Acta zoologica cracoviensia, 62(2) 2019 e-ISSN 2300-0163 Kraków, 2019 https://doi.org/10.3409/azc.62.02 http://www.isez.pan.krakow.pl/en/acta-zoologica.html

Wild bees of the proposed nature reserve “Skarpa Wiœlana” in Mêæmierz (Kazimierski Landscape Park). Part 1 – long-tongued bees Megachilidae and Apidae

Miko³aj BORAÑSKI , Waldemar CELARY , Dariusz TEPER

Received: 14 May 2019. Accepted: 10 December 2019. Article online: 12 December 2019. Issue online

Original article BORAÑSKI M., CELARY W., TEPER D. 2019. Wild bees of the proposed nature reserve “Skarpa Wiœlana” in Mêæmierz (Kazimierski Landscape Park). Part 1 – long-tongued bees Megachilidae and Apidae. Acta zool. cracov., 62(2): 21-39.

Abstract. This paper presents data on bees of the families Megachilidae and Apidae (Apoidea) of the proposed nature reserve “Skarpa Wiœlana” in Mêæmierz (Kazimierski Landscape Park). Distributional and phenological data are given. Thirty-one species of Megachilidae and forty-three species of Apidae were collected. For rare and very rare species (Anthidium oblongatum (ILLIGER, 1806); Heriades crenulatus NYLANDER, 1856; Hoplitis claviventris (THOMSON,1872); Hoplitis papaveris (LATREILLE, 1799); Megachile genalis MORAWITZ, 1880; Osmia cerinthidis MORAWITZ, 1876; Stelis odontopyga NOSKIEWICZ, 1926; Stelis ornatula (KLUG,1807); Epeoloides coecutiens (FABRICIUS, 1775); Eucera interrupta BAER, 1850; Nomada bifasciata OLIVIER, 1811; Nomada stigma FABRICIUS, 1804; Nomada zonata PANZER, 1798) this paper summarizes information about their distribution in 21st century in Poland, as well as data on their bionomics and their present status of threat in Europe.

Key words: checklist, species occurrence, Hoplitis papaveris, Nomada stigma, Osmia cerinthidis.

* Miko³aj BORAÑSKI, Dariusz TEPER, Research Institute of Horticulture, Apiculture Division, Kazimierska 2A, 24-100 Pu³awy, Poland. E-mail: [email protected]

Waldemar CELARY, The Jan Kochanowski University, Institute of Biology, Uniwersytecka 7, 25-406 Kielce, Poland.

I. INTRODUCTION concern: Thysanoptera – KUCHARCZYK (1997); Hemiptera – CMOLUCHOWA (1964), GOLAN et al. “Skarpa Wiœlana” is a fragment of steep slope (2001), £AGOWSKA &GOLAN (2002); Lepidop- situated on the edge of the valley of the Vistula tera – BUSZKO (1997); and some groups of Cole- River near Kazimierz Dolny (Fig. 2). In order to optera: Staphylinidae – STANIEC (2003), and protect the xerothermic grasslands and shrubs, Curculionidae – CMOLUCH (1971). Unfourtunately, habitats of rare animal species, and habitats that there is very little data about wild bees in the area could be repopulated with endangered plant spe- of Mêæmierz. Some information about the bees of cies, HARASIMIUK et al. (1987) proposed the this area can be found in the papers of creation of a floristic reserve in Mêæmierz. Knowl- RUSZKOWSKI et al. (1994, 2004) and WIŒNIOWSKI edge of the entomofauna of the proposed nature re- et al. (2018), however these publications concern serve “Skarpa Wiœlana” in Mêæmierz is fragmentary, only three species of bees, among which particu- however, what data there is allows it to be consid- larly noteworthy is Eucera nigrescens PÉREZ, ered rich and interesting. More extensive data 1879, a rare species in Poland (BANASZAK 2000a).

Ó Institute of Systematics and Evolution of Animals, PAS, Kraków, 2019 Open Access article distributed under the terms of the Creative Commons Attribution License (CC-BY) OPEN Ð ACCESS http://creativecommons.org/licences/by/4.0 22 M. BORAÑSKI et al.

Currently, there are no comprehensive studies of research period. Each collection time was about bees in this area. four hours. The Moericke traps were used from The aim of the present study was to compile a list April until the beginning of September in of the fauna of long-tongued bees inhabiting the 2013-2015. Moericke traps were placed on the proposed nature reserve “Skarpa Wiœlana”, in- ground’s surface. We used three, yellow plastic cluding their zoogeography, and phenology. bowls, 20 cm in diameter, 2/3rds of the way filled with a mixture of water (95%), ethylene glycol (4.8%), and a detergent (0.2%) added to decrease surface tension. Captured insects were removed II. STUDY AREA from the traps every 10 days. The collected bees The proposed nature reserve “Skarpa Wiœlana” are stored in the entomological collection of the in Mêæmierz (UTM - EB68) is situated on the out- Apiculture Division of Research Institute of Horti- skirts of the Be³¿yce Plain Mesoregion, in the area culture in Pu³awy. All specimens were collected of the Kazimierski Landscape Park, about 4 km by M. BORAÑSKI. south of Kazimierz Dolny (Fig. 1). The locality of Classification into families and genera and their Mêæmierz is part of the Nature 2000 – The Lesser systematic arrangement has been presented ac- Poland Gorge of the Vistula (PLH 060045). The cording to SCHEUCHL &WILLNER (2016). The total area of “Skarpa Wiœlana” is 9.27 ha. In recent following publications were used to identify the years, protective measures in counteracting plant species of bees: BANASZAK &ROMASENKO succession and the fragmentation of xerothermic (1998); CELARY (1995a); KASPAREK (2015); communities has been carried out in the area of the PAWLIKOWSKI (1996); SCHEUCHL (2000), (2006); planned nature reserve “Skarpa Wiœlana” SMIT (2018); WARNCKE (1992). The species of (PAW£OWSKI 2009). the Bombus lucorum-complex (BOSSERT 2015) The flowery grassland plants can be assigned to are not distinguishable by morphological features xerothermic grasslands of the Festuco-Brometea and additionally, B. lucorum and B. terrestris are class 6210 (Inuletum ensifoliae alliance and easily confused (WOLF et al. 2010), therefore data Origano-Brachypodietum alliance) and Juniperus on the occurrence of bumblebees of the subgenus communis formations 5130 (JAROSZ-SOSIK 2013). Bombus LATREILLE, 1802 = Terrestribombus They grow on strongly eroded rendzinas formed of VOGT, 1911 are summarized. Honey bees (Apis marls on slopes of southern, south-western and mellifera LINNAEUS, 1758) were observed at all western exposure, rarely on fragments of plateau. times during the study but this species was not in- The xerothermic phytocoenoses have the character cluded because of its anthropogenic origin. The of a loose grassland with a mosaic-like shrub layer zoogeographical partitioning of the regions of Po- as a permanent element. The following species oc- land follows the one used in the Catalogue of Pol- cur here: Juniperus communis L., Prunus spinosa ish Fauna (BURAKOWSKI et al. 1978). IUCN L., Rosa canina L., and Viburnum opulus L. In the categories of threat are given after NIETO et al. layer of herbceous plants, the dominant species is (2014). Status of threat in particular European Inula ensifolia L. or Brachypodium pinnatum (L.) countries is given after available regional red lists P. BEAUV. (Fig. 3) and the following appear per- or red books of threatened species. manently, although less abundantly: Achillea seid- CR – Critically Endangered – species, whose lii J.PRESL & C.PRESL, Adonis vernalis L., numbers have decreased to a critical level, which Anemone sylvestris L., Anthericum ramosum L., persists at single localities, or whose rate of de- Anthyllis vulneraria L., Aster amellus L., Cam- cline is within the range of values established by panula sibirica L., Euphorbia cyparissias L., Me- the IUCN. The survival of species belonging to dicago falcata L., Origanum vulgare L., Salvia this category is rather unlikely without active pro- verticillata L., Salvia pratensis L., and Teucrium tection focused, among others, on elimination of chamaedrys L. (KUCHARCZYK 2000). causes of extinction. EN – Endangered – species facing a very high risk of extinction because of small populations, a III. MATERIAL AND METHODS fragmented, insular range, and/or a quick rate of Field research was conducted over the course of population decline. six growing seasons, from 2010-2015. Two meth- VU – Vulnerable – species facing a high risk of ods were used to collect bees: yellow pan traps extinction due to continuing population decline (Moericke traps) and hand-netting (by searching and habitat loss or over-exploitation; however, the on flowers and at the bees’ favourite nesting sites). observed or prognosticated rate of their decline is Hand-netting was used periodically every slower than in the case of taxa assigned to the 10-14 days, throughout the duration of the field higher categories of threat. Long-tongued bees in proposed nature reserve 23

Fig.1. Location of the study site “Skarpa Wiœlana” in the Kazimierski Landscape Park (www.openstreetmap.com and MapaUTM).

Fig. 2. Panorama of “Skarpa Wiœlana” in Mêæmierz near Fig. 3. Xerothermic grasslands of the Inuletum ensifoliae Kazimierz Dolny – slopes on the edge of the valley of the alliance situated in Mêæmierz. Vistula River.

NT – Near Threatened – species that maybe con- sidered threatened with extinction in the near fu- IV. RESULTS AND DISCUSSION ture, although they don’t currently qualify for the threatened status. LC – Least Concern – species that have been List of Species been evaluated and do not qualify for any other category. Family: Megachilidae DD – Data Deficient – species where there is in- adequate information to make a direct, or indirect, Genus: Anthidiellum COCKERELL, 1904 assessment of their risk of extinction based on their distribution and/or population status. Anthidiellum strigatum (PANZER, 1805) Abbreviations: 12 Jun 2011 – 1F; 27 Aug 2011 – 1M. NP – National Park (e.g. Wolin NP = Wolin Na- tional Park) Genus: Anthidium FABRICIUS, 1804 LP – Landscape Park (e.g. Cisów-Or³owiny LP = Cisów-Or³owiny Landscape Park) Anthidium manicatum (LINNAEUS,1758) F–female,M–male,W–worker 02 Jul 2013 – 1F; 22 Jul 2015 – 2MM. 24 M. BORAÑSKI et al.

Anthidium oblongatum (ILLIGER, 1806) Megachile circumcincta (KIRBY, 1802) 17 Jun 2012 – 1F; 02 Jul 2013 – 1M; 01 Jul 2014 – 1M. 07 Jul 2015 – 1F.

Anthidium punctatum LATREILLE, 1809 Megachile genalis MORAWITZ, 1880 Erigeron annuus (L.) PERS., 12 Jun 2011 – 2FF,1M; Jun 2013 – 1F. 03 Jun 2012 – 3MM; 17 Jun 2012 – 3FF,1M; 02 Jul 2012 – 1M; Salvia pratensis, 29 May 2013 – 1F, Megachile ligniseca (KIRBY, 1802) 1M. 21 Aug 2010 – 1F. Megachile maritima (KIRBY, 1802) Genus: Chelostoma LATREILLE, 1809 Anthericum ramosum, 12 Jul 2011 – 1F. Chelostoma florisomne (LINNAEUS,1758) 08 May 2010 – 3FF,1M; 22 May 2011 – 1F, 1M; Megachile versicolor SMITH, 1844 Ranunculus L., 22 May 2011 – 3FF, 3MM; Hiera- 03 Jul 2010 – 1F; 21 Jul 2010 – 2FF; Jun 2013 – 1M; cium L., 22 May 2011 – 1M; 03 Jun 2012 – 1F; 05 Sep 2013 – 1F; 16 Sep 2015 – 1F. Ranunculus, 17 Jun 2012 – 1F. Genus: Osmia PANZER, 1806 Chelostoma rapunculi (LEPELETIER, 1841) 03 Jul 2010 – 1M; Campanula L., 17 Jun 2012 – Osmia aurulenta (PANZER,1799) 3MM. 08 May 2010 – 5FF, 7MM; 17 May 2010 – 1M; Taraxacum officinale (L.) WEBER ex F.H.WIGG., Genus: Coelioxys LATREILLE, 1809 30 Apr 2011 – 4FF, 7MM; 30 Apr 2011 – 2FF, 5MM; Lotus corniculatus L., 22 May 2011 – 5FF; Coelioxys mandibularis NYLANDER, 1848 Salvia pratensis, 22 May 2011 – 1F, 1M; 22 May 27 Aug 2011 – 1F. 2011 – 2MM; Convolvulus arvensis L., 12 Jun 2011 – 2FF; Hieracium,12 Jun 2011 – 1F; 21 Apr Coelioxys quadridentata (LINNAEUS, 1758) 2012 – 3MM; 01 May 2012 – 1M; 20 May 2012 – Ranunculus, 22 May 2011 – 1M. 8MM; 03 Jun 2012 – 1M; 17 Jun 2012 – 2FF; 06 May 2013 – 3MM; 07 May 2013 – 2MM; 15 Jul 2013 – 1F; 16 Jul 2014 – 2FF; 11 May 2015 – Genus: Heriades SPINOLA, 1808 7MM; 28 May 2015 – 2MM.

Heriades crenulatus NYLANDER, 1856 Osmia bicolor (SCHRANK,1781) 17 Jun 2012 – 1F. 17 Apr 2010 – 1F; 08 May 2010 – 3FF; 17 May 2010 – 2FF; Taraxacum officinale, 30 Apr 2011 – 3FF; Heriades truncorum (LINNAEUS,1758) Salvia pratensis, 11 May 2011 – 1F; Convolvulus 27 Aug 2011 – 1F; 12 Aug 2013 – 1F. arvensis, 12 Jun 2011 – 1F; 21 Apr 2012 – 4FF, 3MM; 20 May 2012 – 2FF; 06 May 2013 – 9FF, Genus: Hoplitis KLUG, 1807 3MM; Hieracium, 29 May 2013 – 2FF; 29 May 2013 – 2FF; 08 Jun 2013 – 1F; 01 Jul 2013 – 1F; Hoplitis adunca (PANZER, 1798) 19 Apr 2014 – 1F; Viburnum opulus, 20 May 2014 Echium vulgare L., 12 Jun 2011 – 1F; Cichorium – 1F; 20 May 2014 – 1F; 16 Jul 2014 – 1F; 11 May intybus L., 12 Jul 2011 – 1F; 30 Jun 2012 – 2FF, 2015 – 2FF, 4MM; 28 May 2015 – 1F. 1M;20May2014–1M. Osmia bicornis (LINNAEUS,1758) Hoplitis claviventris (THOMSON,1872) 21 Apr 2012 – 1M; 06 May 2013 – 1M; 11 May 08 May 2010 – 1M; 12 Jun 2011 – 1F; 17 Jun 2015 – 2MM. 2012 – 1F; 02 Jul 2015 – 1F. Osmia caerulescens (LINNAEUS,1758) Hoplitis leucomelana (KIRBY,1802) 08 May 2010 – 1F. 12 Jun 2011 – 2MM; 15 Jul 2013 – 1F. Osmia cerinthidis MORAWITZ, 1876 Hoplitis papaveris (LATREILLE, 1799) Cerinthe minor L., 17 Jun 2012 – 1F. 03 Jun 2012 – 1M. Osmia leaiana (KIRBY,1802) Genus: Megachile LATREILLE, 1802 Hieracium, 22 May 2011 – 1F.

Megachile centuncularis (LINNAEUS, 1758) Osmia niveata (FABRICIUS, 1804) 27 Aug 2011 – 2FF; 30 Jun 2012 – 1F; Jun 2013 – 1F. 06 May 2013 – 1M. Long-tongued bees in proposed nature reserve 25

Osmia spinulosa (KIRBY,1802) Bombus bohemicus SEIDL, 1838 01 Aug 2010 – 3FF; 21 Aug 2010 – 1F; Hieracium, Inula ensifolia, 12 Jul 2011 – 1M; 24 Jul 2011 – 1M; 12 Jun 2011 – 1F, 1M; Erigeron annuus,12Jun 11 May 2015 – 1F. 2011 – 3MM; 12 Jun 2011 – 7MM; Hieracium, 12 Jul 2011 – 2FF, 1M; 24 Jul 2011 – 1F; 12 Aug Bombus campestris (PANZER, 1801) 2011 – 3MM; Inula ensifolia, 13 Aug 2011 – 5FF; 24 Jul 2011 – 1M. 27 Aug 2011 – 4FF; Ranunculus, 03 Jun 2012 – 2MM; 17 Jun 2012 – 1M; 30 Jun 2012 – 3FF, Bombus hortorum (LINNAEUS, 1761) 9MM; 03 Jun 2013 – 1F, 1M; 08 Jun 2013 – 1M; 27 Jun 2013 – 2FF, 19MM; 01 Jul 2013 – 2FF, 12 Jun 2011 – 2FF, 2MM, 4WW; 31 Jul 2014 – 1W. 6MM; 15 Jul 2013 – 7MM; 24 Jul 2013 – 1F, Bombus hypnorum (LINNAEUS, 1758) 5MM; 02 Aug 2013 – 1F, 2MM; 28 Aug 2013 – 3FF, 1M; 05 Sep 2013 – 3FF, 1M; Inula ensifolia, 20 Jun 2010 – 1F, 2MM, 12 Jun 2011 – 3WW; 15 Jul 2014 – 3FF; 15 Jul 2014 – 4FF; Inula ensifolia, 22 Jul 2014 – 4FF, 1M; 22 Jul 2014 – 6FF, 9MM; Bombus lapidarius (LINNAEUS, 1758) 12 Aug 2014 – 5FF; 02 Jul 2015 – 4FF, 19MM; 01 May 2010 – 1W; 03 Jul 2010 – 3WW; 01 Aug 20 Jul 2015 – 4FF, 1M. 2010 – 1M; Euphorbia cyparissias, 30 Apr 2010 – 1F; 30 Apr 2011 – 1F; Lotus corniculatus,22May Genus: Stelis PANZER, 1806 2011 – 1W; Melampyrum arvense L., 12 Jun 2011 – 1W; 12 Jul 2011 – 1F, 1M, 1W; Origanum vul- Stelis odontopyga NOSKIEWICZ, 1926 gare,12Jul2011–5MM,1W;Centaurea sca- biosa L.,12Jul2011–3MM;12Jul2011–9MM, Inula ensifolia, 13 Aug 2011 – 1F, 1M; 30 Jun 1W; 18 Aug 2011 – 1M, 1W; 01 Jun 2013 – 1W; 2012 – 1F; 02 Aug 2013 – 1F; 22 Jul 2014 – 1F, 1M. 24 Jul 2013 – 3W; 02 Aug 2013 – 2W; 28 Aug 2013 – 1W.

Stelis ornatula (KLUG,1807) Bombus muscorum (LINNAEUS, 1758) Jul2013–1M. 03 Jul 2010 – 1W.

Bombus pascuorum (SCOPOLI, 1763) Genus: Trachusa PANZER, 1804 08 May 2010 – 2WW; 06 Jun 2010 – 1F; 03 Jul Trachusa byssina (PANZER, 1798) 2010 – 1W; 20 Jul 2010 – 1W; 01 Aug 2010 – 1F, 1M, 1W; 21 Aug 2010 – 1F, 1W; Salvia pratensis, 17 Jun 2012 – 1F; 02 Jul 2015 – 2FF. 22 May 2011 – 1W; Melampyrum arvense,12Jun 2011 – 3WW; 12 Jul 2011 – 2WW; Cichorium in- Family: Apidae tybus, 24 Jul 2011 – 2WW; Hieracium, 24 Jul 2011 – 1M; 24 Jul 2011 – 4WW; 01 Jun 2013 – 1W; Tri- Genus: Anthophora LATREILLE, 1803 folium pratense L., 31 Jul 2014 – 1W.

Anthophora aestivalis (PANZER, 1801) Bombus pratorum (LINNAEUS, 1761) 06 Jun 2010 – 2MM; Salvia pratensis,22May Origanum vulgare, 12 Jul 2011 – 1M; 17 Apr 2011 – 1M. 2012 – 1W. Bombus ruderarius (MÜLLER, 1776) Anthophora plumipes (PALLAS, 1772) 01 Aug 2010 – 2MM, 1W; Salvia pratensis, 17 Apr 2010 – 1M; 30 Apr 2011 – 2FF; 21 Apr 22 May 2011 – 1W; Melampyrum arvense,12Jun 2012 – 1F, 1M. 2011 – 4WW; Hieracium,12Jul2011–1W;Inula ensifolia,12Jul2011–1M;Hieracium,24Jul Genus: Bombus LATREILLE, 1802 2011 – 1F; 06 May 2013 – 1F; Trifolium pratense, 31 Jul 2014 – 1M; 28 May 2015 – 1W. Bombus LATREILLE, 1802 = Terrestribombus Bombus rupestris (FABRICIUS, 1793) VOGT, 1911 (subgenus) 06 Jun 2010 – 1W; 03 Jul 2010 – 3W; Salvia Origanum vulgare,24Jul2011–2MM pratensis, 22 May 2011 – 1W; Convolvulus arven- sis, 12 Jun 2011 – 2WW; Hieracium, 12 Jul 2011 – Bombus sylvarum (LINNAEUS, 1761) 1M; Origanum vulgare,12Jul2011–9MM; 08 May 2010 – 1F; Lotus corniculatus,22May 12 Jul 2011 – 2MM, 1W; Origanum vulgare, 2011 – 1W; Origanum vulgare,12Jul2011–2WW; 24 Jul 2011 – 3MM; 24 Jul 2011 – 5MM, 1W; 24 Jul 2011 – 1W; 18 Aug 2011 – 1W; 27 Aug 18 Aug 2011 – 1F. 2011 – 1F, 1W. 26 M. BORAÑSKI et al.

Bombus sylvestris (LEPELETIER, 1832) Nomada flava PANZER, 1798 30 Apr 2011 – 1F. 17 Apr 2010 – 1M; 17 MFy 2010 – 1F; 06 Jun 2010 – 1F; Euphorbia cyparissias, 30 Apr 2011 – 1F; Genus: Ceratina LATREILLE, 1802 21 Apr 2012 – 3MM; 11 May 2015 – 1M.

Ceratina cyanea (KIRBY, 1802) Nomada flavoguttata (KIRBY, 1802) 08 May 2010 – 2MM; 22 May 2011 – 1F; 12 Jul 17 May 2010 – 1F; 30 Apr 2011 – 1M; 19 Apr 2011 – 1M; 21 Apr 2012 – 1M; 20 May 2012 – 2FF; 2014 – 1F; 11 May 2015 – 1F, 3MM; 28 May 2015 17 Jun 2012 – 1M. –1M.

Nomada flavopicta (KIRBY, 1802) Genus: Epeoloides GIRAUD, 1863 Hieracium L., 12 Jul 2011 – 1F. Epeoloides coecutiens (FABRICIUS, 1775) 18 Aug 2011 – 1F; 10 Jul 2018 – 1F. Nomada fucata PANZER, 1798 01 May 2012 – 2FF; 30 Jun 2012 – 1F. Genus: Epeolus LATREILLE, 1802 Nomada fulvicornis FABRICIUS, 1793 Epeolus variegatus (LINNAEUS, 1758) 30 Apr 2011 – 2FF; 21 Apr 2012 – 2MM. 12 Jul 2014 – 1F. Nomada goodeniana (KIRBY, 1802) Genus: Eucera SCOPOLI, 1770 08 May 2010 – 2FF; 06 Jun 2010 – 2FF; 30 Apr 2011 – 1F. Eucera interrupta BAER, 1850 Nomada integra BRULLÉ, 1832 20 May 2012 – 1M. 20 May 2012 – 1F; 06 Jun 2010 – 1F. Eucera longicornis (LINNAEUS, 1758) Nomada lathburiana (KIRBY, 1802) Salvia pratensis,22May2011–4MM;Salvia 30 Apr 2011 – 2MM; 07 May 2013 – 1M; 19 Apr pratensis,12Jun2011–1M;20May2012–1M; 2014 – 1M. Hieracium, 29 May 2013 – 1M. Nomada marshamella (KIRBY, 1802) Genus: Melecta LATREILLE,1802 08 May 2010 – 1F.

Melecta luctuosa (SCOPOLI, 1770) Nomada moeschleri ALFKEN, 1913 30 Apr 2011 – 1M; 20 May 2012 – 1F. 21 Apr 2012 – 1M; 01 May 2012 – 1F; 11 May 2014 – 1M; 28 May 2015 – 1M. Genus: Nomada SCOPOLI, 1770 Nomada panzer LEPELETIER, 1841 Nomada armata HERRICH-SCHÄFFER, 1839 21 Apr 2012 – 1M; 06 May 2013 – 1F,1M; 30 Jun 2012 – 1F. 07 May 2013 – 1F; 11 May 2015 – 1F,1M.

Nomada bifasciata OLIVIER, 1811 Nomada ruficornis (LINNAEUS, 1758) 17 Apr 2010 – 5FF, 4MM; 8 May 2010 – 14FF; 30 Apr 2011 – 1M; Tusisilago farfara L.,21Apr Taraxacum officinale, 30 Apr 2011 – 1F; 30 Apr 2012 – 1M. 2011 – 3FF, 1M; 22 May 2011 – 2FF; 21 Apr 2012 – 5FF, 6MM; 01 May 2012 – 12FF; 06 May Nomada rufipes FABRICIUS, 1793 2013 – 2FF, 3MM; Taraxacum officinale, 07 May 2013 – 3FF; 19 Apr 2014 – 1F; 11 May 2015 – 1M. 21 Aug 2010 – 1M.

Nomada fabriciana (LINNAEUS, 1767) Nomada signata JURINE, 1807 17 May 2010 – 1M. 30 Apr 2011 – 1M; 11 Apr 2015 – 1M.

Nomada ferruginata (LINNAEUS, 1767) Nomada stigma FABRICIUS, 1804 08 May 2010 – 1F; 12 Jun 2011 – 1F; 21 Apr 12 Jun 2011 – 1F. 2012 – 5FF, 3MM; 01 May 2012 – 1F; 06 May 2013 – 1F; 20 May 2014 – 1F; 11 May 2015 – 1F; Nomada zonata PANZER,1798 02 Jul 2015 – 1F. 30 Apr 2011 – 1M. Long-tongued bees in proposed nature reserve 27

Genus: Tetralonia SPINOLA, 1838 LP: Szczecno; DB53 Chêciny-Kielce LP: Miedzian- ka; Nadnidzie LP: DA78 Skorocice, DA69 east Tetralonia malvae (ROSSI, 1790) Piñczów and W³ochy DA79 near Grochowiska – 03 Jul 2010 – 4MM; 12 Jun 2011 – 1M; 12 Jul B¥K-BADOWSKA (2012a); EB01 Cisów-Or³owiny 2011 – 2MM; 30 Jun 2012 – 2FF, 8MM; 16 Jul 2014 – 1M. LP: Rembów – BIOTROWSKI-BADOWSKA (2014), Œwiêtokrzyskie Mts: DB94 Œwiêtokrzyski PN: Tetralonia salicariae (LEPELETIER, 1841) Góra Miejska – B¥K-BADOWSKA (2012a), 22 Jul 2015 – 1M. Lublin Upland: FB59 Polesie NP: Kulczyn – WIŒNIOWSKI &PIOTROWSKI (2013).

V. REVIEW OF PARTICULARLY The present status of threat in Europe is un- NOTEWORTHY SPECIES known. H. crenulatus is listed on the European Red List of Bees as least concern (NIETO et al. Megachilidae 2014), but due to the species’ wide distribution and solitary behaviour, it is presumed to have a large Heriades crenulatus population (LHOMME 2014a). The species is listed This Subponto-Mediterranean species inhabits as least concern on the National Red Lists of the North Africa (from Morocco to Libya) and in Netherlands (PEETERS &REEMER 2003) and Ger- Eurasia, from Portugal across Southern Europe, many (WESTRICH et al. 2011). In Poland, until the Asia Minor and the Caucasus to Kazakhstan; north 21st century, this species was known from only six to Brandenburg, northern Poland, Belarus, central records in the Pomeranian Lakeland, Wielko- Ukraine and Rostov; south to Sicily, Malta and Crete, polska-Kujawy Lowland, Mazovian Lowland, and in Asia to northwestern Iran (SCHEUCHL & Ma³opolska Upland, and Lublin Upland (CELARY WILLNER 2016). H. crenulatus appears in the sec- &WIŒNIOWSKI 2011). In recent years, a dynamic ond half of June and flies till the end of August spreading of this Subponto-Mediterranean species (CELARY &WIŒNIOWSKI 2011). The species is has been observed all over the country, which may oligolectic on Asteraceae (BANASZAK & be related to climate change. Dynamic changes in ROMASENKO 1998). The females nest in pre- species dispersion in relation to climatic changes existing cavities in wooden material, in the galler- have been documented in bumblebees (KERR et al. ies of wood-boring insects and in hollow stems 2015, RASMONT et al. 2015) and solitary bees (SCHEUCHL &WILLNER 2016). Nests are parasi- (HOFMANN et al. 2018). tized by a cuckoo bee Stelis breviuscula Hoplitis claviventris NYLANDER, 1848, (KASPAREK 2015). Information on the Polish localities (with UTM This Palaearctic species occurs from Portugal coordinates) until 2010 are given in CELARY & through Europe, Asia Minor, Caucasus and Siberia WIŒNIOWSKI (2011), however two records of this to lrkutsk; north to Wales and northern England, in species before 2010 were omitted by the authors: Norway to 62°N, in Sweden to the Arctic Circle, in Masurian Lakeland: FF20; FF30-31 near Finland to 65.5°N, in Russia to Karelia and Kirov; Suwa³ki –KRZYSZTOFIAK &KRZYSZTOFIAK south to Sicily, and in northern Greece and south- (2002) and Wielkopolska-Kujawy Lowland: eastern Turkey (SCHEUCHL &WILLNER 2016). XU96 Lubostroñ –BANASZAK (2008b). After this Adults of H. claviventris fly from the second half time H. crenulatus was recorded in various regions of May until mid-August (CELARY & such as: Baltic Coast: VV67 Wolin NP: Wapnica WIŒNIOWSKI 2007). The females visit blooming –BANASZAK (2010b), Pomeranian Lakeland: plants of the families Asteraceae, Boraginaceae, Cedynia LP: VU45-47 near Cedynia; VU47,57 Cistaceae, Crassulaceae, Fabaceae, Lamiaceae, near Zatoñ Dolna – BANASZAK &TWERD (2018), Hypericaceae, and Rosaceae, but with preference Masurian Lakeland: EE36 Ta³ty –BANASZAK for Lotus corniculatus (SCHEUCHL &WILLNER (2010a), Wielkopolska-Kujawy Lowland: XU20-21, 2016). Nesting usually occurs in hollow twigs (e.g. XU30-31 Poznañ –BANASZAK-CIBICKA & Rosa spp. and Rubus spp.) and stems (e.g. Senecio BANASZAK (2011); CD32 Piotrków Kujawski, spp.), less often in the ground or in holes in dead CD22 Gop³o Millennium LP: Mietlica – BANASZAK wood or root plates (FALK &LEWINGTON 2015). &SOBIERAJ-BETLIÑSKA (2016); XU62 Lednica Nests are parasitized by cuckoo bees Stelis minuta LP: Dziekanowice – BANASZAK &RATYÑSKA LEPELETIER &SERVILLE, 1825 and Stelis orna- (2016); CD05 Janikowo – TWERD &BANASZAK tula (KASPAREK 2015). Information on the Polish (2017); WU73 ecological site „Jaskó³cza Skarpa” localities until 2006 are given in CELARY & near Sieraków – WENDZONKA (2011), Bia³owie¿a WIŒNIOWSKI (2007), after this time H. claviven- Forest: FD94 Bia³owie¿a NP: section 314Di of the tris was recorded in various regions: Baltic Coast: strictly protected part – BANASZAK &JAROSZEWICZ CF56 KuŸnica CF56–BANASZAK (2016), Pom- (2009), Ma³opolska Upland: DB82 Cisów-Or³owiny eranian Lakeland: XV67, XV76 Bory Tuchol- 28 M. BORAÑSKI et al. skie NP – KRIGER &CIERZNIAK (2006); Ce- and southern Russia, as well as in Asia Minor, dynia LP: VU45-47 near Cedynia; VU47,57 Caucasus and Central Asia to Buryatia; north to near Zatoñ Dolna – BANASZAK &TWERD (2018), northern Germany, northern Poland, Kirov, and Perm; Masurian Lakeland: EE24 Masurian LP: Kru- south to Sicily, Peloponnese, Israel, and Jordan tyñ; EE33 Krzy¿e –BANASZAK (2010a); EF00 (SCHEUCHL &WILLNER 2016). Adults appear in S¹toczno –BANASZAK &SZEFER (2013), the first half of June and can be observed until Wielkopolska-Kujawy Lowland: WU65 Krzy¿ mid-August (CELARY &WIŒNIOWSKI 2007). Wielkopolski – BANASZAK (2010c); XU61 The females visit blooming plants of the families Pos³onkowe Hill – BANASZAK &RATYÑSKA (2016); Asteraceae, Campanulaceae, Caryophyllaceae, DB95 Bielawy – TWERD &BANASZAK (2017), Cistaceae, Convolvulaceae, Papaveraceae Mazovian Lowland: DC59 Kampinos NP: Bromierzyk, (SCHEUCHL &WILLNER 2016). They nest in pre- CD93 Uniejewo – BANASZAK &KOWALCZYK existing cavities in the soil, seldomly excavating (2007); DC36 Bolimów LP: Borowiny and their own tunnels. Thenest consists of one cell, some- „Polana Siwica” nature reserve – KOWALCZYK & times two cells, with all walls constructed of bits of KURZAC (2009), Bia³owie¿a Forest: FD94 petals (BANASZAK &ROMASENKO 1998). The fe- Bia³owie¿a NP section 314Di of the strictly pro- males usually cut fragments of petals of Papaver tected part – BANASZAK &JAROSZEWICZ (2009), rhoeas L., Cyanus segetum HILL, Malva moschata L., Ma³opolska Upland: CC83, CC92, CC94, DC03 Helianthemum spp. and Genista tinctoria L. £ódŸ, DC13 Ga³ków; CC94 £ódŸ-£agiewniki forest, (WESTRICH 1990). Nests are parasitized by DB17 Rêczno, CB48 Szynkielów – BANASZAK & cuckoo bees: Coelioxys brevis EVERSMANN, 1852; KOWALCZYK (2007); CC50 nature and landscape Coelioxys elongata LEPELETIER, 1841; Coelioxys Complex “Góry Wapienne” – KOWALCZYK et al. inermis (KIRBY, 1802); Coelioxys mandibularis (2009a); DC04 Wzniesienia £ódzkie LP: Boginia and Stelis phaeoptera (KIRBY, 1802) (SCHEUCHL –KOWALCZYK et al. (2009b); DB82 Cisów-Or³owia- &WILLNER 2016). ny LP: near Borków; Chêciny-Kielce LP: DB53 Information on Polish localities before 2006 are Miedzianka, DB63 near Jaworzynia, DB52 Jedlnica, given in CELARY &WIŒNIOWSKI (2007), after this DB62 near Chêciny; Nadnidziañski LP: DA69 time, H. papaveris was recorded in two regions: Piñczów Mountains near Piñczów, east Piñczów Wielkopolska-Kujawy Lowland: CD32 Piotrków and W³ochy DA79 near Grochowiska and near Kujawski – BANASZAK &SOBIERAJ-BETLIÑSKA “Grabowiec” nature reserve – B¥K-BADOWSKA (2016); Lednica LP: XU61 Pos³onkowe Hill, XU62 2012a; DB75 Suchedniów-Oblêgorek LP: Wilczy Dziekanowice – BANASZAK &RATYÑSKA (2016); Bór forest district, division 100 and Bartków forest CD14 Inowroc³aw, CD05 Janikowo, DB95 Bie- district, division 77 – B¥K-BADOWSKA J. (2012b), lawy–TWERD &BANASZAK (2017); XU99 near Mts: Œwiêtokrzyskie EB03 Œwiêtokrzyski PN: near Bydgoszcz – SOBIERAJ-BETLIÑSKA &BANASZAK Trzcianka – B¥K-BADOWSKA (2012a), Eastern (2018); WU73 ecological site „Jaskó³cza Skarpa” Sudetes Mts: YR14 “Góra Gipsowa” steppe reserve near Sieraków – WENDZONKA (2011) and –BANASZAK et al. (2013), BANASZAK et al. (2017). Ma³opolska Upland: DB25 Przedbórz LP: “Mu- This species is listed on the European Red List of rawy Dobromierskie” nature reserve – SOSZYÑSKI Bees as least concern (NIETO et al. 2014), due to et al. (2008); DC04 Wzniesienia £ódzkie LP: the species’ wide distribution and solitary behav- Plichtów – KOWALCZYK et al. (2009b); Chêci- iour, it is presumed to have a large population ny-Kielce LP: DB53 Miedzianka, DB62 near (LHOMME 2014b). The species is listed as least Chêciny and near Korzecko – B¥K-BADOWSKA concern in the National Red Lists of the Nether- (2012a). lands (PEETERS &REEMER 2003) and Germany The present status of threat in Europe is un- (WESTRICH et al. 2011) and it is very rare in Portu- known. According to the IUNC Red List (Europe), gal (BALDOCK et al. 2018). In Poland, until the their category is least concern (NIETO et al. 2014), 21st century, this species was known from 11 rec- but H. papaveris is probably extinct in the Czech ords in the Baltic Coast, Pomeranian Lakeland, Republic (STRAKA &BOGUSCH 2017), Switzer- Masurian Lakeland, Wielkopolska-Kujawy Low- land (AMIET 1994), and in the Netherlands land, Lublin Upland, Roztocze, and Western Be- (PEETERS &REEMER 2003). In Germany it is criti- skidy Mts (CELARY &WIŒNIOWSKI 2007). In cally endangered (WESTRICH et al. 2011). In the recent years, a dynamic spreading of this Palaearc- “Red List of Threatened Animals in Poland”, it is tic species has been observed all over the country, listed as vulnerable (G£OWACIÑSKI 2002). This is which may be related to climate change. the first record of this species in the Lublin Upland. Hoplitis papaveris Megachile genalis This rare bee species occurs from Portugal This Palaearctic species occurs from Spain through Southern and Central Europe, Ukraine through Europe, Asia Minor, the Caucasus, Sibe- Long-tongued bees in proposed nature reserve 29 ria and Central Asia to the Pacific coast in the Far Nadnidzie LP: DA78 near Chotel Czerwony East; north to the Baltics, in Russia to Kirov and „Przêœlin” nature reserve – B¥K-BADOWSKA (2012c); Perm; south to Lazio, Croatia, southern Romania, DB82 Cisów-Or³owiny LP: S³opiec Szlachecki – southern Turkey and Northern Caucasus B¥K-BADOWSKA (2014), Œwiêtokrzyskie Mts: (SCHEUCHL &WILLNER 2016). This is an oligo- EB03 Œwiêtokrzyski PN: near Nowa S³upia – lectic species on Asteraceae (SCHEUCHL 2006). B¥K-BADOWSKA (2012a), Pieniny Mts: DV57, Females usualy build nests in the stems of Allium 67 Pieniny NP: Dunajec and Poprad valleys – cepa L., Angelica sylvestris L., Carduus acanthoides L., DYLEWSKA &KOZIK (2007). Carduus crispus L., Circaea spp., Cirsium palustre This species is listed on the European Red List of (L.) Coss. ex Scop., Conium maculatum L., Dahlia Bees as least concern (NIETO et al. 2014), but it is pinnata CAV., Echinops sphaerocephalus L. and critically endangered in the Czech Republic (STRAKA Heracleum spp. (RUHNKE 2000). They fly from &BOGUSCH 2017) and Germany (WESTRICH et al. June till the begining of September (BANASZAK & 2011). In Poland (G£OWACIÑSKI 2002) and ROMASENKO 1998). Information on the Polish lo- Slovenia (ANONYMOUS 2002), it is listed as vul- calities (with UTM coordinates) until 2010 are nerable. given in CELARY &WIŒNIOWSKI (2011), after this time M. genalis was recorded in Wielkopolska- Anthidium oblongatum Kujawy Lowland: XU98 Ma³e Rudy “Ostrów” near Anthidium oblongatum is listed in literature as Szubin – BANASZAK (2010c); CD14 Inowroc³aw, a Subpontic-Mediterranean species (CELARY 1998, CD05 Janikowo – TWERD &BANASZAK (2017). BANASZAK 2000a, BANASZAK 2003), but consid- The present status of threat in Europe is un- ering the current distribution of this species in the known. On the IUNC Red List (Europe) they are world (SCHEUCHL &WILLNER 2016), it seems listed in the category DD (data deficient) (NIETO et al. better to qualify this species as a South-West Pa- 2014). The species is listed in the National Red laearctic one. A. oblongatum appears in the second Lists as regionally extinct in the Czech Republic half of May and flies until the beginning of August (STRAKA &BOGUSCH 2017), endangered in Ger- (CELARY 1998). The species visits blooming many (WESTRICH et al. 2011), and vulnerable in plants of the families Crassulaceae, Fabaceae, Slovenia (ANONYMOUS 2002). In Switzerland it Resedaceae, with a preference for Lotus corniculatus, was listed as extinct (AMIET 1994) but later dis- Onobrychis viciifolia SCOP., Sedum rupestre L. covered again (AMIET et al. 2014). This is the first (SCHEUCHL &WILLNER 2016). Nests are located record of this species in the Lublin Upland. in broad cavities of stones and rock, independent (BANASZAK &ROMASENKO 1998). Nests are Osmia cerinthidis parasitized by Stelis punctulatissima (KIRBY, This rare Subpontic-Mediterranean species oc- 1802) and probably Chrysis marginata curs in Central, Eastern and Southern Europe, Asia MOCSÁRY, 1889 (SCHEUCHL &WILLNER 2016). Minor, Iran and Sicily (BANASZAK &ROMASENKO In Poland, A. oblongatum is known from single 1998, SCHEUCHL &WILLNER 2016). Adults of stands in the south of the country (BANASZAK O. cerinthidis appear in the second half of April 2000a, BANASZAK et al. 2001). Information on the and fly until the beginning of July (BANASZAK et al. Polish localities until 21st century are given in 2001). This is an oligolectic species on Boragina- CELARY (1998), after this time A. oblongatum was ceae with a strong preference for Cerinthe recorded in various regions: Baltic Coast: CF43 (SCHEUCHL &WILLNER 2016), females have also Gdañsk-Jelitkowo, CF56 KuŸnica –BANASZAK been recorded on the flowers of Anchusa officina- (2016), Pomeranian Lakeland: CE21 „Gruczno” lis L., Sinapis arvensis L. and some species from nature reserve; CE32 Œwiecie –BANASZAK et al. Fabaceae (RUSZKOWSKI &BILIÑSKI 1986). They (2006); Cedynia LP: VU45-47 near Cedynia; nest in pre-existing cavities in different substrata, VU47,57 near Zatoñ Dolna – BANASZAK &TWERD preferring those of plant origin. The cell partitions (2018), Eastern Beskid Mts: EV38 Magura NP: and nest plug are made of mud. The nest consists of Krempna – WIŒNIOWSKI &WERSTAK (2009), 2-9 cells (BANASZAK &ROMASENKO 1998). In Wielkopolska-Kujawy Lowland: XT29 Wielko- Poland, O. cerinthidis is known from a few stands, polska NP: Osowa Góra – BANASZAK (2000b); scattered in the south and south-eastern part of the CD09 Bydgoszcz-Fordon – BANASZAK et al. (2006); country (DYLEWSKA &CELARY 2000, BANASZAK XU98-99, CD08-09 Bydgoszcz – BANASZAK et al. 2001). In the 21st century O. cerinthidis was (2008a); XU96 Lubostroñ –BANASZAK (2008b); recorded in regions: Ma³opolska Upland: DB82 XU98 Ma³e Rudy “Ostrów” near Szubin – Cisów-Or³owiny LP: Szczecno; Chêciny-Kielce BANASZAK et al. (2014); XU20-21, XU30-31 LP: DB62 near Chêciny, DB63 near Jaworzynia Poznañ –BANASZAK-CIBICKA &BANASZAK and near Szewce forest district 97; DA69 Nadnidzie (2011); XU20 Poznañ Botanical Garden, XU30-31 LP: Piñczów Mts near Piñczów, Piñczów Mts west Poznañ Citadel Park – BANASZAK-CIBICKA et al. Piñczów and W³ochy – B¥K-BADOWSKA (2012a); (2018); XT29 Puszczykowo – CIERZNIAK (2003a); 30 M. BORAÑSKI et al.

XT28-29 Wielkopolska NP – CIERZNIAK (2003a) czyñska –WIŒNIOWSKI &PIOTROWSKI (2013) and and CIERZNIAK (2003b); Wzniesienia £ódzkie LP: Ma³opolska Upland: Chêciny-Kielce LP: DB62 DC13-14 Brzeziny, DC04 Plichtów – KOWALCZYK near Chêciny, DB63 near Jaworzynia; Nadnidzie et al. (2009b); CD28 Rzêczkowo, CD47 To- LP: DA68 near Chrobierz, DA69 Pinczów Moun- ruñ-Kaszczorek – PAWLIKOWSKI &HIRSCH tains near Pinczów, Pinczów Mountains west (2002); BD95 Bielawy – TWERD &BANASZAK Piñczów and east Pinczów – B¥K-BADOWSKA (2017); WU73 ecological site „Jaskó³cza Skarpa” (2012a). near Sieraków – WENDZONKA (2011), Mazovian Lowland: The present status of threat in Europe is un- Kampinos NP: CC99 Dziekanów known. On the IUNC Red List (Europe) this bee is Leœny, DD80 near Dziekanów Polski and near Upland: classified as least concern (NIETO et al. 2014). Pieñków –PLEWKA (2003), Ma³opolska This species is rare in Slovenia (ANONYMOUS EB51 „Góry Pieprzowe” nature reserve – 2002), Hungary (JÓZAN 2011), and Switzerland BANASZAK (2003); CC83, CC92, CC94, DC03 (SCHEUCHL &WILLNER 2016). S. odontopyga is £ódŸ, DC23 S³otwiny, CB48 Szynkielów – listed on the National Red Lists of the Czech Republic BANASZAK &KOWALCZYK (2007); Cisów-Or³ow- (near threatened; STRAKA &BOGUSCH 2017), Ger- iny LP: DB82 Szczecno, DB92 S³opiec; Chêciny- many (vulnerable; WESTRICH et al. 2011), and Po- Kielce LP: DB63 near Jaworzynia, DB62 near land (data deficient; G£OWACIÑSKI 2002). Korzecko; Nadnidzie LP: DA78 Skorocice, DA68 near Chrobierz – B¥K-BADOWSKA (2012a); DA78 Stelis ornatula Nadnidzie LP: near Chotel Czerwony „Przêœlin” This rare cleptoparasitic bee occurs in the Medi- nature reserve – B¥K-BADOWSKA (2012c); DB92 Cisów-Or³owiny LP: near Nowa Huta – terranean area from Morocco in the west to Turkey in the east, and in Central and Northern Europe up B¥K-BADOWSKA (2014); CC93 £ódŸ Botanical to 63°N. Its distribution area extends in the east Garden – KOWALCZYK &KURZAC (2003) and into Iran, Central Asia and the Ussuri region in the KOWALCZYK et al. (2004); DC22 Budziszewice – Russian Far East (KASPAREK 2015). Females of KOWALCZYK et al. (2008); CC50 ecological site the species lay their eggs in the nests of a number „Góra Charlawa” – KOWALCZYK et al. (2009a), Mts: of Osmiini species, mainly Hoplitis claviventris, Œwiêtokrzyskie EB03 Œwiêtokrzyski PN: Góra H. leucomelana, sometimes H. acuticornis (DUFOUR Che³mowa – B¥K (2008); DB94 Œwiêtokrzyski &PERRIS, 1840), H. tridentata (DUFOUR &PERRIS, PN: Góra Miejska – B¥K (2008) and B¥K-BADOWSKA 1840), Osmia maritima FRIESE, 1885, and Osmia Kraków- Upland: (2012a), Wieluñ CB46 To- caerulescens. Some hosts from the genus Pseudo- porów – KOWALCZYK &KURZAC (2002); DA16 anthidium have also been recorded (KASPAREK Ojców NP: Czajowice and Pr¹dnik Czajowski – 2015, SCHEUCHL &WILLNER 2016). Hosts appar- WIŒNIOWSKI (2007). ently also include Ceratina cyanea (CELARY The present status of threat in Europe is un- 1989) and Ceratina cucurbitina (ROSSI, 1792) known. On the IUNC Red List (Europe), it is listed (KASPAREK 2015). The bees fly from April till the as least concern (NIETO et al. 2014). This species is end of August (SCHEUCHL &WILLNER 2016). near threatened in Germany (WESTRICH et al. This species was observed on the flowers of Rubus 2011) and vulnerable in Poland (G£OWACIÑSKI L., Potentilla L., Lotus L., Viccia L., Ledum L., 2002). In recent years, there has been an increase Hypochoeris L., and Hieracium L. (RUSZKOWSKI in the number of localities of this species in Po- et al. 1986). In Poland S. ornatula has been found land, however A. oblongatum is still considered to nearly throughout the country, but always on a rare be a rare species (B¥K-BADOWSKA 2014). basis (CELARY 1989, BANASZAK et al. 2001, BANASZAK 2010c). In the 21st century, S. orna- Stelis odontopyga tula was recorded in various regions: Baltic Stelis odontopyga is widely distributed in South- Coast: CF56 KuŸnica –BANASZAK (2016), Mas- ern and Central Europe, extending from Spain in urian Lakeland: EE25 Masurian LP: Dobry the south to Belgium and Thuringia in the north; in Lasek – BANASZAK (2010a), Wielkopolska- the east to Poland, Romania and Ukraine Kujawy Lowland: XU20-21, XU30-31 Poznañ – (KASPAREK 2015). It is a cleptoparasite of Osmia BANASZAK-CIBICKA &BANASZAK (2011); spinulosa (BANASZAK &ROMASENKO 1998). It XU30-31 Poznañ Citadel Park – BANASZAK-CIBICKA flies from June until the begining of August et al. (2018); WU73 ecological site „Jaskó³cza (CELARY 1995b). The species visits blooming Skarpa” near Sieraków – WENDZONKA (2011), plants of the families Apiaceae, Asteraceae and Mazovian Lowland: Kampinos NP: DD80 Bia³a Boraginaceae (CELARY &WIŒNIOWSKI 2007). Góra near Palmiry, DC89 Niepust – PLEWKA Information on the Polish localities until 2006 are (2003), Podlasie: FC40 Poleski PN: Kolonia given in CELARY &WIŒNIOWSKI 2007, after this Wola Wereszczyñska –WIŒNIOWSKI & time S. odontopyga was recorded in two regions: PIOTROWSKI (2013), Bia³owie¿a Forest: FD94 Podlasie: FC40 Poleski PN: Kolonia Wola Weresz- Bia³owie¿a NP: Bia³owie¿a –BANASZAK et al. Long-tongued bees in proposed nature reserve 31

(2009), Ma³opolska Upland: CC93 £ódŸ – KURZAC (2009); DC89 Kampinos NP: £¹ki Strze- BANASZAK &KOWALCZYK (2007). leckie, Niepust, Szczukówek and Wywrotnia Góra Podlasie: The present status of threat in Europe is un- –PLEWKA (2003), FD18 Kurowo – known. On the IUNC Red List (Europe), it is listed BANASZAK (2006a); FB49 Polesie NP: Za³ucze as least concern (NIETO et al. 2014). The species is Stare – WIŒNIOWSKI &PIOTROWSKI (2013), rare, yet widely distributed throughout its range. Bia³owie¿a Forest: FD94 Bia³owie¿a NP: The overall population is presumed to be relatively Bia³owie¿a –BANASZAK &JAROSZEWICZ (2009), large for a parasitic bee (ORTIZ-SÁNCHEZ & Kraków-Wieluñ Upland: CB47 Za³êcze LP: ORNOSA 2014). S. ornatula is listed as least con- Krzeczów – KOWALCZYK et al. (2009c), cern in Finland (RASSI et al. 2010) and Germany Ma³opolska Upland: CB48 Warta-Widawka LP: (WESTRICH et al. 2011). In the Netherlands it is Szynkielów – BANASZAK &KOWALCZYK (2007); vulnerable (PEETERS &REEMER 2003) and rare in DB75 Suchedniów-Oblêgorek LP: Bartków forest Slovenia (ANONYMOUS 2002) and Great Britain district, division 77 – B¥K-BADOWSKA (2012b); (FALK &LEWINGTON 2015). In the “Red List of DB82 Cisów-Or³owiny LP: near „Bia³e £ugi” Threatened Animals in Poland”, it is listed as DD nature reserve and near Trzemoszna; DB63 Chêci- (data deficient) (G£OWACIÑSKI 2002). ny-Kielce LP: near Szewce (forest district 97); DA79 Nadnidzie LP: Piñczów Mountains near Grochowiska and near W³ochy – B¥K-BADOWSKA (2012a); DB82 Cisów-Or³owiny LP: “Bia³e £ugi” Apidae nature reserve – B¥K-BADOWSKA (2014); CC83 £ódŸ Botanical Garden – KOWALCZYK &KURZAC (2003) Epeoloides coecutiens and KOWALCZYK et al. (2004); DB34 Przedbórz LP: This rare cleptoparasitic bee occurs exclusively “Czarna Rózga” nature reserve – SOSZYÑSKI et al. in Europe, mainly in Northern, Central and Eastern (2008), Œwiêtokrzyskie Mts: DB84 Œwiêtokrzyski PN: Europe and in northern parts of Southern Europe Góra Radostowa – BANASZAK &KOWALCZYK (WESTRICH 1990; SCHEUCHL 2000). Females of (2007); DB94 Œwiêtokrzyski PN: Góra Miejska – E. coecutiens lay their eggs in the nests of Macropis B¥K (2008) and B¥K-BADOWSKA (2012a); DB93 fulvipes (FABRICIUS, 1804) and Macropis europaea Œwiêtokrzyski PN: near Kakonin and near Wola WARNCKE, 1973 (BOGUSCH 2005). Epeoloides Szczygie³kowska – B¥K-BADOWSKA (2012a). coecutiens visits blooming plants e.g. Lythrum The species was previously considered to be the salicaria L., Chamaenerion angustifolium (L.) SCOP. rarest European cuckoo bee but in some parts of and Thymus serpyllum L. (CELARY &WIŒNIOWSKI Europe it is clearly quite common (BOGUSCH & 2001). The univoltine, Epeoloides coecutiens flies STRAKA 2014). E. coecutiens is listed on the Euro- in July and August, the period corresponding to the pean Red List of Bees as least concern (NIETO et al. nesting period of its hosts (BOGUSCH 2005). This 2014), the same status of threat is given in the species is observed in different parts of Poland, how- Netherlands (PEETERS &REEMER 2003) and Ger- ever, even where it is found, it is very rare (CELARY many (WESTRICH et al. 2011). The species is also 1990, PAWLIKOWSKI et al. 1993, BANASZAK listed on the National Red Lists as vulnerable in 2010c ). In the 21st century, E. coecutiens was re- Slovenia (ANONYMOUS 2002) and near threat- Baltic Coast: corded in various regions: VV67 ened in the Czech Republic (STRAKA &BOGUSCH Wolin NP: Miêdzywodzie –BANASZAK (2010b), 2017). In the “Red List of Threatened Animals in Pomeranian Lakeland: VU47,57 Cedynia LP: Poland”, it is listed as DD (data deficient) near Zatoñ Dolna – BANASZAK &TWERD (2018), (G£OWACIÑSKI 2002). Masurian Lakeland: EE34 Masurian LP: Wy- gryny – BANASZAK (2010a); EF01 near Stawnica Eucera interrupta –BANASZAK &SZEFER (2013), Wielkopolska- This rare Subpontic-Mediterranean species oc- Kujawy Lowland: XU98 Ma³e Rudy “Ostrów” curs from the Iberian Peninsula in the west, near Szubin – BANASZAK et al. (2014); CD32 Southern and Central Europe, to Asia Minor, the Piotrków Kujawski – BANASZAK &SOBIERAJ- Caucasus and Kazakhstan in the east, the northern BETLIÑSKA (2016); CD07 „Dziki Ostrów” nature border of its range is the Baltic Sea and Perm, reserve near Bydgoszcz – BANASZAK &TWERD southern: Sicily and Thessaly (SCHEUCHL & (2015); DB95 Bielawy – TWERD &BANASZAK WILLNER 2016). These univoltine bees fly from (2017), Mazovian Lowland: DC59 Kampinos May until the end of July (SCHEUCHL 2000). As NP: Bromierzyk – SZCZEPKO et al. (2002); DC59; an oligolectic species, they collect pollen from the DC69 Kampinos NP – SZCZEPKO &KOWALCZYK flowers of the Fabaceae family (SCHEUCHL & (2006); DC36 Bolimów LP: „Polana Siwica” na- WILLNER 2016), e.g. Coronilla varia L., Lotus ture reserve – KOWALCZYK &KURZAC (2007) and corniculatus, Trifolium pretense, Medicago sativa KOWALCZYK &KURZAC (2009); DC46 Bielawy (RUSZKOWSKI et al. 1994). Their nests have nu- Glade and Olszówka Glade – KOWALCZYK & merous branches, with an average depth of 28 cm; 32 M. BORAÑSKI et al. the nest cells are arranged vertically (RUSZKOWSKI &BANASZAK (2011); XU30-31 Poznañ Citadel et al. 1998). Nests are parasitized by a cuckoo bee, Park – BANASZAK-CIBICKA et al. (2018); XU62 Nomada sexfasciata PANZER, 1799, and probably Lednica LP: Dziekanowice – BANASZAK & by Nomada nobilis HERRICH-SCHÄFFER, 1839 RATYÑSKA (2016); CD05 Janikowo, DB95 Bie- (SMIT 2018). In the 21st century, PLEWKA (2003) lawy – TWERD &BANASZAK (2017), Kraków-Wie- confirms the occurrence of this species in the luñ Upland: CA94 Rudno LP: near Mirów – Mazovian Lowland: DD80 Kampinos NP: near MOROÑ et al. (2008), Eastern Sudetes Mts: Dziekanów Polski, and only one new locality of YR14 near Kietrz – BANASZAK et al. (2017). this species was published, but it comes from 1927: This species is observed in different parts of Po- Wielkopolska Kujawy Lowland: - WU14 Gorzów land, however, rarely (CELARY 1995a, CELARY & Wielkopolski – BANASZAK (2006b). The species WIŒNIOWSKI 2007). The new locality of N. bifas- was considered very common in central Europe at ciata in a proposed nature reserve “Skarpa the end of the 19th century, but now the population Wiœlana” in Mêæmierz is characterized by a high trend is considered to be decreasing (QUARANTA number of specimens of this species. The popula- 2014). Recently, a decline in the population and tions of N. bifasciata seem to be stable (SMIT range of this species has been observed in the 2013), and are in the category least concern ac- Czech Republic (STRAKA &BOGUSCH 2017). In cording to the IUNC Red List (Europe) (NIETO et al. the 20th century, in Poland, E. interrupta could be 2014). This species is listed as least concern in observed almost anywhere in the country Germany (WESTRICH et al. 2011), vulnerable in (BANASZAK 1980), but the last known new local- the Netherlands (PEETERS &REEMER 2003), and ity of this species is given by PAWLIKOWSKI et al. deficient data in Poland (G£OWACIÑSKI 2002). (1993) – Lublin Upland: FB84 „Gliniska” nature reserve, GB03 Gródek, GA09 Radków. A lack of new Nomada stigma records in the last 25 years may suggest a decline This rare Palaearctic species occurs in North Af- in the population of this species in Poland as well. rica (Algeria and Tunisia) and Eurasia, from Por- This species is listed on the European Red List of tugal through Europe, Asia Minor, the Caucasus Bees as least concern (NIETO et al. 2014), but it is and Central Asia to Yakutia (SCHEUCHL & rare in Slovenia (ANONYMOUS 2002) and in Por- WILLNER 2016). This species is partially bivoltine tugal (BALDOCK et al. 2018). E. interrupta is listed and flies from April to August (SMIT 2018). No- on the National Red Lists of: the Czech Republic mada stigma visits blooming plants of the families (critically endangered; STRAKA &BOGUSCH 2017), Brassicaceae, Rosaceae, Apiaceae, Fabaceae, Dip- Germany (vulnerable; WESTRICH et al. 2011), sacaceae and Asteraceae (CELARY &WIŒNIOWSKI Switzerland (least concern; AMIET 1994), and Po- 2011). This is a cleptoparasite of Andrena labialis land (data deficient; G£OWACIÑSKI 2002). (KIRBY, 1802) and probably A. decipiens SCHENCK, 1861, A. schencki MORAWITZ, 1866, A. fimbriata Nomada bifasciata BRULLÉ, 1832, A. flavilabris SCHENCK, 1874 This West Mediterranean species inhabits West, (SMIT 2018) as well. Hosts apparently also include South, Central, Southeastern and Eastern Europe, A. humilis IMHOFF, 1832 and A. taraxaci GIRAUD, the Canary Islands, North Africa and the Middle 1861 (CELARY 1995a). East (SMIT 2018). The bees fly from March until Information on the Polish localities (with UTM the end of June (SCHEUCHL &WILLNER 2016). coordinates) until 2010 are given in CELARY & Females of N. bifasciata lay their eggs in the nests WIŒNIOWSKI (2011), after this time N. stigma was of Andrena gravida IMHOFF, 1832, in Spain possi- recorded in two regions: Pomeranian Lakeland: bly of Andrena savignyi SPINOLA, 1838 as well VU47,57 Cedynia LP: near Zatoñ Dolna – (SMIT 2018). The species visits flowers of Salix BANASZAK &TWERD (2018) and Wielkopolska- spp., Euphorbia cyparissias, Potentilla verna L., Kujawy Lowland: XU20-21, XU30-31 Poznañ – Tussilago farfara and Taraxacum officinale BANASZAK-CIBICKA &BANASZAK (2011); (CELARY 1995a). Information on the Polish locali- CD05 Janikowo – TWERD &BANASZAK (2017). ties until 2006 are given in CELARY & This species is listed on the European Red List of WIŒNIOWSKI (2007), after this time N. bifasciata Bees as least concern (NIETO et al. 2014), but was recorded in various regions: Pomeranian populations are small and in a number of countries Lakeland: CE32 Œwiecie –BANASZAK (2010c), the species is in decline (SMIT 2014). This species Masurian Lakeland: Masurian LP: EE25 Dobry is included on the National Red Lists of the follow- Lasek, EE44 Wejsuny – BANASZAK (2010a), ing European countries: Slovenia (regionally ex- Wielkopolska-Kujawy Lowland: XU98-99, tinct; ANONYMOUS 2002), Finland (critically CD08-09 Bydgoszcz – BANASZAK (2008a); CD09 endangered; RASSI et al. 2010), Switzerland (en- Bydgoszcz-Myœlêcinek and Bydgoszcz-Wyszogród, dangered; AMIET 1994), Sweden (vulnerable; CD19 Bydgoszcz-Fordon – BANASZAK (2010c); GÄRDENFORS et al. 2015), the Czech Republic XU20-21, XU30-31 Poznañ –BANASZAK-CIBICKA (vulnerable; STRAKA &BOGUSCH 2017), the Long-tongued bees in proposed nature reserve 33

Netherlands (near threatened; PEETERS &REEMER (Anthidiellum strigatum, Anthidium manicatum, 2003), Germany (least concern; WESTRICH et al. A. punctatum, Chelostoma rapunculi, Coelioxys 2011) and rare in Portugal (BALDOCK et al. 2018). mandibularis, C. quadridentata, Heriades truncorum, In the “Red List of Threatened Animals in Poland” Hoplitis claviventris, H. leucomelana, Megachile this species was not evaluated. This is the first rec- versicolor, M. ligniseca, M. maritima, M. genalis, ord of this species from the Lublin Upland. Osmia bicolor, O. leaiana, O. niveata, Stelis ornatula, Trachusa byssina), 3 – West Palaearctic (Chelostoma Nomada zonata florisomne , Hoplitis adunca, Osmia aurulenta, This rare cuckoo bee lives in North Africa (Mo- O. bicornis, O. caerulescens, O. spinulosa), 4 – rocco) and in Eurasia, from Portugal through Eurocaucasian (Stelis odontopyga), 5 – South-West Southern and Central Europe, Asia Minor, the Palaearctic (Anthidium oblongatum), 6 – South Pa- Caucasus to Central Asia; north to the Baltics, in laearctic (Hoplitis papaveris), 7 – Subponto- Russia to Kirov and Perm; south to Sardinia, Mediterranean (Heriades crenulatus, Osmia cer- Emilia-Romagna, Peloponnese and northern Iran inthidis). The frequency distribution of particular (SCHEUCHL &WILLNER 2016). They are a cleptopara- elements is presented in Table 1. site of Andrena dorsata (KIRBY, 1802), possibly also Andrena congruens SCHMIEDEKNECHT, 1883 (SMIT 2018). N. zonata has two generations: from Aprilto Table 1 May and from July to August (CELARY 1995a). The species mainly visits flowers from the family As- Numerical and percentage frequency of par- teraceae but also visits some flowers from Crassu- ticular zoogeographical elements of Mega- chilidae of the proposed nature reserve laceae, Fabaceae, Lamiaceae, Rhamnaceae, Rosaceae “Skarpa Wiœlana” and Salicaceae (CELARY &WIŒNIOWSKI 2011). Information on the Polish localities (with UTM co- Zoogeographical Number Share ordinates) until 2010 are given in CELARY & element of species in % WIŒNIOWSKI (2011), after this time N. zonata was Baltic Coast: Holarctic 2 6.45 recorded in various regions: VV99 Palaearctic 18 58.06 Trzêsacz –BANASZAK (2016), Masurian Lake- West Palaearctic 6 19.35 land: EE24 Masurian LP: Rosocha – BANASZAK Eurocaucasian 1 3.23 (2010a); EF01 near £êkajny –BANASZAK & South-West Palaearctic 1 3.23 SZEFER (2013), Wielkopolska-Kujawy Lowland: South Palaearctic 1 3.23 XU62 Lednica LP: Ledniczka Island and Mewia Subponto-Mediterranean 2 6.45 Island – BANASZAK &RATYÑSKA (2016), Kraków-Wieluñ Upland: DA24 near Kraków – The results in Table 1 indicate that in the fauna of MOROÑ et al. (2009), Eastern Sudetes Mts: Megachilidae of the proposed nature reserve YR15 near Kietrz – BANASZAK et al. (2017). “Skarpa Wiœlana”, the most numerous elements The present status of threat in Europe is are Palaearctic and West Palaearctic (respectively unknown. On the IUNC Red List (Europe) this – 18 species – 58% and 6 species – 19%), while the species is classified as least concern (NIETO et al. remaining ones are much less numerous (1-2 spe- 2014). It is listed on National Red Lists as probably cies – 3-6%). extinct in Slovenia (Anonymous 2002), near threatened in the Netherlands (PEETERS &REEMER 2003) and Germany (WESTRICH et al. 2011), and Apidae least concern in Poland (G£OWACIÑSKI 2002). Nomada zonata is also a rare species in Lithuania The fauna of Apidae of the proposed nature re- (MONSEVIÈIUS 2004), Hungary (JÓZAN 2011), serve “Skarpa Wiœlana” includes nine zoogeo- the United Kingdom (FALK &LEWINGTON 2015), graphical elements. The following elements have and Portugal (BALDOCK et al. 2018). This is the been evidenced: 1 – Holarctic (Bombus LATREILLE, first record of this species from the Lublin Upland. 1802 = Terrestribombus VOGT, 1911), 2 – Pa- laearctic (Anthophora aestivalis, Bombus bohemi- cus, B. campestris, B. hortorum, B. hypnorum, VI. ZOOGEOGRAPHICAL ANALYSIS B. muscorum, B. pascuorum, B. pratorum, B. ru- derarius, B. rupestris, B. sylvestris, Ceratina cy- Megachilidae anea, Epeoloides coecutiens, Epeolus variegatus, Eucera longicornis, Melecta luctuosa, Nomada The fauna of Megachilidae of the proposed na- flavoguttata, N. fulvicornis, N. lathburiana, ture reserve “Skarpa Wiœlana” includes seven zoo- N. panzer, N. ruficornis, N. rufipes, N. stigma),3– geographical elements. The following elements West Palaearctic (Anthophora plumipes, Bombus have been evidenced: 1 – Holarctic (Megachile lapidaries, B. sylvarum, Nomada fucata, N. fabri- centuncularis, M. circumcincta),2–Palaearctic ciana, N. flavopicta, N. goodeniana, N. integra), 34 M. BORAÑSKI et al.

4 – Eurosiberian (Nomada moeschleri), 5 – Euro- M. maritima, Osmia niveata, O. spinulosa, Stelis caucasian (Nomada armata, N. ferruginata, odontopyga, Trachusa byssina), appear at an aver- N. marshamella), 6 – European (Nomada flava, age daily temperature exceeding 15°C. The fre- N. signata), 7 – South-West Palaearctic (Nomada quency distribution of the phenological groups is zonata, Tetralonia salicariae, T. malvae), 8 – Sub- presented in Table 3. ponto-Mediterranean (Eucera interrupta), 9 – West Mediterranean (Nomada bifasciata). The fre- quency distribution of particular elements is pre- Table 3 sented in Table 2. Numerical and percentage frequency of phe- nological groups in the fauna of Megachilidae of the proposed nature reserve “Skarpa Wiœlana” Table 2 Numerical and percentage frequency of par- Phenological Number Share ticular zoogeographical elements of Apidae group of species in % of the proposed nature reserve “Skarpa Wiœlana” Early spring species 2 6.45 Late spring species 9 29.03 Zoogeographical Number Share Summer species 20 64.52 element of species in % Holarctic 1 2.33 The results in Table 3 show that the most numer- Palaearctic 23 53.49 ous are the summer species (20 species – 64.5%, West Palaearctic 8 18.60 while the late spring species constitute no more Eurosiberian 1 2.33 Eurocaucasian 3 6.97 than 29% of the Megachilidae inhabiting the European 2 4.65 Mêæmierz, and the early spring species are rarest South-West Palaearctic 3 6.97 (2 species – nearly 6.5%). Subponto-Mediterranean 1 2.33 West Mediterranean 1 2.33 Apidae The results in Table 2 show that the most numer- ous species are those with a wide range of distribution In the fauna of Apidae of the proposed nature re- (with the exception of Holarctic and European), serve “Skarpa Wiœlana” all three phenological such as Palaearctic (23 species) and West Palaearc- groups are present as well. The groups include the tic (8 species). The remaining zoogeographical following species: early spring species – Antho- elements are considerably less numerous. phora plumipes, Melecta luctuosa, Nomada bifas- ciata, N. fabriciana, N. ferruginata, N. flava, N. flavoguttata, N. fucata, N. fulvicornis, VI. PHENOLOGICAL ANALYSIS N. goodeniana, N. lathburiana, N. marshamella, N. panzeri, N. ruficornis, N. signata, N. zonata; late spring species – Anthophora aestivalis, Cer- Megachilidae atina cyanea, Eucera longicornis, E. interrupta, Nomada integra, N. moeschleri, N. stigma;sum- Based on DYLEWSKA studies (DYLEWSKA mer species – Epeoloides coecutiens, Epeolus 1987, 2000) the fauna of Megachilidae inhabiting variegatus, Nomada armata, N. flavopicta, the proposed nature reserve “Skarpa Wiœlana”be- N. rufipes, Tetralonia salicariae, T. malvae. Wild long to three phenological groups. The first group, bees of the genus Bombus are social insects (or early spring species (Osmia bicolor, O. bicornis), their parasites) with several generations during the appear when the average daily temperature whole season from March to September or Octo- reaches at least 8°C and the temperature in sun is at ber, so they were excluded from our phenological least 21°C. The second group, late spring species analysis. The frequency distribution of the pheno- (Chelostoma florisomne, C. rapunculi, Hoplitis logical groups is shown in Table 4. adunca, Megachile versicolor, Osmia aurulenta, O. leaiana, O. caerulescens, O. cerinthidis, Stelis The results in Table 4 indicate that the most nu- ornatula), appear when the average daily tempera- merous group includes the early spring species ture is at least 10° C. The third group, summer species (16 species – 53.34%), while the remaining ones (Anthidiellum strigatum, Anthidium manicatum, are less numerous (both 7 species – 23.33%). A. oblongatum, A. punctatum, Coelioxys mandibu- In the study area, we recorded 74 species of wild, laris, C. quadridentata, Heriades crenulatus, long-tongued bees (31 of Megachilidae and 43 of H. truncorum, Hoplitis claviventris, H. leucome- Apidae). This constitutes 35% of the fauna of lana, H. papaveris, Megachile centuncularis, long-tongue bees in Poland. Among of the long- M. circumcincta, M. genalis, M. ligniseca, tongued bees of the proposed reserve “Skarpa Long-tongued bees in proposed nature reserve 35

the studied habitat (64.52%), whereas among the Table 4 Apidae, the most numerous group was the early Numerical and percentage frequency of spring species (53.34%). The high share of summer phenological groups in the fauna of Apidae species among Megachilidae in xerothermic of the proposed nature reserve “Skarpa Wiœlana” habitats showed i.a. BANASZAK (2003) in the reserve „Góry Pieprzowe” – 70.1%; BANASZAK Phenological Number Share et al. (2006) in the xerothermic swards of the lower group of species in % Vistula valley – 72.1% and BANASZAK et al. Early spring species 16 53.34 (2017) in the reserve „Góra Gipsowa” – 76.2%. Late spring species 7 23.33 A large portion of the early spring species of Apidae Summer species 7 23.33 in “Skarpa Wiœlana” (53.34%) is made up of the large number of species from the genus Nomada. A similar relation was recorded in other xerother- mic habitats (BANASZAK et al. 2006, 2017). Wiœlana”, twelve species are included in the “Pol- ish Red List of Threatened and Endangered Ani- Considering the total number of species, a large mals” (G£OWACIÑSKI 2002), three of them are number of which are rare and /or endangered spe- vulnerable: Anthidium oblongatum, Hoplitis papaveris, cies of bees, as well as data on the occurrence of Osmia cerinthidis. All of the recorded species are endangered butterfly species in the study area i.a. listed on the IUCN Red List of Bees (NIETO et al. Chazara briseis (LINNAEUS, 1764) Chelis maculosa 2014). Despite 6 years of research, we did not find (GERNING, 1780), Colias myrmidone (ESPER, Eucera nigrescens – a species that occured in this 1780), Scolitantides orion (PALLAS, 1771) (BUSZKO area in the 80’s of the last century (given as Eucera 1997, PA£KA 1990), the location „Skarpa Wiœlana” tuberculata FABRICIUS, 1793) (RUSZKOWSKI et should be protected as a nature reserve and kept se- al. 1994) – a rare species in Poland (BANASZAK cured against excessive human incursion. At the 2000a). site in Mêæmierz, protective measures should be The species diversity of long-tongued wild bees continued consisting of counteracting plant suc- in the proposed reserve “Skarpa Wiœlana” can be cession and the fragmentation of xerothermic compared with research conducted in similar habi- communities. tats. In the research conducted in the reserves of xerothermic vegetation of the Nadnidziañski Landscape Park (B¥K-BADOWSKA 2012a, 2012c), REFERENCES 62 species of long-tongued bees were recorded, also BANASZAK (2003) from the “Góry Pieprzowe” AMIET F. 1994. Liste rouge des abeilles menacées de Suisse. reserve, lists fewer species – 64. BANASZAK et al. [In:] DUELLI P. (ed.). Listes rouges des espèces animales (2006) recorded 99 species of long-tongued bees menacées de Suisse, Office fédéral de l’environnement, des (43 Megachilidae and 56 Apidae) in the xerother- forêts et du paysage, Berne: 38-44. [In French]. mic swards of the lower Vistula valley, however, AMIET F., HERRMANN M., MÜLLER A., NEUMEYER R. 2014. Hyménoptères Aculéates (Abeilles Solitaires). CSCF & the research area was much larger and included karch News, 39: 6-7. [In German]. 17 locations. Individually analyzed, the number of ANONYMOUS. 2002. 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