Research Article
Research Article
Spatial distribution and seasonal changes of mayflies (Insecta, Ephemeroptera) in a Western Balkan peat bog
expand article infoMarina Vilenica, Andreja Brigić§, Mladen Kerovec§, Sanja Gottstein§, Ivančica Ternjej§
‡ University of Zagreb, Petrinja, Croatia
§ University of Zagreb, Zagreb, Croatia
Open Access


Peat bogs are unique wetland ecosystems of high conservation value all over the world, yet data on the macroinvertebrates (including mayfly assemblages) in these habitats are still scarce. Over the course of one growing season, mayfly assemblages were sampled each month, along with other macroinvertebrates, in the largest and oldest Croatian peat bog and an adjacent stream. In total, ten mayfly species were recorded: two species in low abundance in the peat bog, and nine species in significantly higher abundance in the stream. Low species richness and abundance in the peat bog were most likely related to the harsh environmental conditions and mayfly habitat preferences. In comparison, due to the more favourable habitat conditions, higher species richness and abundance were observed in the nearby stream. Three of the recorded species, Caenis luctuosa from the peat bog, and Eurylophella karelica and Leptophlebia marginata from the stream are new records for the Croatian mayfly fauna. Typical Central European life cycle patterns were confirmed for several species (e.g. Baetis vernus, Nigrobaetis niger, Electrogena ujhelyii), while for several others (e.g. Habrophlebia fusca, Paraleptophlebia submarginata) some discrepancies were observed. Therefore, these results provide new and valuable information on the ecology of mayflies in peat bog habitats.


Environmental factors, life cycle, mayfly assemblages, new records, peat bog


Acidic peat bogs dominated by Sphagnum species occupy approximately 3% of the Earth’s land surface (Kivinen and Pakarinen 1981) and contain one-third of the world’s soil carbon (Joosten and Clarke 2002). Consequently, they play an important role in the global carbon cycle and climate change (Limpens et al. 2008, Battin et al. 2009). Peat bogs are widely distributed in boreal regions of the Northern hemisphere, but in the Western Balkans are in patches of isolated habitat (Spitzer and Danks 2006, Topić and Stančić 2006). These unique and environmentally extreme wetland ecosystems are characterized by diverse aquatic and semiaquatic habitats, high water table and acidity, low oxygen and nutrient levels (Spitzer and Danks 2006).

Peat bogs are amongst the most fragile and endangered ecosystems worldwide (Langheinrich et al. 2004) due to the climate change, agricultural activities (i.e. drainage and peat extraction) and secondary succession (Doyle 1990, Więcek et al. 2013). Even though the conservation values of bogs have been internationally recognized, these wildlife habitats are still understudied in comparison to most other freshwater habitats (Baars et al. 2014). Recent studies have shown that peat bogs are inhabited by unique macroinvertebrate assemblages, often containing rare and threatened species (Hannigan and Kelly-Quinn 2012, Drinan et al. 2013, Baars et al. 2014).

Mayflies are merolimnic insect order (i.e. with aquatic nymphal stages and terrestrial adults) with nymphs inhabiting a wide range of lotic and lentic habitats (Bauernfeind and Soldán 2012). Mayfly assemblages respond to multiple environmental factors, including water temperature (e.g. Bauernfeind and Soldán 2012), water velocity, oxygen content (e.g. Moog 2002; Bauernfeind and Soldán 2012) and pH (e.g. Fiance 1978, Petrin 2011). Mayflies are highly sensitive to habitat alterations (e.g. Zedková et al. 2015, Vilenica et al. 2016) and widely used as indicators in bio-monitoring assessments (Elliott et al. 1988, Sartori and Brittain 2015). Comprehensive data on mayfly life history traits, such as life cycles, habitat and environmental preferences are highly important for the understanding of ecosystem functioning (e.g. Brittain 1990, 1991, Raddum and Fjellheim 1993, Erba et al. 2003).

Aquatic macroinvertebrate (including mayfly) micro-distribution and ecology have primarily been studied in Northern and Central European peat bogs (e.g. Baars et al. 2014, Mieczan et al. 2015), with no comprehensive studies on mayfly assemblages in peat bogs of the Western Balkans. Thus, the aims of this study were to: 1) compare the spatial distribution of mayfly assemblages in two focal habitats: the peat bog and adjacent stream; 2) analyse environmental variables that affect the spatial distribution of mayfly assemblages and 3) determine mayfly seasonal dynamics in studied habitats.


Study area

The study was conducted in the Đon močvar, one of the largest (10 ha) and oldest peat bogs in Croatia. The peat bog is located in the central part of the country (45°19'4.33"N, 15°54'32.83"E, Fig. 1) at 130 m a.s.l., under the slopes of the Petrova gora Mountain and surrounded by the Danković klada Stream. This region is characterised by a temperate humid climate (Šegota and Filipčić 2003) with an average annual temperature of 10.5 °C and an average annual precipitation of 1 050 mm (Zaninović et al. 2008).

Figure 1. 

Geographical position of the Đon močvar peat bog, Croatia.

The peat bog is a complex ecosystem, encompassing a mosaic of different habitats from open woodless Sphagnum spp. L. sites, deep hollows, and small ponds, to swampy areas dominated by Rhynchospora alba (L.) Vahl and Phragmites australis (Cav.) Trin. ex Steud. Abandonment of traditional land-management practices, such as mowing and grazing, has led to severe processes of succession at the peat bog. As a result, during the 20th century, the open area on the bog decreased from 40 ha to 10 ha. The peat bog and its surrounding area are protected as a Botanical Reserve and included in the NATURA 2000 network (Alegro and Šegota 2008). The Danković klada Stream is located at the peat bog edge, running through arable land and deciduous forests. It is characterized by high oscillations of water level between the seasons due to oscillations of the rainfall. The stream banks are overgrown with Alnus glutinosa (L.) Gaertn. and Corylus avellana L. Substrate composition contains mezolithal, microlithal, akal, psammal, argylal, phytal and xylal (Ternjej et al. 2015).

Sampling and identification

Mayflies were sampled together with other aquatic macroinvertebrates at two main habitats: peat bog and stream. Within each habitat type ten replicates were collected once a month, using a benthos net (25×25 cm; mesh size = 500 µm).

In the peat bog, macroinvertebrates were collected from four different types of lentic microhabitats: lake, hollows, ditches and pools. In the stream, all major substrate types were sampled: mezolithal, microlithal, akal, psammal, argylal, phytal and xylal. The study sites differed in physico-chemical water properties, size and vegetation composition (Table 1). The samples were collected during one vegetation season, between March and November 2015.

Table 1.

Comparison of physico-chemical water properties between the Đon močvar peat bog and adjacent stream using Mann-Whitney U test. Key: *** p<0.001, ** p<0.01, ns non-significant. The values are mean ± standard deviation.

Physico-chemical water properties Peat bog Stream Mann-Whitney U test
mean ± SD min max mean ± SD min max U p
Water pH 5.60 ± 0.36 5.02 6.57 6.76 ± 0.37 6.20 7.25 0.00 ***
Alkalinity (CaCO3 mgL-1) 17.80 ± 3.50 10.00 22.50 53.75 ± 15.29 25.00 70.00 0.00 ***
Conductivity (µScm-1) 37.10 ± 47.08 4.98 210.00 99.88 ± 29.81 60.00 128.00 8.00 **
Water depth (cm) 5.00 ± 0.56 3.93 5.60 11.84 ± 4.48 3.50 17.00 8.00 **
Water temperature (°C) 14.90 ± 6.81 5.20 37.00 13.22 ± 3.90 7.30 18.80 23.00 ns
Oxygen (mgL-1) 6.90 ± 2.78 1.00 11.83 7.49 ± 2.08 4.71 10.82 22.00 ns

Species were identified using e.g. Müller-Liebenau (1969), Malzacher (1984) and Bauernfeind and Humpesch (2001). Very young or damaged individuals were identified to the family level. Nomenclature follows Bauernfeind and Sóldan (2012). All voucher specimens are deposited at the Department of Biology, Faculty of Science, Zagreb, Croatia. After identification, total nymphal body length without cerci and antennae was measured using a micrometer on a dissecting stereomicroscope (Stemi 2000-C, Carl-Zeiss).

Environmental variables

The physico-chemical water properties (water temperature, pH, dissolved oxygen concentration and conductivity) were measured at each site during each sampling date, with a multiparameter probe (WTW Multi 3430). Alkalinity (concentration of CaCO3 (mg/L)) was measured using Standard Analytical Procedure (APHA). Since the water was brown coloured, distrophic with low turbidity, standard methods (e.g. depth-meter) could not be applied for measuring water depth. Therefore, water depth was measured with a constructed meter.

Data analysis

Dominance was determined according to Bick (1989). Taxa represented by > 10% of individuals are classified as eudominant, taxa with 5–10% of total abundance as dominant, taxa with 2–5% as subdominant, taxa with 1–2% as recedent and taxa with less than 1% of total share as subrecedent. In order to estimate differences in physico-chemical water properties and mayfly assemblages (number of taxa and number of individuals) between the peat bog and adjacent stream, a Mann-Whitney U test was applied. Prior to the analyses, the data were tested for normality using a Shapiro-Wilk test. These tests are based on pooled microhabitat data both from the peat bog and stream, for physico-chemical parameters and mayfly assemblages. The tests were performed using Statistica 12.0 software package (StatSoft Inc. 2013). For estimation of similarity and differences in mayfly assemblages between the peat bog and stream during the study period, a Bray-Curtis similarity index was used. Prior to analysis, the data were square root transformed. The results of hierarchical cluster analysis were superimposed on Non-metric multidimensional scaling (NMDS) plot. Samples with no mayfly records were excluded from analyses. These analyses were performed using the PRIMER v6 software package (Clarke and Warwick 2001). Life cycle patterns of eudominant and dominant mayfly species were analysed by grouping the nymphs into 1 mm body size classes. All figures were processed with Adobe Illustrator CS6.


In the peat bog, water was highly acidic, differing significantly from the stream (Table 1). Alkalinity and conductivity were three times lower in the peat bog than in the stream. Additionally, water depth was two times lower in the peat bog than in the stream. Water temperature did not differ significantly between the two habitats. However, we observed large variability of water temperature among peat bog microhabitats, particularly in shallow ditches, where summer maximums reached 37 °C. Similar variability was detected for oxygen concentration, with minimum values of only 1 mgL-1 in the peat bog (Table 1).

A total of ten mayfly species were recorded in the peat bog and adjacent stream (Table 2). Only two species were collected from the peat bog, Cloeon dipterum (Linnaeus, 1761) and Caenis luctuosa (Bürmeister, 1839), while in the stream nine species were recorded. Cloeon dipterum was the most abundant species recorded in the peat bog (Table 1), while it was the only subrecedent in the stream. Caenis luctuosa was found only in the peat bog with only one specimen (Table 2). In the stream, Baetis vernus Curtis, 1834) (22.80% of the total catch) was the most numerous species, followed by Habrophlebia fusca (Curtis, 1834) (20.10%) and Electrogena ujhelyii (Sowa, 1981) (15.50%) (Table 2).

Table 2.

Mayfly taxa and their abundance recorded in the Đon močvar peat bog and adjacent stream. Key: * new mayfly records for the Croatian fauna.

Mayfly taxa Peat bog Dominance (%) Stream Dominance (%)
Baetidae juvenile 106 18.40
Baetis rhodani (Pictet, 1843) 6 1.04
Baetis vernus Curtis, 1834 131 22.80
Cloeon dipterum (Linnaeus, 1761) 36 97.30 5 0.90
Nigrobaetis niger (Linnaeus, 1761) 60 10.40
Caenis luctuosa (Bürmeister, 1839) * 1 2.70
Electrogena ujhelyii (Sowa, 1981) 89 15.50
Eurylophella karelica Tiensuu, 1935 * 1 0.17
Habrophlebia fusca (Curtis, 1834) 119 20.10
Leptophlebia marginata (Linnaeus, 1767) * 1 0.17
Paraleptophlebia submarginata (Stephens, 1835) 57 9.91
Species richness (S) 2 9
Number of individuals (N) 37 575

Three species were recorded for the first time for the Croatian mayfly fauna, namely Caenis luctuosa, Eurylophella karelica Tiensuu, 1935 and Leptophlebia marginata (Linnaeus, 1767) (Table 2).

Species richness ranged from 0 to 2 in the peat bog and from 3 to 7 in the stream. It was significantly lower in the peat bog (mean ± SD, 0.66 ± 0.71; Mann-Whitney U test, U = 0.00, p < 0.001; Fig. 2a) than in the stream (4.56 ± 1.24). The number of individuals ranged from 0 to 18 in the peat bog and from 11 to 173 in the stream. There was a significant difference between the peat bog (4.11 ± 5.76) and stream (63.89 ± 52.68; U = 1.00, p < 0.001; Fig. 2b).

Figure 2. 

Mayfly taxa: a species richness (S) and b number of individuals (N) in the peat bog and adjacent stream (mean ± SD). The asterisk indicates significant difference between the habitats (Mann-Whitney U test, p < 0.001).

The similarity between the peat bog and stream was very low, less than 7%. Moreover, NMDS analysis showed clustering of the samples according to the habitat type: the peat bog and stream clustered separately (Fig. 3).

Figure 3. 

Ordination of non-metric multidimensional scaling of mayfly assemblages based on Bray-Curtis similarity coefficient (group average linking) and their square root transformed abundances, with superimposed data of hierarchical cluster analysis.

In the peat bog, mature nymphs of C. dipterum (Fig. 4a) were recorded in June and between August and November, with the highest abundance in August. The body length ranged between 2.2 and 7.04 mm.

Figure 4. 

Seasonal dynamics of a Cloeon dipterum in the Đon močvar peat bog and b Baetis vernus c Nigrobaetis niger in adjacent Daković klada Stream between March and November 2015. Legend: Body length category: A = 0.00–0.99 mm; B = 1.00–1.99 mm; C = 2.00–2.99 mm; D = 3.00–3.99 mm; E = 4.00–4.99 mm; F = 5.00–5.99 mm; G = 6.00–6.99 mm; H = 7.00–7.99 mm.

In the adjacent stream, the body length of B. vernus (Fig. 4b) ranged between 2.56 and 7.76 mm. The species was recorded between March and June and between September and November. Mature nymphs were recorded in both periods of occurrence. The body length of Nigrobaetis niger (Fig. 4c) ranged between 2.64 and 6.40 mm. Mature nymphs were recorded in March, June, and October. Habrophlebia fusca (Fig. 5a) was recorded between March and July, with mature nymphs present from April. The body length ranged between 1.60 and 7.20 mm. Paraleptophlebia submarginata (Fig. 5b) was recorded between August and November. The body length ranged between 2.00 and 8.16 mm, with mature nymphs present in October and November. The body length of E. ujhelyii (Fig. 5c) ranged between 0.90 and 10.95 mm, with mature nymphs present in March, April and November.

Figure 5. 

Seasonal dynamics of a Habrophlebia fusca b Paraleptophlebia submarginata c Electrogena ujhelyii in Danković klada Stream between March and November 2015. Legend: Body length category: A = 0.00–0.99 mm; B = 1.00–1.99 mm; C = 2.00–2.99 mm; D = 3.00–3.99 mm; E = 4.00–4.99 mm; F = 5.00–5.99 mm; G = 6.00–6.99 mm; H = 7.00–7.99 mm; I = 8.00–8.99 mm; J = 9.00–9.99 mm; K = 10.00–10.99 mm.


This study shows that mayflies have low species richness and abundance in the peat bog, as already reported by several other studies (e.g. Bauernfeind and Moog 2000, Joniak and Domek 2006, Schartau et al. 2008). Similarly, NMDS analysis showed a low degree of similarity between the peat bog and adjacent stream. The extreme habitat conditions, such as low pH and high water temperatures were most probably the main limiting factors for mayflies. Nevertheless, two species managed to survive in such harsh environment. The eurytopic and eurythermic C. dipterum, a typical pioneer species exhibiting traits of invasive behaviour (Bauernfeind and Sóldan 2012) was recorded at both focal habitat types (i.e. peat bog and stream). Highly tolerant species to eutrophication and high temperatures, C. luctuosa, generally inhabits lentic habitats, predominantly lakes (Bauernfeind and Sóldan 2012) and it was recorded only in the peat bog. Surprisingly, some studies show high sensitivity of this species to acidification (e.g. Joniak and Domek 2006, Schartau et al. 2008). However, the pH values at the sites in these studies were even lower (approximately 4) than in Đon močvar peat bog, which could indicate that the species is intolerable to pH values less than 5. Future studies should focus on revealing the pH tolerance of C. luctuosa.

The interplay of moderate physico-chemical water properties and a variety of microhabitats in the adjacent stream provided suitable habitat conditions for significantly higher abundances of diverse mayfly species (Bauernfeind and Sóldan 2012). When compared to some other similar streams in that area (e.g. five species recorded in Čatlan, Zeleni dol and Moštanica Streams; see in Vilenica et al. 2015), mayfly species richness recorded from the Danković klada Stream could be considered as relatively high. Mayfly assemblage composition in the stream is a consequence of the mayfly preferences for lotic habitats (e.g. Bauernfeind and Moog 2000, Bauernfeind and Humpesch 2001, Bauernfeind and Sóldan 2012), combined with neutral pH values and moderately high water temperatures. With the exception of E. ujhelyii and E. karelica, whose temperature preferences are not recognized yet, all other recorded species are euritherm, with a preference for moderately warm to warm water temperatures (Buffagni et al. 2009, Buffagni et al. 2015). As water temperature was already recognized as one of the most important environmental factors influencing mayfly assemblages (e.g. Brittain 1979, Harper and Peckarsky 2006) and many authors showed that mayflies are very sensitive to low pH values (Fiance 1978, Gerhardt 1990, Petrin 2011), the results of this study are in accordance.

Mayfly adult life is very short, with the individual life span lasting approximately one day depending on the species. Thus, mayflies spend the majority of their life in the nymphal stage in aquatic habitats (Brittain and Sartori 2003, Bauernfeind and Soldán 2012). Life cycles and seasonal dynamics of most of the temperate mayfly species are well known, with about 60% of the species having univoltine, 30% multivoltine, 4% semivoltine and 3% variable life cycle types (Clifford 1982). The proportion of univoltine species in the study area is in accordance with the latter data, while the proportions of the multivoltine and variable species, show certain discrepancies. According to the literature (Clifford 1982, Bauernfeind and Soldán 2012), 60% of the recorded species were previously determined to have univoltine (e.g. H. fusca, P. submarginata), 20% multivoltine (bivoltine) (N. niger, C. dipterum) and 20% variable (B. rhodani, B. vernus) life cycles. Semivoltine species were not recorded. Certain plasticity, i.e. discrepancies from their representative life cycle patterns were already recorded for some species in different climates and different habitats, which often results in unique patterns (e.g. Alba-Tercedor 1990, López-Rodríguez et al. 2008).

For bivoltine B. vernus, N. niger and univoltine E. ujhelyii (Clifford 1982, Bauernfeind and Sóldan 2012, Buffagni et al. 2015), typical life cycle patterns were confirmed. For C. dipterum, species with highly adaptive life cycles (Clifford 1982, Bauernfeind and Soldán 2012, Buffagni et al. 2015), seasonal bivoltine summer life cycle type was recorded. On the other hand, some discrepancies were observed for two Leptophlebiidae species. Some previous studies have shown that H. fusca and P. submarginata have univoltine life cycles with overwintering in the nymphal stage and mature nymphs present during the early winter season (Bauernfeind and Sóldan 2012). In the Danković klada Stream, mature nymphs of H. fusca and P. submarginata were successively recorded during the early summer and late autumn, respectively. López-Rodríguez et al. (2010) recorded similar pattern in the life cycles of some other species belonging to the same two genera. These seasonal differences in ecological niche partitioning could be related to the availability of the suitable resources in the habitat.

The current study represents an important contribution to the knowledge of the mayfly fauna in Croatia, with several new records for the country together with some records of rare species. Widely distributed, C. luctuosa, recorded only from the peat bog and L. marginata, recorded only from the stream, were documented for the first time in Croatian freshwater habitats (Vilenica et al. 2015, Dekić et al. 2016). What is even more interesting, E. karelica, the species with a disjunct distribution, so far recorded only from Lithuania, North European Russia, Poland and Hungary (Bauernfeind and Sóldan 2012, Alain and Belfiore 2013) was also recorded for the first time (Vilenica et al. 2015, Dekić et al. 2016).

Although the Red list of Croatian mayflies does not exist yet, and none of the species is protected by the law, some recorded species are listed as rare and endangered in European Red lists (e.g. C. dipterum, C. luctuosa, N. niger, H. fusca, L. marginata, P. submarginata, E. ujhelyii; see in e.g. Sartori and Landolt 1999, Zabric 2001). Besides newly recorded C. luctuosa, L. marginata and E. karlelica, all other species are distributed both in Pannonian lowland and Dinaric Western Balkan ecoregions (ER 11 and ER 5, sensuIllies 1978) and in freshwater habitats of both Black Sea and Adriatic Sea Basins. Nigrobaetis niger and P. submarginata were recorded in rivers and streams, H. fusca in springs, rivers and streams, C. dipterum in rivers, streams and lakes and E. ujhelyii in springs and streams (Vilenica et al. 2015). Hence, none of these species is recorded at a critically low number of localities. However, at the localities throughout Croatia where it was previously recorded, N. niger was present in low abundances (Vilenica et al. 2015). Yet, in our study, the species was among the dominant taxa in the Danković klada Stream.

In order to evaluate more precise conservation status and threats to each of the species, additional studies are necessary at an even higher number of freshwater habitats in Croatia.


With three new species records for the country, this study showed that our knowledge of the Croatian mayfly fauna is still growing. Mayfly assemblage composition and abundance in the peat bog is very impoverished and rare species can survive in such harsh environments. A number of species recorded in the adjacent stream preferably occur in lentic habitats, but can also be found in slowly flowing streams (e.g. limnophil E. ujhelyii, L. marginata, limno-rheophil H. fusca, E. karelica; Buffagni et al. 2015). However, it seems that their dispersion to the peat bog was not possible probably due to harsh environmental conditions (low pH, high oscillations of water level and temperature).

New and rare recorded species highlight the high conservation value of the Đon močvar peat bog and adjacent stream. During the 20th century, the abandonment of traditional land-management practices, such as mowing and grazing, has led to severe processes of succession in the studied peat bog. Many of the lentic habitats have decreased in size or completely disappeared, which endangers inhabiting aquatic and terrestrial assemblages. In order to preserve unique habitats and their biodiversity in the Western Balkan region, it is of a crucial importance to protect Croatian largest peat bog from rapid successional changes.

Studies on distribution, biodiversity and ecology are particularly important for conservation planning e.g. for determining the conservation status of species and defining the factors that affect biodiversity patterns (de Silva and Medellín 2001). Thereby, knowledge of mayfly faunal composition, ecology, and seasonal dynamics could contribute to the classification and protection of the peat bog habitats in Croatia.


We would like to thank Antun Alegro, Vladimir Bartovsky, Mirjana Dimnjaković, Marija Ivković, Renata Matoničkin Kepčija, Ivana Pozojević, Ana Previšić, Sandra Slivar and Marija Starčević for the field assistance. Thanks to Miran Katar for help with the artwork. This study was funded by the Institution for protected nature management of Sisak-Moslavina county, grant awarded to IT (No. 402-08/14-01/02).


  • Alain T, Belfiore C (2013) Ephemeroptera, mayflies. Fauna Europaea version 2.6.2. [accessed on 20th of June, 2016]
  • Alba-Tercedor J (1990) Life cycles and ecology of mayflies from Sierra Nevada (Spain). Limnetica 6: 23–34.
  • Alegro A, Šegota V (2008) Florističke i vegetacijske značajke botaničkog rezervata „Đon močvar“ u Blatuši. General technical report. State Institute for Nature Protection, Zagreb, Croatia, 33 pp. [In Croatian]
  • Baars J-R, Murray DA, Hannigan E, Kelly-Quinn M (2014) Macroinvertebrate assemblages of small upland peatland lakes in Ireland. Biology and Environment: Proceedings of the Royal Irish Academy 2014. doi: 10.3318/BIOE.2014.31
  • Battin TJ, Luyssaert S, Kaplan LA, Aufdenkampe AK, Richter A, Tranvik LJ (2009) The boundless carbon cycle. Nature Geoscience 2: 598–600. doi: 10.1038/ngeo618
  • Bauernfeind E, Moog O (2000) Mayflies (Insecta: Ephemeroptera) and the assessment of ecological integrity: a methodological approach. Hydrobiologia 422: 71–83. doi: 10.1023/A:1017090504518
  • Bauernfeind E, Humpesch UH (2001) Die Eintagsfliegen Zentraleuropas - Bestimmung und Ökologie. Verlag NMW, Wien, 239 pp.
  • Bauernfeind E, Soldán T (2012) The mayflies of Europe (Ephemeroptera). Apollo Books. Ollerup, Denmark, 783 pp. doi: 10.1163/9789004260887
  • Bick H (1989) Ökologie: Grundlagen, terrestrische und aquatische Ökosysteme, angewandte Aspekte. Gustav Fischer Verlag, Stuttgart, New York.
  • Brittain JE (1979) Emergence of Ephemeroptera from Øvre Heimdalsvatn, a Norwegian subalpine lake. In: Pasternak K, Sowa R (Eds) Proceedings of the 2nd International Conference on Ephemeroptera. Panstwowe Wydawnictwo Naukowe, Warszawa-Kraków, 115–123.
  • Brittain JE (1990) Life history strategies in Ephemeroptera and Plecoptera. In: Campbell IC (Ed.) Mayflies and Stoneflies. Kluwer Academic Publishers, 1–12. doi: 10.1007/978-94-009-2397-3_1
  • Brittain JE (1991) Life history characteristics as a determinant of the response of mayflies and stoneflies to man-made environmental disturbance (Ephemeroptera and Plecoptera). Proceedings of the 6th International Conference on Ephemeroptera and Plecoptera, Granada, 539–545.
  • Brittain JE, Sartori M (2003) Ephemeroptera (Mayflies). In: Resh VH, Cardé RT (Eds) Encylopedia of Insects. Academic Press, Amsterdam, 373–380.
  • Buffagni A, Cazzola M, López-Rodríguez MJ, Alba-Tercedor J, Armanini DG (2009) Volume 3 – Ephemeroptera. In: Schmidt-Kloiber A, Hering D (Eds) Distribution and Ecological Preferences of European Freshwater Organisms. Pensoft Publishers, Sofia-Moscow, 254 pp.
  • Buffagni A, Armanini DG, Cazzola M, Alba-Tercedor J, López-Rodríguez MJ, Murphy J, Sandin L, Schmidt-Kloiber A (2015) Dataset “Ephemeroptera. - the taxa and autecology database for freshwater organisms, version 6.0 [accessed on 30.03.2016]
  • Clarke KR, Warwick RM (2001) Change in marine communities: an approach to statistical analysis and interpretation. Primer-E, Lutton, United Kingdom.
  • Clifford HF (1982) Life cycles of mayflies (Ephemeroptera), with special reference to voltinism. Quaestiones Entomologicae 18(1–4): 15–90.
  • Dekić S, Ćuk R, Belfiore C (2016) Contribution to Croatian mayfly fauna (Insecta: Ephemeroptera). Natura Croatica 25(1): 101–108. doi: 10.20302/NC.2016.25.6
  • de Silva HG, Medellín RA (2001) Evaluating completeness of species lists for conservation and macroecology: a case study of Mexican land birds. Conservation Biology 15: 1384–1395. doi: 10.1111/j.1523-1739.2001.00177.x
  • Doyle G (1990) Ecology and Conservation of Irish Peatlands. In: Doyle G (Ed.) Ecology and Conservation of Irish Peatlands. Royal Irish Academy, Dublin.
  • Drinan TJ, Foster GN, Nelson BH, O’Halloran J, Harrison SSC (2013) Macroinvertebrate assemblages of peatland lakes: Assessment of conservation value with respect to anthropogenic land-cover change. Biological Conservation 158: 175–187. doi: 10.1016/j.biocon.2012.10.001
  • Elliott JM, Humpesch UH, Macan TT (1988) Larvae of the British Ephemeroptera: a key with ecological notes. Scientific Publications of the Freshwater Biological Association 49: 145.
  • Erba S, Melissano L, Buffagni A (2003) Life cycles of Baetidae (Insecta: Ephemeroptera) in a North Italian Prealpine stream. In: Gaino E (Ed.) Research update on Ephemeroptera & Plecoptera. Università di Perugia, Perugia, 177–186.
  • Fiance SB (1978) Effects of pH on the biology and distribution of Ephemerella funeralis (Ephemeroptera). Oikos 31: 332–339. doi: 10.2307/3543659
  • Gerhardt A (1990) Effects of Subacute Doses of Cadmium on pH-stressed Leptophlebia marginata (L.) and Baetis rhodani Pictet (Insecta: Ephemeroptera). Environmental Pollution 6: 29–42. doi: 10.1016/0269-7491(90)90170-H
  • Hannigan E, Kelly-Quinn M (2012) Composition and structure of macroinvertebrate communities in contrasting open-water habitats in Irish peatlands: implications for biodiversity conservation. Hydrobiologia 692(1): 19–28. doi: 10.1007/s10750-012-1090-4
  • Illies J (1978) Limnofauna Europaea. Gustav Fischer Verlag, Stuttgart & New York, 532 pp.
  • Joniak T, Domek P (2006) Influence of humification on biodiversity of lake benthic macroinvertebrates. Acta Agrophysica 7(2): 363–368.
  • Joosten H, Clarke D (2002) Wise Use of Mires and Peatlands-Background and Principles including a Framework for Decision Making. International Mire Conservation Group, International Peat Society.
  • Kivinen E, Pakarinen P (1981) Geographical distribution of peat resources and major peatland complex types in the world. Suomalaisen Tiedeakatemian toimituksia Series A III Geologica-Geographica 132: 1–28.
  • Langheinrich U, Tischew S, Gersberg RM, Lüderitz V (2004) Ditches and canals in management of fens: opportunity or risk? A case study in the Drömling Natural Park, Germany. Wetlands Ecology and Management 12: 429–445. doi: 10.1007/s11273-004-0700-y
  • Limpens J, Berendse F, Blodau C, Canadell JG, Freeman C, Holden J, Roulet N, Rydin H, Schaepman-Strub G (2008) Peatlands and the carbon cycle: from local processes to global implications, a synthesis. Biogeosciences 5: 1475–1491. doi: 10.5194/bg-5-1475-2008
  • López-Rodríguez MJ, Tierno de Figueroa JM, Alba-Tercedor J (2008) Life history and larval feeding of some species of Ephemeroptera and Plecoptera (Insecta) in the Sierra Nevada (Southern Iberian Peninsula). Hydrobiologia 610: 277–295. doi: 10.1007/s10750-008-9444-7
  • López-Rodríguez MJ, Tierno de Figueroa JM, Alba-Tercedor J (2010) Comparative Study of the Nymphal Biology of Two Coexisting Species of Mayflies (Insecta: Ephemeroptera) in a Mediterranean Stream in Southern Europe. International Review of Hydrobiology 95(1): 58–71. doi: 10.1002/iroh.200811197
  • Malzacher P (1984) Die europäischen Arten der Gattung Caenis Stephens (Insecta: Ephemeroptera). The European species of the genus Caenis Stephens (Insecta: Ephemeroptera). Stuttgarter Beiträge zur Naturkunde, Serie A (Biologie) 373: 1–48.
  • Mieczan T, Tarkowska-Kukuryk M, Adamczuk M, Pęczuła W, Demetraki-Paleolog A, Niedźwiecki M (2015) Research of Different Types of Peatbogs: Relationships of Bioceonosis Structures and Physico-Chemical Parameters. Polish Journal of Environmental Studies 24(1): 191–198.
  • Moog O (2002) Fauna Aquatica Austriaca, Edition 2002, Wassserwirtschaftskataster, Bundesministerium für Land und Forstwirtschaft, Umwelt und Wasserwirtschaft, Vienna.
  • Müller-Liebenau I (1969) Revision der europäischen Arten der Gattung Baetis Leach, 1815. (Insecta, Ephemeroptera). Gewässer und Abwasser 66/67: 95–101.
  • Petrin Z (2011) Species traits predict assembly of mayfly and stonefly communities along pH gradients. Oecologia 167(2): 513–524. doi: 10.1007/s00442-011-2003-3
  • Raddum GG, Fjellheim A (1993) Life cycle and production of Baetis rhodani in a regulated river in Western Norway: comparison of pre - and post - regulation conditions. Regulated Rivers: Research and Management 8: 49–61. doi: 10.1002/rrr.3450080109
  • Sartori M, Landolt P (1999) Atlas de distribution des Ephémères de Suisse (Insecta, Ephemeroptera). Fauna helvetica 3. SEG-CSCF Ed., Neuchâtel.
  • Sartori M, Brittain JE (2015) Order Ephemeroptera. In: Thorp J, Rodgers DC (Eds) Thorp and Covich’s Freshwater Invertebrates: Ecology and General Biology, 4th Edition, Academic Press, New York, 873–891. doi: 10.1016/B978-0-12-385026-3.00034-6
  • Schartau AK, Moe SJ, Sandin L, McFarland B, Raddum GG (2008) Macroinvertebrate indicators of lake acidification: analysis of monitoring data from UK, Norway and Sweden. Aquatic Ecology 42(2): 293–305. doi: 10.1007/s10452-008-9186-7
  • Šegota T, Filipčić A (2003) Köppenova podjela klima i hrvatsko nazivlje. Geoadria 8/1: 17–23. [In Croatian]
  • Ternjej I, Alegro A, Brigić A, Gottstein S, Kerovec M, Matoničkin Kepčija R, Šegota V, Previšić A, Vilenica M, Lajtner J, Antonović I, Starčević M, Bujan J (2015) Revitalizacija cretnog staništa posebnog botaničkog rezervata Đon-Močvar. Croatian Botanical Society, Zagreb, 138 pp. [In Croatian]
  • Topić J, Stančić Z (2006) Extinction of fen and bog plants and their habitats in Croatia. Biodiversity and Conservation 15: 3371–3381. doi: 10.1007/s10531-005-4874-2
  • Vilenica M, Gattolliat J-L, Mihaljević Z, Sartori M (2015) Croatian mayflies (Insecta, Ephemeroptera): species diversity and distribution patterns. ZooKeys 523: 99–127. doi: 10.3897/zookeys.523.6100
  • Vilenica M, Previšić A, Ivković M, Popijač A, Vučković I, Kučinić M, Kerovec M, Gattolliat J-L, Sartori M, Mihaljević Z (2016) Mayfly (Insecta: Ephemeroptera) assemblages of a regulated perennial Mediterranean river system in the Western Balkans. Biologia 71(9): 1038–1048. doi: 10.1515/biolog-2016-0121
  • Więcek M, Martin P, Gąnka M (2013) Distribution patterns and environmental correlates of water mites (Hydrachnidia, Acari) in peatland microhabitats. Experimental and Applied Acarology 61(2): 147–160. doi: 10.1007/s10493-013-9692-8
  • Zabric D (2001) Analiza stanja biotske raznovrsnosti enodnevnic (Ephemeroptera). Ekspertne študije za Pregled stanja biotske raznovrsnosti in krajinske pestrosti v Sloveniji. Agencija Republike Slovenije za okolje, Ljubljana, 116–122. [In Slovenian]
  • Zaninović K, Gajić-Čapka M, Perčec Tadić M, Vučetić M, Milković J, Bajić A, Cindrić K, Cvitan L, Katušin Z, Kaučić D, Likso T, Lončar E, Lončar Ž, Mihajlović D, Pandžić K, Patarčić M, Srnec L, Vučetić V (2008) Klimatski atlas Hrvatske / Climate atlas of Croatia 1961–1990, 1971–2000. Državni hidrometeorološki zavod, Zagreb, 200 pp.
  • Zedková B, Rádková V, Bojková J, Soldán T, Zahrádková S (2015) Mayflies (Ephemeroptera) as indicators of environmental changes in the past five decades: a case study from the Morava and Odra River Basins (Czech Republic). Aquatic Conservation: Marine and Freshwater Ecosystems 25(5): 622–638. doi: 10.1002/aqc.2529