malaysia and Indonesia found that most translocated orangutans that underwent veterinary screens, along with other interventions, survived translocation and the first three months post-translocation. Four studies, including three before-and-after studies, in Liberia, the Republilc of Congo and Guinea found that most reintroduced chimpanzees that underwent veterinary screens, alongside other interventions, survived over 1-5 years. One before and after study in Uganda found that a reintroduced chimpanzee repeatedly returned to human settlements after undergoing pre-release veterinary screens, alongside other interventions. Five studies, including four before-and-after studies, in Belize, French Guiana, Madagascar, Congo and Gabon found that most reintroduced or translocated primates that underwent veterinary screens, alongside other interventions, survived at least four months or increased in population size. Five studies, including four before-and-after studies, in French Guiana, Madagascar, South Africa and Vietnam found that most reintroduced or translocated primates were assumed to have died post-release despite undergoing pre-release veterinary screens, alongside other interventions. One controlled study in Kenya found that a population of translocated olive baboons were still surviving 16 years after translocation when veterinary screens were applied alongside other interventions. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1553https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1553Thu, 19 Oct 2017 20:15:52 +0100Collected Evidence: Collected Evidence: Detect & report dead primates and clinically determine their cause of death to avoid disease transmission One before-and-after study in the Republic of Congo found that most reintroduced chimpanzees survived over five years when dead chimpanzees were examined to determine their cause of death, alongside other interventions. One before-and-after study in French Guiana found that most translocated white-faced sakis survived over four months when dead sakis were examined to determine their cause of death, alongside other interventions. One before-and-after study in Madagascar found that most black-and-white ruffed lemurs did not survive over five years despite the fact that dead lemurs were clinically examined to determine their cause of death, alongside other interventions. One controlled, before-and-after study in Rwanda, Uganda and the Democratic Republic of Congo found that the population size of mountain gorillas where dead animals were examined to determine the cause of death, alongside other interventions, increased by 168% over 41 years. One before-and-after, site comparison study in Congo and Gabon found that most western lowland gorillas survived over four years when dead individuals were examined to determine their cause of death, alongside other interventions. Two studies, including a before-and-after, in Vietnam and Indonesia found that most reintroduced pygmy slow lorises either died or disappeared despite the fact that dead lorises were examined to determine their cause of death, alongside other interventions. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1556https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1556Thu, 19 Oct 2017 20:58:29 +0100Collected Evidence: Collected Evidence: Translocate (capture & release) wild primates from development sites to natural habitat elsewhere One study in Malaysia found that the majority of orangutans survived following translocation from a development site to natural habitat, alongside other interventions. Three before-and-after studies in Tanzania, French Guiana, and Madagascar found that a majority of primates survived for 5-30 months following translocation from a development site to natural habitat, alongside other interventions. One study in French Guiana found that a minority of primates survived for at least 18 months. One before-and-after study in India found that rhesus monkeys remained at the sites where they were released following translocation from a development site to natural habitat, alongside other interventions. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1558https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1558Fri, 20 Oct 2017 09:44:55 +0100Collected Evidence: Collected Evidence: Allow primates to adapt to local habitat conditions for some time before introduction to the wild Two studies in Brazil and Thailand found that reintroduced primate populations were smaller after 12-17 months and one study in Belize found primate populations increased five years after allowing individuals to adapt to local habitat conditions before introduction into the wild, alongside other interventions. One study found that a reintroduced population of black howler monkeys had a birth rate of 20% after they were allowed to adapt to local habitat conditions before introduction into the wild, along with other interventions. Seven studies in Brazil, Madagascar, Malaysia, French Guiana, South Africa found that a minority of primates survived for at least 15 weeks to 12 years after allowing them to adapt to local habitat conditions before introduction into the wild, along with other interventions. Four studies in Belize, Brazil, Gabon, South Africa found that the majority of primates survived for at least four to 12 months. One study in Vietnam found that half of reintroduced pygmy slow lorises survived for at least two months. Two before-and-after studies in Gabon and the Republic of Congo found that a majority of western lowland gorillas survived for nine months to four years after allowing them to adapt to local habitat conditions before introduction into the wild, along with other interventions. Three studies in Liberia and the Congo found that a majority of chimpanzees survived for at least three to five years after allowing them to adapt to local habitat conditions before introduction into the wild, along with other interventions. One before-and-after study in Uganda found that a chimpanzee repeatedly returned to human settlements after allowing it to adapt to local habitat conditions before introduction into the wild, along with other interventions. A study in Indonesia found that Sumatran orangutans that were allowed to adapt to local habitat conditions before introduction performed less well than individuals that were directly released into the forest, alongside other interventions. One controlled study in Indonesia found that after being allowed to adapt to local habitat conditions a pair of introduced Bornean agile gibbons had a similar diet to wild gibbons. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1564https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1564Fri, 20 Oct 2017 10:08:36 +0100Collected Evidence: Collected Evidence: Reintroduce primates in groups Two studies in Brazil and Thailand found that populations of introduced primates declined after reintroduction in groups, alongside other interventions, while one study in Belize recorded an increase in populations. Two studies in Madagascar and India found that primate populations persisted 4-55 years after reintroduction in groups, alongside other interventions. Seven studies in Brazil, French Guiana, Madagascar, and South Africa found that a minority of primates survived for at least 15 weeks to seven years after reintroduction in groups, alongside other interventions. Seven studies in Belize, Brazil, French Guiana, Madagascar, and South Africa found that a majority of primates survived after between two and thirty months. One study in Madagascar found that introduced black-and-white ruffed lemurs Varecia variegata had similar diets to individuals in a wild population after reintroduction in groups, alongside other interventions. One study in The Gambia found that a population of introduced chimpanzees increased 25 years after reintroduction in groups, alongside other interventions. Four studies in Guinea, Liberia and the Republic of Congo found that the majority of chimpanzees survived for at least two to five years, after reintroduction in groups, alongside other interventions. Two before-and-after studies in Gabon and the Republic of Congo found that the majority of western gorillas survived for at least nine months to four years, after reintroduction in groups, alongside other interventions. One controlled study in Indonesia found that all Sumatran orangutans survived for at least three months after reintroduction in groups, alongside other interventions. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1567https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1567Fri, 20 Oct 2017 10:46:09 +0100Collected Evidence: Collected Evidence: Cut/remove/thin forest plantations and rewet peat Eleven studies evaluated the effects of cutting/removing trees and rewetting peat (in combination): six in fens, two in bogs, and three in both fens and bogs. In four of the studies, the peatlands naturally contained some trees. Three studies were based on one experimental set-up, and two studies were based on another. Plant community composition (5 studies): Of three replicated studies in fens, two in Finland found that removing trees/rewetting had no effect on the overall plant community composition whilst one in Sweden reported only a small effect. Two site comparison studies in bogs and fens in Finland found that removing trees/rewetting changed the overall plant community composition. It became less like sites that remained drained and forested. Characteristic plants (2 studies): Two before-and-after studies (one site comparison, one controlled) in bogs and fens in Finland and Sweden reported that removing trees/rewetting increased the abundance of wetland-characteristic plants. Moss cover (6 studies): Of five studies that examined the effect of removing trees/rewetting on Sphagnum moss, two replicated, paired studies in bogs and fens in Sweden and Finland found that the intervention increased Sphagnum cover. One replicated, before-and-after, site comparison study in forested fens in Finland found no effect. Two before-and-after studies in a bog in Finland and a fen in Sweden found mixed effects depending on site or species. Additionally, three studies (two replicated and paired) in peatlands in the UK and Finland found that removing trees/rewetting reduced cover of non-Sphagnum or forest-characteristic mosses. However, one replicated, before-and-after, site comparison study in forested fens in Finland found no effect of thinning trees/rewetting on forest mosses. Herb cover (7 studies): Seven studies (including two replicated, paired, controlled) in bogs and fens in the UK, Finland and Sweden reported that removing trees/rewetting increased cover of at least one group of herbs, including cottongrasses and sedges. However, one of these studies reported loss of cottongrass from a fen where it was rare before intervention, along with reduced purple moor grass cover. Vegetation structure (4 studies): One replicated site comparison study in a bog in the UK found that removing trees/rewetting increased ground vegetation height. One replicated, paired, controlled study in a fen in Sweden reported that removing trees/rewetting had no effect on canopy height after eight years. Two replicated, paired, site comparison studies in bogs and fens in Finland found that thinning trees/rewetting reduced the number of tall trees present for 1–3 years (although not to the level of natural peatlands). Overall plant richness/diversity (4 studies): Two replicated, paired, controlled studies in rich fens in Sweden reported that removing trees/rewetting increased plant species richness. However, two replicated studies in fens in Finland found that removing trees/rewetting had no effect on total plant species richness or diversity. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1732https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1732Mon, 27 Nov 2017 21:16:46 +0000Collected Evidence: Collected Evidence: Maintain/restore water flow across service corridors One study evaluated the effects on peatland vegetation of restoring water flow across service corridors. The study was in a fen. Characteristic plants (1 study): One before-and-after study in a fen in the USA found that following restoration of water inflow across a road (along with general rewetting), cover of wet peatland sedges increased whilst cover of grasses preferring drier conditions decreased. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1741https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1741Mon, 27 Nov 2017 21:25:06 +0000Collected Evidence: Collected Evidence: Rewet peatland (raise water table) Thirty-six studies evaluated the effects of rewetting (without planting) on peatland vegetation. Fifteen studies were in bogs (two being restored as fens). Fifteen studies were in fens or fen meadows (two were naturally forested). Six studies were in general or unspecified peatlands. Some studies were based on the same experimental set-up or sites as each other: two studies in Germany, three studies in Sweden, two studies in west Finland and two studies in south Finland. Plant community composition (13 studies): Six before-and-after studies (four also replicated) in peatlands in Finland, Hungary, Sweden, Poland and Germany reported changes in the overall plant community composition following rewetting. Typically, drier grassland communities were replaced by more wetland- or peatland-characteristic communities. One replicated, paired, controlled study in a bog in the Czech Republic found that rewetted plots developed a different plant community to drained plots. Three site comparison studies in Finland and Canada reported that rewetted peatlands contained a different plant community to natural peatlands. Three replicated studies in peatlands in the UK and fens in Germany reported that rewetting typically had no effect, or insignificant effects, on the plant community. Characteristic plants (11 studies): Five studies (including one replicated site comparison) in peatlands in Canada, the UK, China and Poland reported that rewetting (sometimes along with other interventions) increased the abundance of wetland- or peatland-characteristic plants. Two replicated site comparison studies in fens or fen meadows in central Europe found that rewetting reduced the number of fen-characteristic plant species. Two studies (one replicated, paired, controlled, before-and-after) in fens in Sweden reported that rewetting had no effect on cover of fen-characteristic plants. Two before-and-after studies in fens in the USA and New Zealand reported that upland plant cover decreased following rewetting.  Moss cover (19 studies): Twelve studies (five replicated, two also paired and controlled) in the UK, Ireland, Germany, Sweden, Latvia, Canada and Spain reported that rewetting bogs, fens or other peatlands (sometimes along with other interventions) increased Sphagnum moss cover or abundance. Three of these studies reported mixed responses by species. Two additional replicated studies, in bogs in Latvia and forested fens in Finland, reported that rewetting had no effect on Sphagnum cover. Five studies (one paired, controlled, before-and-after) in Finland, Sweden and Canada reported that rewetting bogs or fens had no effect on cover of non-Sphagnum mosses (or mosses/lichens). However, two controlled studies in bogs in Ireland and the UK reported that rewetting reduced cover of non-Sphagnum mosses or bryophytes. One site comparison study in Finland reported that a rewetted peatland had similar moss cover (Sphagnum and total) to a natural peatland, but another site comparison study in Canada reported that a rewetted bog had lower moss cover (Sphagnum and other) than nearby target peatlands. Herb cover (25 studies): Twenty-one studies (including four replicated, paired, controlled) reported that rewetting (sometimes along with other interventions) increased cover of at least one group of herbs. These studies were in bogs, fens or other peatlands in the UK, Finland, Ireland, the Czech Republic, the USA, the Netherlands, Sweden, Germany, China, Latvia, Poland, Canada and Spain. Specifically, rewetting increased other/total sedge cover in 13 of 15 studies, increased cottongrass cover in eight of nine studies, and increased reed/rush cover in five of seven studies. Three of four before-and-after studies in peatlands in the UK and Sweden reported that rewetting reduced purple moor grass cover; the other study reported no effect. One replicated site comparison study in forested fens in Finland reported that rewetting had no effect on total herb cover. Two site comparison studies in Europe reported greater herb cover in rewetted than natural peatlands (overall and sedges/rushes, but not forbs). Tree/shrub cover (13 studies): Ten studies (including two paired and controlled) in peatlands in Finland, the UK, Germany, Latvia and Canada reported that rewetting typically reduced (seven studies) or had no effect (six studies) on tree and/or shrub cover. Two before-and-after studies in fens in Sweden and Germany reported that rewetting increased tree/shrub cover. One before-and-after study in a bog in the UK reported mixed effects of rewetting on different tree/shrub species. Overall vegetation cover (4 studies): Of four before-and-after studies (three also controlled) that examined the effect of rewetting on overall vegetation cover, two in bogs in Ireland and Sweden reported that rewetting increased it. One study in a fen in New Zealand reported that rewetting reduced vegetation cover. One study in a peatland in Finland reported no effect. Overall plant richness/diversity (14 studies): Six studies (including one replicated, paired, controlled, before-and-after) in Sweden, Germany and the UK reported that rewetting increased total plant species richness or diversity in bogs, fens or other peatlands. However, five studies found no effect: in bogs in the Czech Republic and Latvia, fens in Sweden and Germany, and forested fens in Finland. One study in fen meadows in the Netherlands found scale-dependent effects. One paired, controlled, before-and-after study in a peatland in Finland reported that rewetting reduced plant diversity. Of four studies that compared rewetted and natural peatlands, two in Finland and Germany reported lower species richness in rewetted peatlands, one in Sweden found higher species richness in rewetted fens, and one in Europe found similar richness in rewetted and natural fens. Growth (1 study): One replicated site comparison study in forested fens in Finland found that rewetting increased Sphagnum moss growth to natural levels. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1756https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1756Mon, 27 Nov 2017 21:33:59 +0000Collected Evidence: Collected Evidence: Fill/block ditches to create conditions suitable for peatland plants (without planting) Three studies evaluated the effects of filling or blocking ditches (without planting) on peatland vegetation within them. Two studies were in bogs and one was in a fen. Vegetation cover (3 studies): Two studies in a bog in the UK and a fen in the USA reported that blocked or filled ditches were colonized by herbs and bryophytes within 2–3 years. In the USA, vegetation cover (total, bryophyte, forb, grass and sedge) was restored to natural, undisturbed levels. One replicated study in bogs in the UK reported that plants had not colonized blocked gullies after six months. Overall plant richness/diversity (1 study): One site comparison study in a fen in the USA found that a filled ditch contained more plant species than adjacent undisturbed fen, after two years. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1805https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1805Tue, 28 Nov 2017 08:29:55 +0000Collected Evidence: Collected Evidence: Directly plant peatland mosses Seven studies evaluated the effects on peatland vegetation of planting mosses. Six studies were in bogs and one was in a fen. Survival (1 study): One study in Lithuania reported that of 50 Sphagnum-dominated sods planted into a rewetted bog, 47 survived for one year. Growth (2 studies): Two before-and-after studies in a fen in the Netherlands and bog pools in the UK reported that mosses grew after planting. Moss cover (5 studies): Five before-and-after studies in a fen in the Netherlands and bogs in Germany, Ireland, Estonia and Australia reported that after planting mosses, the area covered by moss increased in at least some cases. The study in the Netherlands reported spread of planted moss beyond the introduction site. The study in Australia was also controlled and reported that planted plots developed greater Sphagnum moss cover than unplanted plots. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1818https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1818Tue, 28 Nov 2017 08:44:34 +0000Collected Evidence: Collected Evidence: Create or maintain small dams to provide foraging and drinking habitat for bats One study evaluated the effects of maintaining small dams as foraging and drinking habitat for bats on bat populations. The study was in Portugal. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (1 STUDY) Abundance (1 study): One replicated, site comparison study in Portugal found that reservoirs created using small dams had greater activity (relative abundance) of four bat species than the streams feeding into them. BEHAVIOUR (0 STUDIES)Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1997https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1997Wed, 05 Dec 2018 14:43:11 +0000Collected Evidence: Collected Evidence: Relocate bat colonies roosting inside dams One study evaluated the effects of relocating bat colonies inside dams on bat populations. The study was in Argentina. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (1 STUDY) Abundance (1 study): One study in Argentina found that almost two-thirds of a large colony of Brazilian free-tailed bats relocated to a different dam compartment five months after being displaced from six compartments where the colony originally roosted. BEHAVIOUR (0 STUDIES)  Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1998https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F1998Wed, 05 Dec 2018 14:44:59 +0000Collected Evidence: Collected Evidence: Reduce intensity of grazing by domestic livestock Thirteen studies evaluated the effects on mammals of reducing the intensity of grazing by domestic livestock. Six studies were in the USA, six were in Europe and one was in China. COMMUNITY RESPONSE (3 STUDIES) Richness/diversity (3 studies): Two of three site comparison or controlled studies, in the USA and Norway, found that reduced livestock grazing intensity was associated with increased species richness of small mammals whilst one study did not find an increase in species richness. POPULATION RESPONSE (13 STUDIES) Abundance (13 studies): Six of nine site comparison or controlled studies (including seven replicated studies), in the USA, Denmark, the UK, China, Netherlands and Norway, found that reductions in livestock grazing intensity were associated with increases in abundances (or proxies of abundances) of small mammals, whilst two studies showed no significant impact of reducing grazing intensity and one study showed mixed results for different species. Two replicated studies (including one controlled and one site comparison study), in the UK and in a range of European countries, found that reducing grazing intensity did not increase numbers of Irish hares or European hares. A controlled, before-and-after study, in the USA found that exclusion of cattle grazing was associated with higher numbers of elk and mule deer. A replicated, site comparison study in the USA found that an absence of cattle grazing was associated with higher numbers of North American beavers. BEHAVIOUR (0 STUDIES)Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2408https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2408Fri, 29 May 2020 08:14:23 +0100Collected Evidence: Collected Evidence: Airborne translocation of mammals using parachutes One study evaluated the effects of airborne translocation of mammals using parachutes. This study was in the USA. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (1 STUDY) Survival (1 study): A study in the USA found that at least some North American beavers translocated using parachutes established territories and survived over one year after release. BEHAVIOUR (0 STUDIES)Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2466https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2466Wed, 03 Jun 2020 09:31:50 +0100Collected Evidence: Collected Evidence: Provide artificial waterholes in dry season Three studies evaluated the effects on mammals of providing artificial waterholes in the dry season. One study was in South Africa, one was in Tanzania and one was in Jordan. COMMUNITY RESPONSE (1 STUDY) Richness/diversity (1 study): A site comparison study in Tanzania found that artificial waterholes were used by a similar number of large mammal species as was a natural waterhole. POPULATION RESPONSE (0 STUDIES) BEHAVIOUR (2 STUDIES) Use (2 studies): A study in South Africa found that areas around artificial waterholes were used more by eight out of 13 mammalian herbivore species than was the wider landscape. A study in Jordan found that artificial waterholes were used by striped hyenas. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2484https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2484Thu, 04 Jun 2020 12:15:59 +0100Collected Evidence: Collected Evidence: Provide dams/water holes during drought We found no studies that evaluated the effects on mammals of providing dams or water holes during drought. ‘We found no studies’ means that we have not yet found any studies that have directly evaluated this intervention during our systematic journal and report searches. Therefore, we have no evidence to indicate whether or not the intervention has any desirable or harmful effects.Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2554https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2554Tue, 09 Jun 2020 10:44:26 +0100Collected Evidence: Collected Evidence: Restore or create shrubland Three studies evaluated the effects on mammals of restoring or creating shrubland. Two studies were in the USA and one was in Mexico. COMMUNITY RESPONSE (2 STUDIES) Richness/diversity (2 studies): Two site comparison studies, in the USA and Mexico, found that following desert scrub or shrubland restoration, mammal species richness was similar to that in undisturbed areas. POPULATION RESPONSE (1 STUDY) Abundance (1 study): A site comparison study in the USA found that restored desert scrub hosted similar small mammal abundance compared to undisturbed desert scrub. BEHAVIOUR (1 STUDY) Use (1 study): A replicated, site comparison study in the USA found that restoring shrubland following tree clearance did not increase usage of areas by mule deer compared to tree clearance alone. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2569https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2569Tue, 09 Jun 2020 16:19:23 +0100Collected Evidence: Collected Evidence: Provide mammals with escape routes from canals Five studies evaluated the effects on mammals of providing mammals with escape routes from canals. Two studies were in Germany and one each was in the USA, the Netherlands and Argentina. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (2 STUDIES) Survival (2 studies): One of two studies (one before-and-after), in Germany and the USA, found that ramps and ladders reduced mule deer drownings whilst the other study found that ramps and shallow-water inlets did not reduce mammal drownings. BEHAVIOUR (3 STUDIES) Use (3 studies): Three studies (one replicated) in Germany, the Netherlands and Argentina, found that ramps and other access or escape routes out of water were used by a range of medium-sized and large mammals species. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2638https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2638Fri, 12 Jun 2020 13:06:54 +0100Collected Evidence: Collected Evidence: Install bypass channels in dams We found no studies that evaluated the effects of installing bypass channels in dams on marine and freshwater mammal populations. ‘We found no studies’ means that we have not yet found any studies that have directly evaluated this action during our systematic journal and report searches. Therefore we have been unable to assess whether or not the action is effective or has any harmful impacts. Please get in touch if you know of such a study for this action.Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2848https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2848Fri, 05 Feb 2021 16:37:32 +0000Collected Evidence: Collected Evidence: Backfill canals or trenches: freshwater marshes Three studies evaluated the effects, on vegetation, of backfilling canals or trenches in freshwater marshes. All three studies were in the USA. There was overlap in the canals used in two of the studies. VEGETATION COMMUNITY Overall extent (3 studies): Three replicated studies in freshwater marshes in the USA reported coverage of emergent marsh vegetation between 6 months and 25 years after backfilling. All three studies reported that coverage was greater on former spoil areas alongside canals than within the partly filled canal channels. Relative abundance (1 study): One replicated, paired, site comparison study in a freshwater marsh in the USA reported that in levelled former spoil areas alongside backfilled canals, the relative abundance of some key plant species differed from natural marshland. Vegetation was surveyed three years after backfilling. VEGETATION ABUNDANCE   VEGETATION STRUCTURECollected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2987https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2987Thu, 25 Mar 2021 21:10:33 +0000Collected Evidence: Collected Evidence: Backfill canals or trenches: brackish/salt marshes Four studies evaluated the effects, on vegetation, of backfilling canals or trenches in brackish/salt marshes. All four studies were in the USA. There was overlap in the canals used in three of the studies. All studies included some freshwater areas in some analyses, but all results are based predominantly on canals in brackish or saline marshes. VEGETATION COMMUNITY Overall extent (4 studies): One paired, site comparison study in marshes in the USA reported that emergent vegetation coverage was typically lower in backfilled canals, after four years, than in adjacent undisturbed marsh. Three other studies in marshes in the USA simply reported coverage of emergent marsh vegetation between 6 months and 25 years after backfilling canals. All four studies reported that coverage was greater on former spoil areas alongside canals than within the partly filled canal channels. Two of the studies also reported the frequency of submerged/floating vegetation after 6–60 months, and one reported coverage of upland plant species on spoil banks that had not been completely levelled after 6–11 years. Overall richness/diversity (2 studies): One replicated, site comparison study in marshes in the USA reported that former spoil areas alongside backfilled canals had greater plant species richness than nearby natural marsh, due to the presence of upland species on unlevelled areas. One other study of a backfilled canal in predominantly brackish and saline marshes in the USA simply quantified richness of submerged vegetation four years after backfilling. VEGETATION ABUNDANCE   VEGETATION STRUCTURECollected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2988https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2988Thu, 25 Mar 2021 21:10:50 +0000Collected Evidence: Collected Evidence: Plug/dam canals or trenches: freshwater marshes One study evaluated the effects, on vegetation, of plugging/damming canals or trenches in freshwater marshes. The study was in the USA. VEGETATION COMMUNITY Overall extent (1 study): One replicated, site comparison study of backfilled canals in freshwater marshes in the USA reported that emergent marsh vegetation coverage was greater within the channels of plugged than unplugged canals, after 6–60 months. However, coverage on former spoil areas did not significantly differ between plugged and unplugged canals. VEGETATION ABUNDANCE   VEGETATION STRUCTURECollected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2991https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2991Mon, 29 Mar 2021 12:08:23 +0100Collected Evidence: Collected Evidence: Plug/dam canals or trenches: brackish/salt marshes Two studies evaluated the effects, on vegetation, of plugging/damming canals or trenches in brackish/salt marshes. Both studies were in the USA. There was overlap in the canals used in the studies. Both studies included some freshwater areas in some analyses, but all results are based predominantly on canals in brackish or saline marshes. VEGETATION COMMUNITY   VEGETATION ABUNDANCE Overall abundance (2 studies): Two replicated, site comparison studies studied emergent vegetation of backfilled canals in the USA. One study reported that plugged canals had greater coverage of emergent marsh vegetation than unplugged canals after 6–60 months. One study found that emergent vegetation coverage on former spoil heaps did not significantly differ alongside plugged and unplugged canals after 6–11 years. The first study also reported that plugged canals were more likely to contain floating/submerged vegetation than unplugged canals. VEGETATION STRUCTURECollected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2992https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2992Mon, 29 Mar 2021 12:08:35 +0100Collected Evidence: Collected Evidence: Plug/dam canals or trenches: freshwater swampsWe found no studies that evaluated the effects, on vegetation, of plugging/damming canals or trenches in freshwater swamps.   ‘We found no studies’ means that we have not yet found any studies that have directly evaluated this action during our systematic journal and report searches. Therefore we have been unable to assess whether or not the action is effective or has any harmful impacts. Please get in touch if you know of such a study for this action.Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2993https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2993Mon, 29 Mar 2021 12:08:51 +0100Collected Evidence: Collected Evidence: Plug/dam canals or trenches: brackish/saline swampsWe found no studies that evaluated the effects, on vegetation, of plugging/damming canals or trenches in brackish/saline swamps.   ‘We found no studies’ means that we have not yet found any studies that have directly evaluated this action during our systematic journal and report searches. Therefore we have been unable to assess whether or not the action is effective or has any harmful impacts. Please get in touch if you know of such a study for this action.Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2994https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F2994Mon, 29 Mar 2021 12:09:11 +0100Collected Evidence: Collected Evidence: Raise water level to restore degraded freshwater marshes Five studies evaluated the effects, on vegetation, of raising the water level to restore degraded freshwater marshes. There were three studies in the USA and one in each of the Netherlands and Japan. VEGETATION COMMUNITY Overall extent (1 study): One before-and-after study of a floodplain in Japan reported that the area covered by marsh vegetation was higher five years after dechannelizing a river than 10 years before. Community types (1 study): One before-and-after study of a floodplain in Japan reported changes in the area covered by different marsh plant communities over five years after dechannelizing a river compared to 10 years before. Community composition (1 study): One replicated study of dune slacks in the Netherlands reported changes in the overall plant community composition after stopping groundwater extraction (along with other interventions). Overall richness/diversity (2 studies): One replicated, site comparison study of dune slacks in the Netherlands reported that overall plant species richness was greater in restored slacks (groundwater extraction stopped five years previously, along with other interventions) than in mature unmanaged slacks. One replicated, before-and-after study of floodplain marshes in the USA reported that total plant species richness tended to be lower over nine years after raising the water table than before, but that there was no significant difference for diversity. Characteristic plant richness/diversity (1 study): One replicated study of dune slacks in the Netherlands simply quantified the richness of characteristic plant species – typical of dune slacks or nutrient-rich marshes – over five years after stopping groundwater extraction (along with other interventions). VEGETATION ABUNDANCE Overall abundance (3 studies): One replicated, before-and-after study of floodplain marshes in the USA reported that total vegetation cover tended to be lower over nine years after raising the water table than before. One replicated, randomized, paired, controlled, before-and-after study of freshwater marshes in the USA found that damming to raise the water table prevented increases in understory vegetation cover over the following year. One replicated study of dune slacks in the Netherlands simply quantified total vegetation over five years after stopping groundwater extraction (along with other interventions). Cover never exceeded 50%. Herb abundance (1 study): One replicated, randomized, paired, controlled, before-and-after study of freshwater marshes in the USA found that damming to raise the water table had no significant effect on cover of sedges Carex There were similar increases in dammed and undammed marshes over one year. Characteristic plant abundance (1 study): One replicated, before-and-after study of floodplain marshes in the USA reported changes in the cover of wetland- and habitat-characteristic plant species over nine years after raising the water table. Individual species abundance (3 studies): Three studies quantified the effect of this intervention on the abundance of individual plant species. For example, one replicated, before-and-after study in the USA reported that rewetted floodplain marshes became dominated by a non-native wetland shrub, approximately 4–9 years after raising the water table. One replicated study of a freshwater wetland in the USA reported that the effects of reflooding on the density of emergent plant species depended on the species and water level. VEGETATION STRUCTURECollected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3026https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3026Wed, 31 Mar 2021 14:47:11 +0100Collected Evidence: Collected Evidence: Raise water level to restore degraded brackish/salt marshes Two studies evaluated the effects, on vegetation, of raising the water level to restore degraded brackish/salt marshes. One study was in the Netherlands and one was in Tunisia. VEGETATION COMMUNITY Community types (2 study): One before-and-after study of a lakeshore brackish/salt marsh in Tunisia reported an increase in coverage of bulrush-dominated vegetation relative to salt marsh vegetation over three years after modifying a canal to retain water in the marsh. One study of a salt marsh in the Netherlands reported increased coverage of pioneer succulent plant communities, and reduced coverage of short-grass communities, over approximately 10 years following abandonment of the drainage system (along with other interventions). Overall richness/diversity (1 study): One study of a salt marsh in the Netherlands reported that overall plant species richness increased over 14 years after abandoning drainage systems (along with other interventions). VEGETATION ABUNDANCE Individual species abundance (1 study): One study of a salt marsh in the Netherlands reported that some individual plant species became more common over 14 years after abandoning drainage systems (along with other interventions). These included saltbush Atriplex prostrata and seablite Suaeda maritima. Some other species became less common, including creeping bentgrass Agrostis stolonifera and common cordgrass Spartina anglica. VEGETATION STRUCTURECollected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3027https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3027Wed, 31 Mar 2021 14:47:25 +0100Collected Evidence: Collected Evidence: Actively manage water level: freshwater marshes Ten studies evaluated the effects, on vegetation, of active water level management in freshwater marshes. Eight studies were in the USA. One study was in Cameroon and one study was in the Netherlands. VEGETATION COMMUNITY Community composition (1 study): One before-and-after study in the USA found that directly pumping water into drained marshes and wet meadows generated plant communities characteristic of wetter conditions. This change was reversed in some plots when the pump output was moved further away from the focal wetlands. Relative abundance (2 studies): One replicated, randomized, controlled study of freshwater marshes in the USA reported that irrigated and non-irrigated marshes supported a similar relative abundance of the most common plant species. One before-and-after study on a floodplain in Cameroon found that the relative abundance of some key plant species changed over four years after restoring wet-season flooding. There was also an increase in the cover of perennial relative to annual herbs. Overall richness/diversity (4 studies): One before-and-after study of a marsh/swamp in the USA found that overall plant diversity was higher in the autumn following a managed flood/drawdown than in the autumn before. Two before-and-after studies of marshes and wet meadows in the USA reported that plant species richness and/or diversity declined over 5–6 years of water level management (fluctuation or water addition). One study in the USA simply reported the number of plant species that colonized a floodplain, over three weeks after lowering the river level. VEGETATION ABUNDANCE Overall abundance (3 studies): One study of riparian moist/wet meadows in the USA reported that vascular plant biomass increased in two of three meadow types, over the second year of artificially augmented streamflow. Meanwhile, vascular plant cover declined in two of three meadow types. Two studies in the Netherlands and the USA simply quantified overall vegetation abundance after 1–9 growing seasons of active water level management (sometimes along with other interventions). Characteristic plant abundance (2 studies): Two before-and-after studies of marshes and wet meadows in the USA reported increases in abundance of some individual wetland- or habitat-characteristic species over 5–6 years of water level management (fluctuation or water addition). Moss abundance (1 study): One study of riparian moist/wet meadows in the USA reported that moss cover did not significantly change in two of three meadow types, over the second year of artificially augmented streamflow. It declined in the other meadow type. Individual species abundance (7 studies): Seven studies quantified the effect of this action on the abundance of individual plant species. For example, one before-and-after study of a marsh/swamp in the USA reported mixed effects of a managed flood/drawdown on species cover, including increased cover of Pacific willow Salix lucida and reduced cover of reed canarygrass Phalaris arundinacea. One controlled study of freshwater marshes in the USA found that irrigated marshes developed a greater biomass of pink smartweed Polygonum pensylvanicum, after one growing season, than marshes that were left dry. VEGETATION STRUCTURE Vegetation height (1 study): One replicated, randomized, controlled study of freshwater marshes in the USA reported that four common plant species were taller in irrigated than non-irrigated marshes. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3038https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3038Thu, 01 Apr 2021 10:02:54 +0100Collected Evidence: Collected Evidence: Actively manage water level: brackish/salt marshes Ten studies evaluated the effects, on vegetation, of active water level management in brackish/salt marshes. Six studies were in the USA. There was overlap in the sites used in two of these studies. Two studies were in Canada and based on the same experimental set-up. One study was in France and one was in Tunisia. VEGETATION COMMUNITY Community types (1 study): One before-and-after study of a lakeshore brackish/salt marsh in Tunisia reported an increase in coverage of bulrush-dominated vegetation over nine years of freshwater releases into the lake (to increase its level and restore winter flooding of the marsh). Community composition (3 studies): One replicated, paired, controlled, before-and-after study of brackish marshes in France reported that artificially flooded marshes developed different plant communities, over five years, to fields with unmanaged flooding. One before-and-after, site comparison study of brackish/salt marshes in the USA reported that the overall plant community composition changed more, over four years, in a marsh directly irrigated with treated wastewater than in downstream marshes. One replicated, paired, site comparison study of brackish/salt marshes in the USA reported that that marshes in which water levels were drawn down each spring/autumn (along with disking soils) shared only 24–34% of plant species with marshes that were not drawn down (or disked). Overall richness/diversity (5 studies): Two replicated, site comparison studies of brackish/salt marshes in the USA found that marshes in which water levels were managed (sometimes along with other interventions) had similar plant species richness and/or diversity to marshes without water level management. One replicated, site comparison study of brackish and salt marshes in the USA reported that marshes in which water levels were managed had similar or higher plant species richness, in winter, than marshes without water level management. One before-and-after, site comparison study of brackish/salt marshes in the USA reported that plant species richness increased, over four years, in marshes directly irrigated with treated wastewater – but only to similar levels as in downstream marshes. One replicated, paired, controlled, before-and-after study of brackish marshes in France reported that the effects of artificial flooding on plant species richness depended on whether the marshes were grazed. VEGETATION ABUNDANCE Overall abundance (2 studies): Two replicated, site comparison studies of brackish and salt marshes in the USA reported that marshes in which water levels were managed typically had similar overall vegetation cover to marshes without water level management. One of the studies also reported that cover of standing dead vegetation was higher in the managed marshes than in the unmanaged marshes. Individual species abundance (6 studies): Six studies quantified the effect of this action on the abundance of individual plant species. For example, four replicated, site comparison studies of brackish and salt marshes in the USA reported mixed effects of water level management on the abundance of saltmeadow cordgrass Spartina patens. One replicated, paired, controlled, before-and-after study of brackish marshes in France reported that the effects of artificial flooding on the cover of individual plant species depended on the flooding (and grazing) regime. VEGETATION STRUCTURE   OTHER Germination/emergence (2 studies): Two replicated studies of brackish marshes in Canada reported that seedlings of wetland plants germinated in the spring/summer following drawdowns, after a period of deep flooding. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3039https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3039Thu, 01 Apr 2021 10:03:10 +0100Collected Evidence: Collected Evidence: Cut large trees/shrubs to maintain or restore disturbance: freshwater marshes Four studies evaluated the effects, on vegetation, of cutting large trees/shrubs to maintain or restore disturbance in freshwater marshes. Three studies were in the USA. One was in Germany. VEGETATION COMMUNITY Community types (1 study): One study of a riparian wet meadow in Germany reported changes in the area of plant community types over four years after cutting trees/shrubs (along with grazing). Community composition (1 study): One replicated, randomized, controlled, before-and-after study aiming to restore freshwater marshes in the USA found that cutting trees (along with other interventions) significantly affected the overall plant community composition over the following five years. Overall richness/diversity (1 study): One study of a riparian wet meadow in Germany reported that plant species richness increased over four years after cutting trees/shrubs (along with grazing). VEGETATION ABUNDANCE Overall abundance (2 studies): Of two replicated, randomized, paired, controlled, before-and-after studies in the USA, one found that cutting and removing woody plants from a degraded wet prairie had no significant effect on overall vegetation cover three years later. The other study was in wet patches of a pine forest and found that understory vegetation cover increased more, over one year, where trees were thinned than where they were not thinned. 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 cutting trees (along with other interventions), 16 were obligate wetland taxa. Herb abundance (1 study): One replicated, randomized, paired, controlled, before-and-after study in wet patches of a pine forest in the USA found that cover of sedges Carex increased more, over one year, where trees were thinned than where they were not thinned. Tree/shrub abundance (2 studies): One replicated, randomized, paired, controlled, before-and-after study of a wet prairie in the USA found that woody plant cover declined, over three years, in plots where trees/shrubs were cut – but increased in plots where trees/shrubs were not cut. One study of a riparian wet meadow in Germany simply reported that some trees/shrubs regrew over four years after cutting trees/shrubs (along with grazing). Individual species abundance (1 study): One study quantified the effect of this action on the abundance of individual plant species. The replicated, randomized, paired, controlled, before-and-after study of a wet prairie in the USA found, for example, that cutting trees and shrubs had no significant effect on cover of the dominant herbaceous plant, tussock grass Deschampsia cespitosa, three years later. VEGETATION STRUCTURE Height (1 study): One site comparison study of a riparian wet meadow in Germany reported that an area in which trees/shrubs were cut back (along with reinstating cattle grazing) contained shorter vegetation than an adjacent unmanaged area. OTHER Survival (2 studies): One replicated, randomized, paired, controlled study in a wet prairie in the USA found that cutting woody plants did not significantly affect their survival in the following year. One study of a riparian wet meadow in Germany simply reported that 20% of black alder Alder glutinosa trees were still alive after being cut back and grazed for four years. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3046https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3046Thu, 01 Apr 2021 19:06:56 +0100Collected Evidence: Collected Evidence: Restore/create freshwater marshes or swamps (specific action unclear) Twenty-five studies evaluated the effects, on vegetation, of restoring/creating freshwater marshes or swamps using unclear or incompletely described actions. Twenty-three studies were in the USA. Two were in Canada. Two of the studies used the same set of wetlands. VEGETATION COMMUNITY Community types (1 study): One replicated, site comparison study in the USA reported that created wetlands had greater coverage of herbaceous vegetation after 7–8 years than natural wetlands, but lower coverage of forest and shrubby vegetation. Community composition (17 studies): Four replicated, site comparison studies in the USA found that the overall plant community composition in created freshwater wetlands differed from the community in natural wetlands, after 1–21 years. Two replicated, site comparison studies in the USA and Canada reported mixed effects of freshwater marsh restoration/creation on overall algal or plant community composition, depending on the habitat and use of mining waste during creation. Of four replicated, site comparison studies in the USA and Canada, three reported lower quality vegetation in restored/created wetlands than in natural wetlands, but one reported similar vegetation quality in created and natural wetlands. Two replicated, site comparison studies in the USA found that created marshes developed a plant community characteristic of similar wetness to natural marshes within 4–21 years – but in one study, this was only true for created marshes >10 years old. Seven replicated studies in the USA simply quantified the composition, quality or wetness of the plant community up to 22 years after wetland restoration/creation. Overall richness/diversity (17 studies): Eleven replicated studies, in the USA and Canada, compared overall plant richness/diversity in created/restored and natural/unmanaged freshwater wetlands. Five of the studies found that created/restored wetlands typically had similar plant taxonomic richness to natural/unmanaged wetlands. Three of the studies reported lower species richness in created than natural wetlands after 1–18 years. Two of the studies reported higher species richness in created than natural wetlands after 1–21 years. The final study reported mixed effects of marsh creation on plant species richness, depending on the vegetation zone and use of mining waste during creation. Two of the studies reported identical results for plant diversity as for richness (similar or greater in created vs natural wetlands) but one study found that the effect of management on plant diversity depended on the timing of drawdown. Six replicated studies in the USA simply quantified overall plant species richness and/or diversity over 1–16 years after wetland restoration/creation. Native richness/diversity (3 studies): Of two replicated, site comparison studies of freshwater wetlands in the USA, one found that restored/created wetlands contained more native plant species than natural wetlands after 1–11 years. The other found that restored wetlands contained fewer native plant species than natural wetlands after 2–8 years. One replicated study of swamp restoration sites in the USA simply quantified native plant richness over 1–8 years after intervention. VEGETATION ABUNDANCE Overall abundance (7 studies): Six replicated studies, all in the USA, compared overall vegetation abundance in created/restored and natural wetlands. Four of the studies found that created/restored freshwater wetlands contained less vegetation (cover or biomass) than natural wetlands after 1–18 years. Two of the studies found that created and natural fresh/brackish/saline wetlands contained a similar amount of vegetation (overall cover and density; wetland plant cover) after >1 year. One of these studies reported that restored wetlands had lower vegetation cover than natural marshes – but this reflected management goals. One replicated study in the USA simply quantified total vegetation cover and biomass 3–10 years after marsh creation. Herb abundance (2 studies): One replicated, site comparison study in the USA reported that created wetlands had greater overall cover of herb species, after 7–8 years, than natural wetlands. One replicated study in the USA simply quantified herb biomass in wetland restoration sites after 7–22 years. Tree/shrub abundance (1 study): One replicated study in the USA simply quantified the density of woody vegetation in wetland restoration sites after 7–22 years. Algae/phytoplankton abundance (1 study): One replicated, site comparison study in the USA found that ≤15-year-old restored freshwater marshes contained a similar phytoplankton biomass to natural marshes. Individual species abundance (9 studies): Nine studies quantified the effect of this action on the abundance of individual plant species. For example, one replicated, site comparison study in the USA found that created and natural freshwater marshes supported a similar abundance of pickerelweed Pontederia cordata after 1–11 years. VEGETATION STRUCTURECollected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3190https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3190Wed, 07 Apr 2021 07:27:57 +0100Collected Evidence: Collected Evidence: Raise water level to restore/create freshwater marshes from other land uses Twenty-six studies evaluated the effects, on vegetation, of raising the water level to restore/create freshwater marshes from other land uses or habitat types. Twenty-one studies were in the USA. There was one study in each of Israel, the UK, China, Luxembourg and Canada. Eight studies used sites from a common set of 62 restored prairie potholes in the Midwest USA. Five studies monitored the effects of one river dechannelization project in Florida. VEGETATION COMMUNITY Overall extent (5 studies): One replicated, paired, before-and-after, site comparison study in the USA reported that damming a stream reduced the area of emergent vegetation on the floodplain. Two before-and-after studies of a floodplain in the USA reported that after dechannelizing a river to raise the water level, the area of emergent herbaceous vegetation increased. Two studies in the USA and Luxembourg simply quantified coverage of wetland vegetation 1–6 years after raising the water table (sometimes along with other interventions). Community types (9 studies): Nine studies quantified the effect of this action on specific types of marsh vegetation. For example, one before-and-after study of a floodplain in the USA reported greatly increased coverage of wet prairie plant communities after dechannelizing a river to raise the water table, but only slightly increased coverage of mixed herbaceous/shrubby wetland communities. Five studies in the USA and Luxembourg simply quantified the number, abundance or extent of wetland plant communities present 1–6 years after raising the water table (typically along with other interventions). Community composition (8 studies): Three replicated, site comparison studies (two also paired) in the USA evaluated the effects of rewetting farmed depressions (along with planting cover crops in/around them). One of these studies reported that restored wetlands contained a different overall plant community to natural wetlands after 5–7 years. One study reported that the plant community composition differed more between restored and natural wetlands than amongst restored or natural wetlands. The final study found that restoration increased vegetation quality after ≥10 years, but not to the level of natural wetlands. Two site comparison studies in China and the USA reported that the plant community became more similar to natural wetlands over 6–15 years after raising the water level – in terms of species composition or overall wetness. Three replicated studies in the USA simply quantified the plant community composition for up to three years after rewetting farmland (sometimes along with other interventions). Overall richness/diversity (12 studies): Four replicated, site comparison studies (two also paired) of one set of historically farmed depressions in the USA reported that restored wetlands (rewetted, along with planting cover crops in/around the sites) had lower overall plant species richness than nearby natural wetlands, after 1–7 years. Two before-and-after, site comparison studies of historical wetlands on a floodplain in the USA reported that raising the water level reduced overall plant species richness in the following six years. One site comparison study of lakeshore marshes in China reported that the total plant species richness in former paddy fields with breached weirs was similar to a nearby natural marsh, after 2–15 years. Five studies (two replicated) in the USA and Israel simply quantified overall plant species richness and/or diversity between three months and 19 years after raising the water table (sometimes along with other interventions). Characteristic plant richness/diversity (1 study): One before-and-after, site-comparison study of a floodplain in the USA reported that dechannelizing a river to raise the water level had no clear effect on the richness of wetland-characteristic plant species in the following six years. VEGETATION ABUNDANCE                                                                             Overall abundance (9 studies): Three before-and-after, site-comparison studies of historical wetlands on a floodplain in the USA reported that dechannelizing a river to raise the water level reduced overall vegetation cover in the following 6–9 years. One site comparison study in China reported that vegetation biomass in former paddy fields with breached weirs was similar to a nearby natural marsh, after 2–15 years. In contrast, one replicated, site comparison study in the USA found that vegetation cover in rewetted, formerly farmed depressions (also planted with cover crops) was lower than in nearby natural wetlands, after 5–7 years. Four studies (two replicated) in the USA and the UK simply quantified vegetation abundance between three months and six years after raising the water table (sometimes along with other interventions). Characteristic plant abundance (4 studies): Three before-and-after studies (two also site comparisons) of historical wetlands on a floodplain in the USA reported that dechannelizing a river to raise the water level increased the abundance of habitat- and/or wetland-characteristic plant species in the following 6–9 years. One study in the UK simply quantified the abundance of wet meadow plant species present 3–5 years after rewetting farmland (and introducing grazing). Bryophyte abundance (1 study): One replicated, site comparison study in the USA found that the frequency of bryophytes in (the wettest parts of) marshes rewetted 34 years previously was not significantly different from their frequency in (the wettest parts of) nearby natural marshes. Individual species abundance (11 studies): Eleven studies quantified the effect of this action on the abundance of individual plant species. For example, one replicated, site comparison study of freshwater marshes in the USA reported that Kneiff’s feathermoss Leptodictyum riparium was the most abundant plant species in marshes rewetted 34 years previously and nearby natural marshes. One before-and-after study of historical wetlands on a floodplain in the USA reported that after dechannelizing a river to raise the water level, some plots became dominated by a non-native grass species. VEGETATION STRUCTURECollected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3198https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3198Fri, 09 Apr 2021 07:44:56 +0100Collected Evidence: Collected Evidence: Maintain dams or water impoundments One study evaluated the effects of maintaining dams or water impoundments on reptile populations. This study was in the USA. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (0 STUDIES) BEHAVIOUR (1 STUDY) Use (1 study): One replicated, before-and-after study in the USA found that after sediment removal, or dam maintenance along with sediment removal, one water impoundment was still used by Sonoran mud turtles and a second was not used. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3667https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3667Fri, 10 Dec 2021 11:22:04 +0000Collected Evidence: Collected Evidence: Modify dams or water impoundments to enable wildlife movements One study evaluated the effects on reptile populations of modifying dams or water impoundments to enable wildlife movements. This study was in the USA. COMMUNITY RESPONSE (0 STUDIES) POPULATION RESPONSE (0 STUDIES) BEHAVIOUR (1 STUDY) Use (1 study): One study in the USA found that an eel ladder was used by common watersnakes in five of eight years. Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3668https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3668Fri, 10 Dec 2021 11:24:28 +0000Collected Evidence: Collected Evidence: Install artificial dams in streams to raise water levels One study evaluated the effects on butterflies and moths of installing artificial dams in streams to raise water levels. This study was in the USA. COMMUNITY RESPONSE (0 STUDIES)   POPULATION RESPONSE (1 STUDY) Survival (1 study): One replicated, randomized, paired, controlled study in the USA found that installing artificial dams in streams did not increase the survival of Appalachian brown butterfly eggs, caterpillars or pupae. BEHAVIOUR (0 STUDIES)  Collected Evidencehttps%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3954https%3A%2F%2Fwww.conservationevidence.com%2Factions%2F3954Sat, 13 Aug 2022 15:22:51 +0100
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What Works in Conservation

What Works in Conservation provides expert assessments of the effectiveness of actions, based on summarised evidence, in synopses. Subjects covered so far include amphibians, birds, mammals, forests, peatland and control of freshwater invasive species. More are in progress.

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