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Biodiversity Data Journal :
Data Paper (Biosciences)
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Corresponding author: Roberto Pizzolotto (piz@unical.it), Fabiola Durante (fabiola.durante@unical.it)
Academic editor: Paulo Borges
Received: 29 Jan 2025 | Accepted: 07 Mar 2025 | Published: 15 Apr 2025
© 2025 Roberto Pizzolotto, Fabiola Durante
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Pizzolotto R, Durante F (2025) Dataset of carabid beetles in Southern Dolomites from 1983 to 1996. Biodiversity Data Journal 13: e148207. https://doi.org/10.3897/BDJ.13.e148207
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The Carabid beetles are a key group for assessing ecological characteristics of natural environments because they play a role as bioindicator organisms suitable for both theoretical and applied studies. Moreover, they are one of the few Coleoptera orders with numerous quantitative ecological studies conducted using consistent methodologies in the Dolomite environments (Eastern Italian Alps). In this paper, natural and semi-natural habitats located at mid- and high-altitude located in the Southern Dolomites were studied, specifically the populations of carabids living in alpine grasslands and active scree-slopes from 1300 m a.s.l. to 2160 m a.s.l.
This dataset advances the initiative of adopting a formal structure for carabid beetle datasets and promotes open access to such data. This publication specifically targets historical data published in grey literature, written in Italian or published as technical reports not available online. The Darwin Core standard was used to create the datasets and tables have been made available through the GBIF portal (the Global Biodiversity Information Facility). This ensures the data adhere to the FAIR principles (Findable, Accessible, Interoperable, Reusable), aligning with current best practices in scientific research.
Alps, Darwin Core, GBIF, Italy, soil fauna
The aim of this dataset is to increase our understanding of carabid beetle communities inhabiting mountain environments in the Eastern Alps. The first contribution of this study is to make datasets available to the scientific community via the GBIF portal, making them freely accessible and compliant with FAIR principles. Additionally, we gave FAIR quality to data previously limited to grey literature or Italian-language publications (or both), therefore inaccessible to the international research community (
The main object of this study is historical data on carabid beetles, sourced from grey literature written in Italian and from technical reports not accessible online. Most of the material is stored in the collection of the Dept. B.E.S.T. of the Calabria University (Italy). The focus on these organisms is due to their well-documented biology and ecological significance, both globally and specifically in the Italian Alps (
The main purpose of this dataset is to give open access to data as complete as possible on the distribution and abundance of carabid beetles in the Eastern Dolomites (Italian Alps).
This is the second available dataset, after
Carabid beetles were collected between 1983 and 1996, sampling 27 sample sites in different locations, in different years by pitfall traps. At the end of every sampling campaign, a “year’s sample” was obtained, which is the sum of the collections made during the research campaign. The pitfall traps were plastic vessels with an upper diameter of 9.2 cm, a depth of 11 cm and a small opening at 4 cm below the rim to avoid rainwater overflowing, filled with 200 ml of a preservative mixture made of wine vinegar and 5% formalin.
Given the unpredictable events that cause traps to break (e.g. cows, tourists, marmots), the number of individuals sampled in a year within each site (year sample) may be affected by an uneven sampling effort. For this reason, species abundance is evaluated as annual Activity Density (aAD), which is based on the total annual number of individuals caught and on the total annual sampling effort unit (EU), related to a period of ten days, as follows:
eu = (traps * days) / 10
eu is the effort unit for each single sampling period from which the total annual capture effort (EU) is given by the sum of:
EU = ∑eu
and, therefore,
aAD = total number of individuals / EU.
Pitfall traps were randomly placed, distanced about 10 metres, in each of the sites included in the study (see Table
Sample sites description. Data from sites with label ending with 1983 were published in
| Site | Altitude (a.s.l.) | Aspect | Slope | Veg. cover | Vegetation NAT2000 |
| VdFAo1_1983 | 1950 m | NE | 45° | 35% | 8120 Calcareous and calcshist screes of the montane to alpine levels (Thlaspietea rotundifolii) |
| VdFAo2_1983 | 2120 m | SSE | 50° | 40% | 8120 Calcareous and calcshist screes of the montane to alpine levels (Thlaspietea rotundifolii) |
| VdFAo3_1983 | 2080 m | WNW | 45° | 40% | 8120 Calcareous and calcshist screes of the montane to alpine levels (Thlaspietea rotundifolii) |
| VdFSC1_1983 | 2160 m | SSW | 35° | 95% | 6170 Alpine and subalpine calcareous grasslands |
| VdFSC2_1983 | 2100 m | SW | 45° | 65% | 6170 Alpine and subalpine calcareous grasslands |
| VdFSC3_1983 | 2080 m | NW | 25° | 50% | 6170 Alpine and subalpine calcareous grasslands |
| VdFSC4_1983 | 2090 m | NE | 40° | 60% | 6170 Alpine and subalpine calcareous grasslands |
| VdFSC5_1983 | 2090 m | W | 20° | 100% | 6170 Alpine and subalpine calcareous grasslands |
| VdFAH_1983 | 1970 m | NNE | 45° | 60% | 8120 Calcareous and calcshist screes of the montane to alpine levels (Thlaspietea rotundifolii) |
| VdFAH2_1989 | 2000 m | NW | 35° | 60% | 8120 Calcareous and calcshist screes of the montane to alpine levels (Thlaspietea rotundifolii) |
| VdFRM_1989 | 1950 m | NW | 40° | 70% | 4060 Alpine and Boreal heaths |
| VdFAd_1983 | 1980 m | E | 35° | 100% | 8120 Calcareous and calcshist screes of the montane to alpine levels (Thlaspietea rotundifolii) |
| VdFNa_1989 | 1880 m | NE | 2° | 100% | Nardus stricta-dominated grasslands |
| VdFRu_1989 | 1880 m | NNE | 2° | 80% | Rumicetum alpini on overgrazed pasture |
| VdFdia1_1983 | 2160 m | SSW | 2° | 50% | Rocky habitat |
| VdFdia2_1983 | 2050 m | SSE-NNW | 2° | 40% | Rocky habitat |
| ErBrEB1_1996 | 1950 m | SE | 0°-2° | 100% | Grassland in snow bed |
| ErBrEB2_1996 | 1960 m | SW | 25° | 100% | Grass mats on calcareous scree |
| ErBrEB3_1996 | 1970 m | NE | 35° | 1% | 8120 Calcareous and calcshist screes of the montane to alpine levels (Thlaspietea rotundifolii) |
| ErBrEB4_1996 | 1700 m | NW | 25° | 100% | Alpine pasture |
| LaVarLV1_1995 | 1700 m ca. | N | 5° | 100% | Mown grasslands and grazed pastures |
| LaVarLV2_1995 | 1700 m ca. | E | 20° | 100% | Mown grasslands and grazed pastures |
| LaVarLV3_1995 | 1700 m ca. | S | 5° | 100% | Mown grasslands and grazed pastures |
| LaVarLV4_1995 | 1700 m ca. | S | 40° | 90% | Mown grasslands and grazed pastures |
| LaVarLV5_1995 | 1700 m ca. | E | 3° | 100% | Mown grasslands and grazed pastures |
| MGarGa2_1990 | 1300 m | SE | 20° | 90% | Montane pastures |
| MGarGa1_1990 | 1300 m | NW | 20° | 100% | Montane pastures |
The study area was in the South Eastern Dolomites, Italian Eastern Alps. The main peaks are (from west to east): Monte Pavione 2335 m, Piz di Sagron 2486 m, Monte Brendol 2160 m, Monte Talvena 2542 m and Monte Schiara 2565 m (see Fig.
45.95 and 46.26 Latitude; 11.83 and 12.171 Longitude.
| Rank | Scientific Name | Common Name |
|---|---|---|
| family | Carabidae | carabids |
CC BY-NC 4.0
Table of the sampled sites. Twenty-seven sites (records) were sampled within 1300–2200 m altitude, including montane pastures to alpine scree-slopes. See text for details and map.
| Column label | Column description |
|---|---|
| eventID | An identifier for the set of information associated with a dwc:Event (something that occurs at a place and time). Here an identifier specific to the dataset. |
| samplingProtocol | The names of, references to, or descriptions of the methods or protocols used during a dwc:Event. |
| sampleSizeValue | Number of active pitfall traps. |
| sampleSizeUnit | One pitfall trap. |
| samplingEffort | ∑traps*(days/10). |
| eventDate | The date-time or interval during which a dwc:Event occurred. |
| startDayOfYear | The earliest integer day of the year on which the dwc:Event occurred (e.g. 33 is the 2nd of February). |
| endDayOfYear | The latest integer day of the year on which the dwc:Event occurred. |
| countryCode | The standard code for the country in which the dcterms:Location occurs. |
| maximumElevationInMetres | The upper limit of the range of elevation (altitude, usually above sea level), in metres. |
| habitat | A category or description of the habitat in which the dwc:Event occurred. Here the NAT2000 classification was used. |
| decimalLatitude | Latitude in decimal degrees. |
| decimalLongitude | Longitude in decimal degrees. |
| geodeticDatum | The ellipsoid, geodetic datum or spatial reference system (SRS), upon which the geographic coordinates given in dwc:decimalLatitude and dwc:decimalLongitude are based. |
| coordinateUncertaintyInMetres | The horizontal distance (in metres) from the given decimalLatitude and decimalLongitude describing the smallest circle containing the whole of the Location. |
| locality | Geographic information of the place where sample sites were located. |
Twenty-seven records (i.e. sample sites, see previous table) where the annual Activity Density of 66 species was given.
| Column label | Column description |
|---|---|
| eventID | An identifier for the set of information associated with a dwc:Event (something that occurs at a place and time). Here an identifier specific to the dataset (the same as for the event table). |
| occurrenceID | An identifier for the Occurrence, possibly a persistent global unique identifier. Here, it is given by the eventID plus the four first letters of genus and species. |
| basisOfRecord | The specific nature of the data record. Here, all records come from human observation. |
| individualCount | The number of individuals present at the time of the dwc:Occurrence. |
| organismQuantity | A number or enumeration value for the quantity of organisms. Here, an index of activity density (see organismQuantityType column). |
| organismQuantityType | The type of quantification system used for the quantity of organisms. Here, the activity density = individualCount/sampling effort. |
| lifeStage | The age class or life stage of the dwc:Organism(s) at the time the dwc:Occurrence was recorded. |
| occurrenceStatus | A statement about the presence or absence of a dwc:Taxon at a Location. |
| scientificName | The full scientific name. |
| kingdom | The full scientific name of the kingdom in which the species is classified. |
| phylum | The full scientific name of the phylum in which the species is classified. |
| class | The full scientific name of the class in which the species is classified. |
| order | The full scientific name of the order in which the species is classified. |
| family | The full scientific name of the family in which the species is classified. |
| genus | The full scientific name of the genus in which the species is classified. |
| specificEpithet | The name of the species epithet of the dwc:scientificName. |
| taxonRank | The taxonomic rank of the most specific name in the dwc:scientificName. |
A total of 56 species were collected in 27 sample sites (Table
Species list. Frequence% gives the relative frequency, while Total aAD gives the sum of the aAD of each species in the 27 sample sites.
| Species | Frequence% | Total aAD |
| Pterostichus burmeisteri Heer, 1837 | 100.0 | 81.288 |
| Pterostichus josephi Csiki, 1930 | 85.2 | 46.571 |
| Calathus melanocephalus (Linnaeus, 1758) | 66.7 | 9.605 |
| Carabus germarii Sturm, 1815 | 66.7 | 7.269 |
| Carabus creutzeri Fabricius, 1801 | 63.0 | 17.499 |
| Trichotichnus laevicollis (Duftschmid, 1812) | 63.0 | 10.500 |
| Carabus convexus Fabricius, 1775 | 55.6 | 4.124 |
| Amara alpestris A. & G.B.Villa, 1833 | 51.9 | 42.505 |
| Carabus bertolinii (Kraatz, 1878) | 48.1 | 6.996 |
| Notiophilus aquaticus (Linnaeus, 1758) | 44.4 | 1.117 |
| Abax ecchelii Bertolini, 1887 | 37.0 | 5.997 |
| Duvalius breiti (Ganglbauer, 1900) | 33.3 | 1.026 |
| Nebria diaphana K. & J.Daniel, 1890 | 33.3 | 2.710 |
| Amara nitida Sturm, 1825 | 29.6 | 1.587 |
| Cychrus angustatus Hoppe & Hornschuch, 1825 | 29.6 | 0.520 |
| Leistus nitidus (Duftschmid, 1812) | 29.6 | 1.901 |
| Stomis rostratus (Duftschmid, 1812) | 29.6 | 0.319 |
| Abax parallelepipedus (Piller & Mitterpacher, 1783) | 25.9 | 1.214 |
| Abax pilleri Csiki, 1916 | 25.9 | 8.997 |
| Calathus micropterus (Duftschmid, 1812) | 25.9 | 1.540 |
| Tapinopterus placidus (Rosenhauer, 1847) | 25.9 | 0.484 |
| Dyschirius globosus (Herbst, 1784) | 22.2 | 0.169 |
| Harpalus latus (Linnaeus, 1758) | 22.2 | 0.834 |
| Harpalus solitaris Dejean, 1829 | 22.2 | 0.654 |
| Molops piceus (Panzer, 1793) | 22.2 | 0.864 |
| Trichotichnus knauthi (Ganglbauer, 1901) | 22.2 | 0.854 |
| Amara erratica (Duftschmid, 1812) | 18.5 | 0.859 |
| Laemostenus janthinus (Duftschmid, 1812) | 18.5 | 6.784 |
| Trechus pallidulus Ganglbauer, 1891 | 18.5 | 2.508 |
| Cymindis vaporariorum (Linnaeus, 1758) | 14.8 | 0.439 |
| Pterostichus schaschli (Marseul, 1880) | 14.8 | 1.900 |
| Amara montivaga Sturm, 1825 | 11.1 | 0.170 |
| Bradycellus caucasicus (Chaudoir, 1846) | 11.1 | 0.044 |
| Harpalus rubripes (Duftschmid, 1812) | 11.1 | 0.101 |
| Lebia chlorocephala (J.J.Hoffmann, 1803) | 11.1 | 0.074 |
| Notiophilus biguttatus (Fabricius, 1779) | 11.1 | 0.432 |
| Poecilus versicolor (Sturm, 1824) | 11.1 | 7.293 |
| Amara communis (Panzer, 1796) | 7.4 | 0.123 |
| Amara lunicollis Schiödte, 1837 | 7.4 | 2.976 |
| Bembidion glaciale Heer, 1837 | 7.4 | 0.524 |
| Bembidion lampros (Herbst, 1784) | 7.4 | 11.243 |
| Cychrus attenuatus (Fabricius, 1792) | 7.4 | 1.585 |
| Laemostenus schreibersii (Küster, 1846) | 7.4 | 0.041 |
| Amara brunnea (Gyllenhal, 1810) | 3.7 | 3.500 |
| Badister bullatus (Schrank, 1798) | 3.7 | 0.013 |
| Bembidion deletum Audinet-Serville, 1821 | 3.7 | 0.010 |
| Carabus coriaceus Linnaeus, 1758 | 3.7 | 0.118 |
| Carabus problematicus Herbst, 1786 | 3.7 | 0.013 |
| Harpalus honestus (Duftschmid, 1812) | 3.7 | 0.027 |
| Harpalus laevipes Zetterstedt, 1828 | 3.7 | 0.042 |
| Harpalus marginellus Gyllenhal, 1827 | 3.7 | 0.056 |
| Nebria jockischii Sturm, 1815 | 3.7 | 0.020 |
| Pterostichus rhaeticus Heer, 1837 | 3.7 | 0.020 |
| Pterostichus strenuus (Panzer, 1796) | 3.7 | 0.048 |
| Pterostichus vernalis (Panzer, 1796) | 3.7 | 0.056 |
| Synuchus vivalis (Illiger, 1798) | 3.7 | 0.143 |