The journal, Conservation Evidence
Our online journal publishes research, monitoring results and case studies on the effects of conservation interventions. All papers include some monitoring of the effects of the intervention and are written by, or in partnership with, those who did the conservation work. It includes interventions such as habitat creation, habitat restoration, translocations, reintroductions, invasive species control, and education or integrated conservation development programmes, from anywhere around the world.
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A volume is created each year with peer-reviewed papers published throughout the year. We now accept Short Communications as well as standard papers.
Special issues contain new papers on a specific topic.
Virtual collections collate papers published in the journal on specific topics such as management of particular groups of species.
To search for papers on a specific topic within the journal select Advanced search, enter your keyword(s) and within the Source box type: "conservation evidence". This will take you to a list of actions that contain Conservation Evidence papers. In order to see the list of individual Conservation Evidence papers on the topic, please click on 'You can also search Individual Studies' at the top of this page.
Newell D. (2019), 16, 24-26
Common swifts Apus apus have shown significant declines in the UK over recent decades, and one possible cause is loss of nesting sites. Nest boxes have previously shown to be effective for this species. Here we test whether the addition of an artificial ‘nest form’ affected the occupancy of nest boxes. Nest boxes that contained a form were 4.6 times more likely to be occupied by common swifts than nest boxes without a form. The design of the form did not appear to affect occupancy rate. Further study is needed to discover whether nest forms increase overall occupancy rates.
Davies J.G. (2019), 16, 17-23
The intervention described in this paper was designed to allow greater horseshoe bats Rhinolophus ferrumequinum to cross safely underneath a newly constructed road scheme in Pembrokeshire, Wales. The mitigation measures, consisting of bridges, culverts and underpasses, were designed and positioned to increase the likelihood that they would be used by bats. These features were then monitored to determine their effectiveness from the proportion of bats flying safely through the mitigation compared to over the carriageway. This was done using a combination of bat surveyors with hand-held detectors and night-vision equipment, and automated bat detectors. Effectiveness of the different mitigation features increased with increasing cross-sectional area, with a culvert of 1500 mm diameter used less frequently than a larger culvert of 1800 mm x 3000 mm. The larger mitigation measures were generally more than 85% effective. Position in the landscape and the presence of features to guide bats into the mitigation are also likely to be important. In order to assess the likely impacts of a new road scheme on a designated bat population this study also considers local bat population trends, the time of night when most bats cross the road and approximate traffic volumes at these times.
Hosie C., Rothero E.C. & Wallace H. (2019), 16, 12-16
In July 2010 green hay from a species-rich donor field was used to diversify a species-poor floodplain meadow (the receiver field), which had previously been managed as a pasture. The receiver site was prepared through harrowing. Green hay was then collected from the donor site and spread on the receiver site using a bale shredder and spreader. It was then managed as a hay meadow, with an annual hay cut in July or August, followed by aftermath grazing. The vegetation in the receiver field was monitored from 2010-2017, as was an adjacent species-rich meadow, which was used as a target reference site. Over this period, the receiver field moved towards a species-rich sward, similar to the target Alopecurus pratensis - Sansguisorba officinalis floodplain community. In 2011, 12 months after the green hay application and change of management, species richness had increased significantly, as had the goodness-of-fit to the target floodplain-meadow community. The transformation from species-poor eutrophicated grassland to a more herb-rich floodplain meadow continued over the following six years, with further increases in the frequency and cover of target species.
White I.C. & Hughes S.A. (2019), 16, 6-11
The hazel dormouse Muscardinus avellanarius has experienced a marked decline in the UK in recent years, attributable in part to habitat fragmentation associated with an expanding road and rail network. A number of arboreal crossing structures have been installed in the UK to reconnect fragmented habitat, but the only proven usage of such structures by wild hazel dormice has been associated with a large-scale land bridge. This has highlighted the need for affordable, evidence-based alternative designs. We tested the effectiveness of a new dormouse bridge, previously shown to be used by Japanese dormice Glirulus japonicas in Japan, in reconnecting two woodland patches bisected by a railway in southern England. Hazel dormice were recorded on the bridge within nine hours of its erection and exhibited a clear preference for using the bridge, with more than ten times more observations of dormice on the bridge compared to crossing the railway at ground level. Red squirrels Sciurus vulgaris, another rare UK mammal, were also recorded on the bridge. The trial provided evidence of the effectiveness of this design of crossing structure in reconnecting arboreal habitat for hazel dormice and other wildlife, with implications for hazel dormouse mitigation in infrastructure projects.
Shellswell C.H. & Squire V. (2019), 16, 1-5
As part of the ‘Save Our Magnificent Meadows’ project, a two hectare field was converted to hay meadow on the National Trust’s Llanerchaeron Estate in west Wales. The field had previously been heavily grazed by sheep. Green hay was collected from an established meadow and spread by hand onto the receptor site in 2014, in order to increase the number of plant propagules present. The field was then managed as a hay meadow, with aftermath grazing. There was a significant increase in both positive indicator species and forb cover over the five year period from 2013-2017. In 2013, there was less than one positive indicator species/quadrat compared to 4.6 positive indicator species/quadrat in 2017. The results are discussed in relation to the change in management from intensive sheep grazing to hay making with aftermath grazing, and the spreading of green hay to increase the number of plant propagules present.