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While the registration of dragonflies on man-made reservoirs of the Silesian Region took place, in 2006 there were recorded nu- merous males and less numerous females of Aeshna affinis. Single individuals have been reported in 1939 in Gwoździany and in 1966 in Ustroń. Since its last record Aeshna affi­nis has been noted again in 2005 in an old river bed of the River Odra River in Lasaki. It has been recorded on seven new sites in the next year. Most of those new sites were smali sinkhole ponds created by coal-mining. What is morę Aeshna affinis was recorded on a few natural sites too. While on natural sites there were 2-4 specimens recorded, on anthropogenic water bodies there were usu- ally about 20 individuals. Creating tandems indicated making attempts to inhabit anth­ropogenic water bodies by this species. The­re was another ąuite rare and stenothermic species - Crocothemis erythraea recorded on two sites together with Aeshna affinis. This species has been observed sińce 2002 in Odra River Valley, near the Southern bor- der of Silesian Region with Czech Republic. Nevertheless it was recorded for the first time in sinkhole ponds in 2006.
Two new localities (within 35 km) of the Scarlet Dragonfly were recorded on the clay pits in the South Wielkopolska region: 1) Odolanów (Ostrów Wielkopolski district, 51º35’ N, 17º39’ E, UTM: XT81): one ♂ on 28th May 2007; 2) Kotlin (Jarocin district, 51º54’ N, 17º40’ E, UTM: XT85): one ♂ on 23rd June 2007. Those records were made 4-48 km from localities detected by Żurawlew (2009) in Pleszew district (Fig. 1) and support his opinion about high importance of clay pits for this species. Both records came from Kartoteka Przyrodnicza Południowej Wielkopolski (Nature Database of the South Wielkopolska), the “citizen science” scheme, led by local group of the Polish Society for the Protection of Birds. The wider co-operation of the odonatologists with such groups and schemes is proposed in the article.
The paper presents data on 22 localities of Crocothemis erythraea recorded in Poland in 2009 (Fig. 1). 20 localities are completely new which corresponds with 40% of contemporary known so far ones (Bernard et al. 2009). Data is given from the South Greater Poland Lowland in western Poland (4 localities) as well as different regions in south-eastern Poland (18 localities). The species occupied wide spectrum of habitats. Those were in general: fish ponds, sand, gravel and clay excavations, in a lesser degree - peat excavations, natural and anthropogenic small water bodies, a canal, a regulated small river, a peat bog lake and two eutrophic lakes. However, the majority of key features of those habitats was suitable for the optimum of C. erythraea (Fig. 2). The localities in Wielkopolska (Great Poland) are situated in the region where C. erythraea has already been recorded and two of the described populations last for 2-3 years. Abundant data from southeastern Poland has different meaning - it shows that the central part of this area (the Lublin Region) has just started to be intensively colonised. Despite many researches, only three localities of C. erythraea have been known from his area: historical one (Fudakowski 1932) and two from the years 2007-2008 (Bernard et al. 2009; Buczyn- ski unpubl. data). The intensity of migration in 2009 is well pictured by the fact that in the best examined area (51°10'-51°25' N, 22°44'-23°'07 E) C. erythraea was found up to 20% of all studied localities. Authors link the strengthening of the presence of C. erythraea in Wielkopolska and colonisation of the Lublin Region with the recent occurrence of stable populations to the north of the arc of the Carpathian Mts. - their migrating individuals towards the north do not have to cross a mountain barrier. Imagines of the second generation of C. erythraea observed in September were reproductively active at rather low temperatures as for this species (ca. 20°C in shadow). Last dates of observations are also interesting (the third decade of September) - the latest in Poland so far, however, quite similar to data from Czech Republic and the Ukraine as well as a bit earlier from the latest observations in Bavaria.
Crocothemis erythraea (Brullć, 1832) has been recorded in Poland at 11 localities in Southern and eastern parts of coun­try, and one in western part - this work presents the new locality from this region, with description of observations and the analysis of literaturę data. C. erythraea is a typical thermophilous, Mediterranean species, which reproduces in Africa, southwestern Asia and in most Southern and central European countries, to circa 53°N. On the distribution border short-lived populations are sometimes found. C. erythraea was observed in the year 2002 in a pond near village Gostyń Stary, 51°54’N, 16°57’E, by Gostyń, 65 km to the S of Poznań. It was the same water body where Aeshna affinis was recorded in 1995. It was a middle-size pond, with the area of ca. 25x120 m and its long axis directed to W-E. In the middle the shallow place with Phragmites australis was found. The who- le water column of water body was densely overgrown by Chara sp., up to the surface. Chara sp. divided the water surface on smaller areas (see photo). Inshore - sparsely T. latifolia. The shore of the whole pond linę grown by Alnus glutinosa individually. In those days, maximum air temperatu­rę at noon was 34°C. On 10 July 2002, sińce 2 pm, two terri- torial males, which sat on the last year's stalks of P. australis, were observed. The distance between them was ca. 5 m. From time to time (2-10 min.), one of two ma­les had flown round the water surface, next, the second one followed its footsteps. Unexpectedly, about 5.30 pm, both males flew away to the east, despite that the inso- lation was still very good and air tempera­turę went down “only” to 31°C. Next day, 11 July 2002, both males ap- peared on their own positions at 11 am. Ana- logous situation from day before was obse- rved, moreover, one of the males rinsed ab- domen during the flight. The specimens were moderately skittish - their escape distance was 3 m. Co-existing species in those days were as follows: Calopteryx splendens, Lestes spon- sa, Platycnemis pennipes, Erythromma viri- dulum, Ischnura elegans, Coenagrion pud­la, Anax imperator, Cordulia aenea, Soma- tochlora metallica, Libellula ąuadrimacula- ta, Sympetrum flaveolum, S. sanguineum. Interaction between C. erythraea and the mentioned above species was not observed. Although the females were not observed, reproduction was very possible (abdomen rinsing could show on earlier copulation). Unfortunately, larvae and exuviae searches from 18 V, 8 VI, 21 VI and 2 VII 2003 did not give positive result. Presented data are the first from Poland, which gives information about adults C. ery­thraea behaviours. In comparison to litera­turę data from Germany, where this species was recorded regularly and often, the de- scribed information are typical for this dragonfly. Specimen activity, fly time and behaviour are very similar. In our climate, C. erythraea is not fastidious species at se- lection of environment. It could be any sta- gnant water body with dense aąuatic vege- tation. It must be sufficiently deep and can not freeze to the bottom in winter. The de- scribed pond possessed a few additional features: it was sunny, covered from wind well and shallowed by overgrown Chara sp. Chara sp. limited water circulation and waving which facilitated heating of super- ficial layers of water. Literaturę descriptions show other plants performing the same function: Ceratophyllum, Myriophyllum (typical substrate of oviposition) and Utri- cularia. C. erythraea prefers clean and elear water. It is possible, that pieces of Chara sp. had one morę function in this water body. The bottom of this pond was heterogene- ous, partly of clay, and water usually was stirred by fish and waterfowls. Within the areas of Chara sp. water was always clean. The most essential feature of this pond was his specific microclimate, which make an impression Mediterranean or subtropi- cal climate: strong insolation, stagnant air and high temperaturę and humidity. There are similar reąuirements for A. affinis, which often co-exists with C. erythraea, which shows similar microclimate preferen- ces. Others characteristics species, which may co-exist with C. erythraea, are: Leucor- rhinia caudalis and Orthetrum cancellatum. They have most similar habitat preferences. Sympetrum fonscolombii and E. viridulum can be also found. The second one, is a ther- mophilous species, which prefers Myrio- phyllum or Ceratophyllum vegetation type. C. erythraea is a thermophilous species, given as an example and proof of global warming. Every year, from European co- untries, lying on the same geographical la- titude like Poland (for example from Gre- at Britain, Holland, Germany, Ukraine), where species was only regarded as a rare migrating element, numerous data about new localities has been given in recent years.
Crocothemis erythraea belongs to rare species in Poland. Previously it was mainly recorded in southern and eastern part of the country, sites from the west were definitely less numerous. The site described in the paper near Dzwonów (53o24’43” N; 15o12’37” E) is the northernmost site of this species in Po- land. It is the complex of a dozen or so ponds with the total area of 500 ha. The biggest pond is shallow, with quickly heating up water of high transparency, with the bottom of silt partially overgrown by: Myriophyllum verticillatum, Potamogeton pectinatus, P. natans, Nuphar luteum and Polygonum amphibium. Shores of the pond are covered with a narrow belt of: Phragmites australis, Typha latipholia and Sparganium erectum. The presence of three males flying above dams was recorded. To the accompanying species belonged: Calopteryx splendens, Lestes sponsa, Erythromma najas, Ischnura elegans, Sympecma fusca, S. paedisca, Platycnemis pennipes, Coenagrion puella, C. pulchellum, Gomphus vulgatissimus, Orthetrum cancellatum, Libellula quadrimaculata and Sympetrum sanguineum. The conditions of this habitat provide the full development of Crocothemis erythraea. Due to the lack of the larvae it is only a possibility.
In the years 2007 and 2008 in the Pleszew Poviat over 60 study sites were controlled against the occurrence of dragonflies Odonata. 45 species were recorded within (61,6% of the dragonfly fauna in Poland). The Scarlet Dragonfly was recorded at four study sites (all of them were clay excavations): 1) Kwileń (51º59’N, 17º51’E, UTM: XT96), in 2007 – 4 observations 1♂, and in 2008 it was noted during 9 controls: the highest numbers 10 VI – ca. 15♂♂, 3 VII and 31 VII – each ca. 10♂♂, additionally,10 VI a pair in copula was observed, and next, 1♀ laying eggs in Batrachium sp.; 2) Kowalew (51º53’N, 17º43’E, UTM: XT85), 1♂ observed 11 VI 2008; 3) Nowa Wieś (51º52’N, 17º46’E, UTM: XT95), 1♂ recorded on 18 VI 2008; 4) Lenartowice (51º55’N, 17º48’E, UTM: XT95), 2♂♂ patrolling and territorial noted on 25 VI 2008. In Poland the stable populations of the Scarlet Dragonfly have been found so far in the valley of the Upper Vistula River and in Przemyśl Upland. Clay excavations are the environments that play very important role in the existence of many dragonfly species (Tab. 1). This refers not only to the Pleszew Poviat but also to the whole south-eastern Great Poland (Wielkopolska).
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