Biodiversity Data Journal :
Data Paper (Biosciences)
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Corresponding author: Oleg Artaev (artaev@gmail.com)
Academic editor: Davide Badano
Received: 19 Aug 2024 | Accepted: 17 Oct 2024 | Published: 18 Oct 2024
© 2024 Alexander Ruchin, Vladimir Makarkin, Mikhail Esin, Leonid Egorov, Oleg Artaev, Evgeniy Lobachev, Sergey Lukiyanov, Vasilii Anikin, Anatoliy Khapugin, Gennadiy Semishin
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:
Ruchin A, Makarkin V, Esin M, Egorov L, Artaev O, Lobachev E, Lukiyanov S, Anikin V, Khapugin A, Semishin G (2024) Occurrences of Neuroptera and Raphidioptera in some regions in European Russia. Biodiversity Data Journal 12: e135019. https://doi.org/10.3897/BDJ.12.e135019
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The document presents an extensive set of data on the occurrence of Neuroptera and Raphidioptera in some regions of European Russia. The results of our own research, as well as scientific collections, have been processed. The data were collected in 17 regions. In our own research, we used different ways to obtain information, which allowed us to collect extensive material for the dataset. This dataset provides valuable information about the biodiversity of Neuroptera and Raphidioptera, the abundance of each taxon collected and the time of taxon collections.
Our dataset contains up-to-date information on the occurrence of Neuroptera and Raphidioptera in the Volga River and Don River Basins located in the Russian Plain of European Russia (17 regions of European Russia). The dataset consists of 4,826 occurrence records. All of them are georeferenced (17,373 individuals were studied). A total of 83 species of Neuroptera (8 families, 36 genera) and four species of Raphidioptera (2 families, 4 genera) were recorded within the investigated area.
dataset, observations, biodiversity, data paper
At present, the study and conservation of biological diversity are urgent global problems. Many species are on the verge of extinction, which is caused, amongst other factors, by anthropogenic activities that change the habitats of plants and animals. There are many causes that make habitats for living organisms change and disappear, for example, fires (
Neuroptera (lacewings), Megaloptera (dobsonflies, alderflies) and Raphidioptera (snakeflies) constitute the super-order Neuropterida, which is considered a sister of the Coleoptera and Strepsiptera (
This paper is aimed at describing a modern dataset on the occurrence of Neuroptera and Raphidioptera in the centre of European Russia, which has been recently published in GBIF as the Darwin Core Archive (
All Neuroptera and Raphidioptera individuals were identified at the species level. The taxonomic diversity of the study area is represented by 87 species belonging to 10 families of two orders. Given the long-term nature of our research, this almost complete list of species (except the family Coniopterygidae) forms natural self-reproducing populations, although records of a few species new for the region occur regularly.
Some common species are distributed nearly continuously in this region, both in forests and open habitats (e.g. Chrysoperla carnea (Stephens, 1836), Hemerobius humulinus Linnaeus, 1758 and Micromus angulatus (Stephens, 1836)). Similarly, Chrysopa perla (Linnaeus, 1758) occurs almost everywhere, except steppes. Many species are more or less common over the region, but occur mainly on deciduous or conifer trees in the forests (e.g. Nineta flava (Scopoli, 1763), N. vittata (Wesmael, 1841), Apertochrysa flavifrons (Brauer, 1851), Cunctochrysa albolineata (Killington, 1935) and C. cosmia (Navás, 1918)). Other species prefer open habitats (e.g. Psectra diptera (Burmeister, 1839), Chrysopa phyllochroma Wesmael, 1841, Ch. abbreviata Curtis, 1834, Ch. commata Кis & Újhelyi, 1965, Ch. dasyptera McLachlan, 1872 and Ch. walkeri McLachlan, 1893).
In general, it is difficult to estimate the real abundance of lacewings in natural biocoenoses, as it largely depends on the collecting methods. For example, crown bait traps set on various deciduous trees and pines attract almost exclusively those species of lacewings that feed at the imaginal stage on pollen and nectar of flowers (phytophages) and honeydews (glycophages) (
The known area of Nothochrysa fulviceps (Stephens, 1836) in Russia is restricted only to the studied region (
The population of Chrysopa viridinervis Jakowleff, 1869 in the Khvalynsk Forest (Saratov Oblast) is isolated. The nearest known localities of the species are the Donetsk Region and the North Caucasus.
The northern limit of the distribution of many southern species lies within this region. These are almost all species of Myrmeleontidae (except Myrmeleon bore (Tjeder, 1941) and M. formicarius Linnaeus, 1767), Ascalaphidae, Mantispidae (Mantispa aphavexelte U. Aspöck & H. Aspöck, 1994, Mantispilla perla (Pallas, 1772)) and a few Hemerobiidae (e.g. Micromus lanosus (Zelený, 1962)). Most of these occur in open habitats (steppe, forest-steppe, dry meadows), except for the Osmylidae and Hemerobiidae.
The occurrence in this region of three species (i.e. Chrysoperla mutata (McLachlan, 1898), Wesmaelius navasi (Andréu, 1911) and W. vaillanti (Navás, 1927)) is particularly noteworthy. These findings are northernmost in Europe.
To date, the eastern limit of the distribution for the following species lies within the region: Hemerobius lutescens Fabricius, 1793, H. micans, M. hirtus (Linnaeus, 1761), M. lanosus (Zelený, 1962), Sympherobius elegans and S. pygmaeus.
The occurrence of Chrysopa viridana and Ch. nigricostata in the region needs confirmation.
Each observation contained fundamental information, such as location (coordinates), date, name of observer and name of identifier. A large part of the coordinates was determined directly on site using a GPS device. The margin of error in the measurement of coordinates is 50 m. When using references and data before 2007, the coordinates were indicated, which were processed on the Google map with reference to the locality indicated by the authors of the publications. At the same time, the accuracy of such data was up to 500 m. The accuracy of determining coordinates is up to the fourth digit. In all cases, the WGS 84 coordinate system is used.
To collect the material, we used fermental traps (
The dataset contains information on occurrences of Neuroptera and Raphidioptera taxa in 17 Russian regions, namely Chuvash Republic, Republic of Kalmykia, Republic of Mordovia, Mari El Republic, Republic of Tatarstan, Astrakhan Oblast, Nizhny Novgorod Oblast, Penza Oblast, Orenburg Oblast, Ryazan Oblast, Samara Oblast, Saratov Oblast, Tambov Oblast, Ulyanovsk Oblast, Vladimir Oblast, Volgograd Oblast and Voronezh Oblast (Fig.
All collecting sites are located on the East European Plain. The main number of studied regions is situated on the Volga River Upland and Oka-Don Lowland, as well as Kalach Upland, Ergeni Upland, Don High Plain, Vyatsky Uval Upland, Mari Lowland, Peri-Caspian Lowland and Khoper-Buzuluk Plain. The north-to-south extent of the study area is more than 1300 km. In this regard, a number of climatic zones (i.e. taiga, zones of mixed forests, forest-steppe and steppe) are located within this area.
In the study area, the climate is moderate continental, with clearly distinct seasons (
In the study area, the watersheds of some large rivers of European Russia pass. The study area lies within the Black Sea Basin (watershed of the Don River) and the Caspian Sea Basin (watershed of the Volga River). In the study area, all rivers are of a typically low-lying type and belong to the Eastern European type. The relief is characterised by vast plain areas with altitudes of 130–250 m a.s.l. (up to 300 m a.s.l.). They alternate with wide valleys of large rivers, elongated in the meridional direction (e.g. Sura River, Moksha River, Don River, Voronezh River, Bityug River, Khoper River, Medveditsa River, Ilovlya River, Sviyaga River, Tsna River). In the northern part of the study area, swampy drainage lowlands are common.
44°58'52"N and 56°36'21"N Latitude; 39°14'39"E and 60°58'28"E Longitude.
There were 4,826 occurrence records published on Neuroptera and Raphidioptera from 17 regions of Russia: Chuvash Republic, Republic of Kalmykia, Republic of Mordovia, Republic of Tatarstan, Mari El Republic, Astrakhan Oblast, Nizhny Novgorod Oblast, Penza Oblast, Orenburg Oblast, Ryazan Oblast, Samara Oblast, Saratov Oblast, Tambov Oblast, Ulyanovsk Oblast, Vladimir Oblast, Volgograd Oblast and Voronezh Oblast. The authors of this dataset collected the records from 1987 to 2022. In addition, reliable data are presented from verified references that contain information on dates and localities of finds. We present a dataset that includes data on 83 species of Neuroptera and four species of Raphidioptera from natural and anthropogenic ecosystems. This is the first geographically referenced dataset on the occurrences of these insects for the European part of Russia. The classification of Neuropterida follows
Table
Taxonomic composition of the dataset, number of observations and individuals.
Taxa |
Number of observations |
Number of specimens |
Number of regions where the species has been recorded |
NEUROPTERA |
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Coniopterygidae |
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Aleuropteryx loewii Klapálek, 1894 |
1 |
1 |
1 |
Coniopteryx pygmaea Enderlein, 1906 |
6 |
43 |
1 |
Coniopteryx tineiformis Curtis, 1834 |
1 |
1 |
1 |
Conwentzia pineticola Enderlein, 1905 |
2 |
2 |
2 |
Parasemidalis fuscipennis (Reuter, 1894) |
3 |
3 |
3 |
Semidalis aleyrodiformis (Stephens, 1836) |
9 |
16 |
5 |
Sisyridae |
|||
Sisyra nigra (Retzius, 1783) |
35 |
230 |
5 |
Sisyra terminalis Curtis, 1854 |
5 |
7 |
2 |
Ascalaphidae |
|||
Libelloides macaronius (Scopoli, 1763) |
21 |
48 |
4 |
Osmylidae |
|||
Osmylus fulvicephalus (Scopoli, 1763) |
5 |
12 |
1 |
Hemerobiidae |
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Drepanepteryx algida (Erichson, 1851) |
1 |
1 |
1 |
Drepanepteryx phalaenoides (Linnaeus, 1758) |
12 |
12 |
3 |
Hemerobius atrifrons McLachlan, 1868 |
1 |
1 |
1 |
Hemerobius humulinus Linnaeus, 1758 |
59 |
72 |
11 |
Hemerobius lutescens Fabricius, 1793 |
3 |
3 |
2 |
Hemerobius marginatus Stephens, 1836 |
11 |
13 |
4 |
Hemerobius micans Olivier, 1793 |
7 |
10 |
3 |
Hemerobius nitidulus Fabricius, 1777 |
25 |
55 |
6 |
Hemerobius pini Leach, 1815 |
1 |
1 |
1 |
Hemerobius simulans Walker, 1853 |
5 |
7 |
2 |
Hemerobius stigma Stephens, 1836 |
9 |
9 |
3 |
Hemerobius striatus Nakahara, 1915 |
4 |
7 |
1 |
Megalomus hirtus (Linnaeus, 1761) |
19 |
23 |
3 |
Micromus angulatus (Stephens, 1836) |
94 |
131 |
10 |
Micromus lanosus (Zelený, 1962) |
1 |
1 |
1 |
Micromus paganus (Linnaeus, 1767) |
4 |
4 |
3 |
Micromus variegatus (Fabricius, 1793) |
33 |
51 |
5 |
Psectra diptera (Burmeister, 1839) |
11 |
16 |
4 |
Sympherobius elegans (Stephens, 1836) |
2 |
2 |
2 |
Sympherobius fuscescens (Wallengren, 1863) |
1 |
1 |
1 |
Sympherobius pygmaeus (Rambur, 1842) |
4 |
6 |
4 |
Wesmaelius concinnus (Stephens, 1836) |
9 |
10 |
3 |
Wesmaelius mortoni (McLachlan, 1899) |
2 |
2 |
1 |
Wesmaelius navasi (Andréu, 1911) |
1 |
1 |
1 |
Wesmaelius nervosus (Fabricius, 1793) |
8 |
10 |
2 |
Wesmaelius vaillanti (Navás, 1927) |
1 |
1 |
1 |
Chrysopidae |
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Apertochrysa flavifrons (Brauer, 1851) |
178 |
418 |
10 |
Apertochrysa prasina (Burmeister, 1839) |
836 |
5371 |
16 |
Apertochrysa ventralis (Curtis, 1834) |
149 |
223 |
8 |
Chrysopa abbreviata Curtis, 1834 |
76 |
135 |
9 |
Chrysopa commata Кis & Újhelyi, 1965 |
80 |
272 |
10 |
Chrysopa dasyptera McLachlan, 1872 |
18 |
27 |
2 |
Chrysopa dorsalis Burmeister, 1839 |
18 |
29 |
6 |
Chrysopa dubitans McLachlan, 1887 |
5 |
5 |
4 |
Chrysopa formosa Brauer, 1851 |
33 |
61 |
8 |
Chrysopa gibeauxi (Leraut, 1989) |
158 |
321 |
10 |
Chrysopa hummeli Tjeder, 1936 |
21 |
38 |
4 |
Chrysopa nigricostata Brauer, 1851 |
1 |
1 |
1 |
Chrysopa pallens (Rambur, 1838) |
21 |
28 |
9 |
Chrysopa perla (Linnaeus, 1758) |
394 |
1300 |
11 |
Chrysopa phyllochroma Wesmael, 1841 |
58 |
124 |
9 |
Chrysopa viridana Schneider, 1845 |
1 |
3 |
1 |
Chrysopa viridinervis Jakowleff, 1869 |
3 |
3 |
1 |
Chrysopa walkeri McLachlan, 1893 |
105 |
180 |
8 |
Chrysoperla carnea (Stephens, 1836) |
493 |
1863 |
16 |
Chrysoperla mutata (McLachlan, 1898) |
1 |
1 |
1 |
Chrysopidia ciliata (Wesmael, 1841) |
469 |
2110 |
10 |
Cunctochrysa albolineata (Killington, 1935) |
36 |
46 |
7 |
Cunctochrysa cosmia (Navás, 1918) |
29 |
48 |
8 |
Nineta alpicola (Kuwayama, 1956) |
493 |
2039 |
10 |
Nineta flava (Scopoli, 1763) |
135 |
298 |
12 |
Nineta vittata (Wesmael, 1841) |
94 |
146 |
8 |
Nothochrysa fulviceps (Stephens, 1836) |
52 |
124 |
8 |
Mantispidae |
|||
Mantispa aphavexelte U. Aspöck & H. Aspöck, 1994 (=Mantispa lobata Navás, 1912 sensu Zakharenko, 1987) Mantispa styriaca (Poda, 1761) |
7 22 |
52 57 |
4 7 |
Mantispilla perla (Pallas, 1772) |
3 |
3 |
3 |
Myrmeleontidae |
|||
Acanthaclisis occitanica (Villers, 1789) |
14 |
37 |
4 |
Creoleon plumbeus (Olivier, 1811) |
10 |
20 |
4 |
Deutoleon lineatus (Fabricius, 1798) |
21 |
76 |
4 |
Distoleon tetragrammicus (Fabricius, 1798) |
32 |
214 |
6 |
Euroleon nostras (Geoffroy, 1785) |
3 |
4 |
1 |
Lopezus fedtschenkoi (McLachlan, 1875) |
2 |
2 |
1 |
Macronemurus bilineatus Brauer, 1868 |
3 |
4 |
2 |
Megistopus flavicornis (Rossi, 1790) |
16 |
22 |
6 |
Mesonemurus guentheri Hölzel, 1970 |
2 |
7 |
1 |
Myrmecaelurus trigrammus (Pallas, 1771) |
45 |
262 |
7 |
Myrmecaelurus uralensis (Hölzel, 1969) |
6 |
8 |
2 |
Myrmeleon bore (Tjeder, 1941) |
438 |
111 |
7 |
Myrmeleon formicarius Linnaeus, 1767 |
60 |
115 |
11 |
Myrmeleon immanis Walker, 1853 |
19 |
62 |
4 |
Myrmeleon inconspicuus Rambur, 1842 |
25 |
55 |
4 |
Neuroleon nemausiensis (Borkhausen, 1791) |
5 |
8 |
2 |
Myrmecaelurus zigan (H. Aspöck et al. 1980) |
13 |
50 |
4 |
RAPHIDIOPTERA |
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Raphidiidae |
|||
Dichrostigma flavipes (Stein, 1863) |
85 |
118 |
8 |
Raphidia ophiopsis Linnaeus, 1758 |
6 |
29 |
3 |
Xanthostigma xanthostigma (Schummel, 1832) |
12 |
26 |
5 |
Inocelliidae |
|||
Inocellia crassicornis (Schummel, 1832) |
4 |
4 |
4 |
TOTAL |
4,826 |
17,373 |
Rank | Scientific Name |
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phylum | Arthropoda |
class | Insecta |
order | Neuroptera |
family | Ascalaphidae |
family | Coniopterygidae |
family | Chrysopidae |
family | Hemerobiidae |
family | Mantispidae |
family | Myrmeleontidae |
family | Osmylidae |
family | Sisyridae |
order | Raphidioptera |
family | Inocelliidae |
family | Raphidiidae |
The total number of occurrences in the dataset per month ranges from 0 in February and December to 1780 in July (Fig.
In the dataset, the main number of occurrences (3,577, 73.9%) was made in 2019–2022 (Fig.
CC-BY 4.0
Column label | Column description |
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occurrenceID | An identifier for the Occurrence (as opposed to a particular digital record of the occurrence). |
basisOfRecord | The specific nature of the data record: HumanObservation. |
scientificName | The full scientific name including the genus name and the lowest level oftaxonomic rank with the authority. |
kingdom | The full scientific name of the kingdom in which the taxon is classified. |
phylum | The full scientific name of the phylum or division in which the taxon is classified. |
class | The full scientific name of the class in which the taxon is classified. |
decimalLatitude | The geographic latitude of location in decimal degrees. |
decimalLongitude | The geographic longitude of location in decimal degrees. |
coordinateUncertaintyInMetres | The horizontal distance (in metres) from the given decimalLatitude and decimal-Longitude describing the smallest circle containing the whole of the Location. |
geodeticDatum | The ellipsoid, geodetic datum or spatial reference system (SRS) upon which the geographic coordinates given in decimalLatitude and decimalLongitude are based. |
country | The name of the country in which the Location occurs. Here - Russia. |
countryCode | The standard code for the country in which the Location occurs. Here - RU. |
stateProvince | The name of the administrative region within country in which the Location occurs. |
individualCount | The number of individuals represented present at the time of the Occurrence. |
eventDate | The date when material from the trap was collected or the range of dates during which the trap collected material. |
year | The integer year of the month on which the Event occurred. |
month | The integer month on which the Event occurred. |
day | The integer day of the month on which the Event occurred. |
locality | The original textual description of the place. |
georeferenceSources | A maps service used to georeference the location. |
recordedBy | A person, group or organisation responsible for recording the original Occurrence. |
identifiedBy | A list of names of people, who assigned the Taxon to the subject. |
taxonRank | The taxonomic rank of the most specific name in the dwc:scientificName. |
associatedReferences | A list of identifiers (publication, bibliographic reference, global unique identifier, URI) of literature associated with the dwc:Occurrence. |
occurrencesRemarks | Comments or notes about the dwc:Occurrence. |
habitat | A category or description of the habitat in which the dwc:Event occurred. |
samplingProtocol | The methods or protocols used during a dwc:Event. |
Seventy-eight observers contributed to the dataset, of which 42 (53.8%) contributed to more than one dataset record. Additionally, 18 (23.1%) observers contributed to more than ten occurrences in the dataset (Table
This research was funded by the Russian Science Foundation, grant number 22-14-00026.