<?xml version="1.0" encoding="UTF-8"?>
<rss version="2.0" xmlns:dc="http://purl.org/dc/elements/1.1/" xmlns:atom="http://www.w3.org/2005/Atom">
  <channel>
    <atom:link rel="self" type="application/rss+xml" href="https://researchdata.se/sv/catalogue/search.rss?search=smultron"/>
    <link>https://researchdata.se/sv/catalogue</link>
    <title>Researchdata.se</title>
    <description>Search results</description>
    <language>sv</language>
    <item>
      <title>Data och kod för "Strong diel variation in the activity of insect taxa sampled by Malaise traps"</title>
      <description>Här presenteras all data och kod för artikeln "Strong diel variation in the activity of insect taxa sampled by Malaise traps" av Viktor Gårdman, Emme McDonald &amp; Tomas Roslin.

Provtagningen av insekter har utförts av författarna . 24 Malaisefällor sattes upp i en boreal skog i centrala Sverige  (Lat. 60.024855, long. 17.751336) och tömdes varannan timme under fem dagar, med undantag för nätter (22:00-06:00), som hade ett interval på fyra timmar (tömning 22:00, 02:00, 06:00). Malaisefällornas position i förhållande till varandra illustreras bäst via Fig. 1B i artikeln. Insekterna identifierades till taxonomisk familj för flugor (Diptera), skalbaggar (Coleoptera) och steklar (Hymenoptera). Överfamiljerna Chalcidoidea och Cynipoidea inom Parasitsteklar (Parasitica; Hymenoptera) identifierades enbart till överfamilj på grund av svårigheter med att familjebestämma arter inom dessa överfamiljer. Halvvingar (Hemiptera) bestämdes till familj inom skinbagggar (Heteroptera), men enbart till underordning för stritar (Auchenorrhyncha) och växtlöss (Sternorrhyncha). För att förenkla bestämningsprocessen så gjordes ingen vidare identifiering av småfjärilar (microlepidoptera) och för alla insektsordningar förutom Coleoptera, Diptera, Hymenoptera, Hemiptera och Lepidoptera identifierades arter enbart till ordning.

Filen "HRS_SpeciesData" innehåller information om varje individ som fångades under provtagningsperioden. Det inkluderar datum för fångsten ('Date', givet som DD/M); vilken fälla som individen hittades i (TrapID); tid i hh:mm (Time); tid i enbart timmar (Time_con), tid som en fraktion mellan 0 (00:00) och 1 (23:59) (Time_Num); superfamilj för varje taxon (Superfamily); taxon som varje individ delats in i (Taxon). För taxon med högre taxonomisk nivå än superfamilj anges den taxonomiska nivån i kolumnen för superfamilj.

Filen "HRS_EnviData" innehåller information om hur många individer per taxon som fångades vid varje provtagningstillfälle för de 17 mest frekventa taxa (förekommande som fler än 49 individer eller vid mer än 19 provtagningstillfällen), summerat över alla fällor. Kolumnerna "Taxon" och "Superfamily" följer samma princip som ovan, men här finns även en kolumn för taxonomisk ordning (Order). Kolumnerna för tid och datum följer samma princip som ovan. Kolumnen "ID" är en unik kombination av datum och tid anget som DDhh. T.ex tömningen 20:00 den 15:e har ID 1520. Utöver abundansen av individer för varje ID och taxa ges vädervariabler. Temperatur anges i grader Celsius (°C), vind i meter per sekund (m/s), molntäcke (cloud cover) som en fraktion mellan 0 (klar himmel) och 1 (totalt molntäcke), regn i mm, vindriktning i väderstreck och relativ luftfuktighet i %. Värdena är medelvärden från fem mätningar varje halvtimme från den förra provperioden till nästa, med undantag för nätter där medelvärden kommer från nio halvtimmesmätningar per tömning (tömning 22:00, 02:00, 06:00). Väderdatan kommer från väderstationen 327 Björklinge (Lat. 60.05042, long. 17.62149) och tillhandahålls av Trafikverket (https://www.trafikverket.se/).

All kod är skriven in R version 4.4.0 och presenteras via Rmarkdown</description>
      <pubDate>Fri, 05 Dec 2025 12:45:22 GMT</pubDate>
      <link>https://researchdata.se/sv/catalogue/dataset/2025-211</link>
      <guid>https://researchdata.se/sv/catalogue/dataset/2025-211</guid>
      <dc:publisher>Sveriges lantbruksuniversitet</dc:publisher>
      <dc:creator>Viktor Gårdman</dc:creator>
      <dc:creator>Emme McDonald</dc:creator>
      <dc:creator>Tomas Roslin</dc:creator>
    </item>
    <item>
      <title>Samhällen i infrastrukturmiljöer är artrika men hyser bara delvis arter kopplade till ängs- och betesmarker</title>
      <description>Denna studie är en del av projektet GINFRA – green rights-of-way infrastructure for biodiversity and ecosystem services. Projektets huvudsyfte var att kvantifiera om linjära infrastrukturmiljöer (vägkanter och kraftledningsgator) bidrar till mångfalden av växter och insekter i olika rumsliga skalor. Detta gjordes genom att uppskatta hur linjära infrastrukturmiljöers mängd i landskapet bidrar till mångfalden samt hur mycket de bidrar till landskapets konnektivitet.

Datan samlades genom att inventera dagfjärilar, humlor, och växter i fem typer av gräsmarker (betesmarker, vägrenar längs enskilda vägar, vägrenar längs allmänna vägar, kraftledningsgator, och åkerkanter). Alla dessa habitat typer fanns inom 32 landskap med 4 km² area, som skiljde sig i areal av linjära infrastrukturmiljöer (vägrenar och kraftledningsgator) och ängs-och betesmarker. Arealen av andra markanvändningar var konstanta mellan landskap och alla landskap var skogsdominerade.

This study makes part of the research project GINFRA – green rights-of-way infrastructure for biodiversity and ecosystem services. The aim of the project was to quantify whether linear infrastructure habitats (road verges and power-line corridors) support biodiversity by assessing the influence of the area of these habitats in the landscape, their contribution to landscape connectivity and population persistence.
The linked data was collected by surveying butterflies, bumblebees, and vascular plants in five types of prevalent grasslands (pastures, road verges along small gravel roads, road verges along big paved roads, power line corridors, and field borders). These grasslands were embedded in 32 landscapes with an area of 4 km2 that differed in the area of linear infrastructure habitats (road verges and power line corridors) and semi-natural grasslands of high nature value, while other land-use types were kept constant. The landscapes were dominated by forest. 
Within each grassland habitat, the surveyor established a 200 m transect and then identified all butterflies and bumblebees along it. For plants, a 1 x 1 m quadrat was established at the centre of a 50 m section in each transect, i.e. each transect had four plots in which all plant species were identified. 

The dataset consists of the following files: 
1.	Transect_coordinates: this file contains the coordinates for the beginning, end, and centroid of each transect. The explanation for each column in this file is as follows: 

Landscape: corresponds to the code of each 2 × 2 km landscape in which the transects are embedded. 
Transect_type: The name of the grassland habitat type is given. All landscapes contained at least three of the habitats: pastures, road verges along small gravel roads and road verges along big paved roads. The other two habitats, power line corridors and field borders, were present in only some of the landscapes. Power line corridors were present in half (i.e. 16) of the landscapes due to the design of the study. 
Start_X: Gives the x-coordinate for the start of the transect.
Start_Y: Gives the y-coordinate for the start of the transect.
End_X: Gives the x-coordinate for the end of the transect.
End_Y: Gives the y-coordinate for the start of the transect.
Centroid_X: Gives the x-coordinate for the centroid of the transect. This was calculated with ArcMap 10.7 using the start and end coordinates stated above. 
Centroid_Y: Gives the y-coordinate for the centroid of the transect. This was calculated with ArcMap 10.7 using the start and end coordinates stated above. 

All coordinates use the Swedish National reference frame, SWEREF99.

2.	Database_alpha_diversity: This file contains the necessary information for the analysis exploring whether species richness of butterflies, bumblebees, and vascular plants differs among the grassland habitat types, and whether such differences relate to the area of linear infrastructure habitats in the surrounding landscape and/or on the area of semi-natural pastures of high nature value. 

Landscape: corresponds to the code of each 2 × 2 km landscape in which the transects are embedded. 
Transect_type: The name of the grassland habitat type is given. All landscapes contained at least three of the habitats: pastures, road verges along small gravel roads and road verges along big paved roads. The other two habitats, power line corridors and field borders, were present in only some of the landscapes. Power line corridors were present in half (i.e. 16) of the landscapes due to the design of the study.
Butterfly_richness: Gives the number of butterfly species found along the corresponding transect type in a specific landscape.
Bumblebee_richness: Gives the number of bumblebee species found along the corresponding transect type in a specific landscape.
Vascular_plant_richness: Gives the number of vascular plant species found in all the four plots placed along the transect. 
Semi-natural_pastures: Gives the total area of semi-natural pastures of high nature value in square kilometres within the corresponding 2 × 2 km landscape.  
Powerline: Gives the total area of power line corridors in square kilometres within the corresponding 2 × 2 km landscape.  
Railway: Gives the total area of railways in square kilometres within the corresponding 2 × 2 km landscape.  
Road: Gives the total area of private (small) roads in square kilometres within the corresponding 2 × 2 km landscape.  
Public_road: Gives the total area of public (big) roads in square kilometres within the corresponding 2 × 2 km landscape.  
Between_fields: Gives the total area of grassy field borders in square kilometres within the corresponding 2 × 2 km landscape.  
Forest: Gives the total area of forest in square kilometres within the corresponding 2 × 2 km landscape.  
Arable: Gives the total area of arable land in square kilometres within the corresponding 2 × 2 km landscape.  
Semi-natural_pastures: Gives the total area in square kilometres within the corresponding 2 × 2 km landscape.  
Open_areas: Gives the total area of open areas (e.g. ley, parks, or other open grassy areas that are not semi-natural pastures of high nature value) in square kilometres within the corresponding 2 × 2 km landscape.  
Urban: Gives the total area of urban areas in square kilometres within the corresponding 2 × 2 km landscape.  
Water: Gives the total area of water surfaces in square kilometres within the corresponding 2 × 2 km landscape.  
PL: Stands for PowerLine. This field indicates whether the corresponding landscape had a presence (1) or absence (0) of a power line corridor. This was used as an explanatory factor in the models.
RD: Stands for Road Density. This field indicates whether the corresponding landscape had a high (1) or a low (0) density of roads. This was used as an explanatory factor in the models.

3.	Mean_abundance: This file contains the list of species found in the study, whether they were present in the Swedish Red list (2015), as well as the mean abundances, minimum abundances, and maximum abundances for each species in each habitat type.
Taxa: describes to which species group (taxa) the corresponding species belongs to. It can be either a bumblebee, a butterfly, or a vascular plant species or species group.
Species: name of the species or species group
Red_listed: If the corresponding species was present in the Swedish Red List (2015) then the species is classified as 1. If the species was not in the species list, the species or species group was classified as 0. An empty field corresponds to the category NA in the Swedish red list (Not Applicable). 
Mean_abundance_Pasture: Mean abundance of the corresponding species / species group in pastures. 
Min_abundance_Pasture: Minimum abundance of the corresponding species / species group in pastures. 
Max_abundance_ Pasture: Maximum abundance of the corresponding species / species group in pastures. 
Mean_abundance_Powerline: Mean abundance of the corresponding species / species group in power line corridors. 
Min_abundance_Powerline: Minimum abundance of the corresponding species / species group in power line corridors. 
Max_abundance_Powerline: Maximum abundance of the corresponding species / species group in power line corridors. 
Mean_abundance_Big_road: Mean abundance of the corresponding species / species group in road verges along big paved roads. 
Min_abundance_Big_road: Minimum abundance of the corresponding species / species group in road verges along big paved roads. 
Max_abundance_Big_road: Maximum abundance of the corresponding species / species group in road verges along big paved roads. 
Mean_abundance_Small_road: Mean abundance of the corresponding species / species group in road verges along small gravel roads. 
Min_abundance_Small_road: Minimum abundance of the corresponding species / species group in road verges along small gravel roads. 
Max_abundance_Small_road: Maximum abundance of the corresponding species / species group in road verges along small gravel roads. 
Mean_abundance_Field_border: Mean abundance of the corresponding species / species group in uncultivated field borders. 
Min_abundance_Field_border: Minimum abundance of the corresponding species / species group in uncultivated field borders. 
Max_abundance_Field_border: Maximum abundance of the corresponding species / species group in uncultivated field borders.</description>
      <pubDate>Thu, 04 Apr 2024 09:16:47 GMT</pubDate>
      <link>https://researchdata.se/sv/catalogue/dataset/2023-23-1</link>
      <guid>https://researchdata.se/sv/catalogue/dataset/2023-23-1</guid>
      <dc:publisher>Sveriges lantbruksuniversitet</dc:publisher>
      <dc:creator>Juliana Dániel-Ferreira</dc:creator>
      <dc:creator>Yoan Fourcade</dc:creator>
      <dc:creator>Riccardo Bommarco</dc:creator>
      <dc:creator>Jörgen Wissman</dc:creator>
      <dc:creator>Erik Öckinger</dc:creator>
    </item>
  </channel>
</rss>